Accepted Manuscript Comparative TOPSIS-ELECTRE TRI methods for optimal sites for photovoltaic solar farms. Case study in Spain J.M. Sánchez-Lozano, M.S. García-Cascales, M.T. Lamata PII:
S0959-6526(16)30246-3
DOI:
10.1016/j.jclepro.2016.04.005
Reference:
JCLP 7010
To appear in:
Journal of Cleaner Production
Received Date: 19 November 2014 Revised Date:
5 March 2016
Accepted Date: 3 April 2016
Please cite this article as: Sánchez-Lozano JM, García-Cascales MS, Lamata MT, Comparative TOPSIS-ELECTRE TRI methods for optimal sites for photovoltaic solar farms. Case study in Spain, Journal of Cleaner Production (2016), doi: 10.1016/j.jclepro.2016.04.005. This is a PDF file of an unedited manuscript that has been accepted for publication. As a service to our customers we are providing this early version of the manuscript. The manuscript will undergo copyediting, typesetting, and review of the resulting proof before it is published in its final form. Please note that during the production process errors may be discovered which could affect the content, and all legal disclaimers that apply to the journal pertain.
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Comparative TOPSIS-ELECTRE TRI methods for optimal sites for photovoltaic solar
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farms. Case study in Spain.
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J. M. Sánchez-Lozano(1) , M. S. García-Cascales(2), M. T. Lamata(3)
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(1)
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Cartagena, San Javier, Murcia, Spain
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(2)
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de Cartagena (UPCT), Murcia, Spain
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(3)
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Granada.18071 Granada, Spain
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Centro Universitario de la Defensa. Academia General del Aire. Universidad Politécnica de
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Depto de Electrónica, Tecnología de Computadoras y Proyectos. Universidad Politécnica
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Depto de Ciencias de la Computación e Inteligencia Artificial. Universidad de
*Corresponding author: María Teresa Lamata Jiménez
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E-mail:
[email protected]
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Telephone: +34 958240593
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Fax: +34 958243317
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Abstract
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This paper is to select the best locations to build solar photovoltaic farms (large grid-
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connected photovoltaic systems which have more than 100kWp of installed capacity), with the
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coast of Murcia in the southeast of Spain being used as an example. In order to solve the
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problem, the suitable locations to implant such facilities will be identified by a Geographical
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Information System (GIS). To obtain the weights of the criteria which influence the proposed
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problem, the Analytic Hierarchy Process (AHP) will be employed. Then, the suitable
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ACCEPTED MANUSCRIPT locations will be evaluated and classified using two different multi-criteria decision methods,
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the Technique for Order Preference by Similarity to Ideal Solution (TOPSIS) and
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ELimination and Choice Expressing Reality (ELECTRE), in this case the version TRI. We
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are thus also able to establish a comparison between the two methods. This comparison
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demonstrates how although the results do not completely coincide, some similarity can be
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seen between the two methods.
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Keywords: Solar photovoltaic farms; GIS; Restrictions; Criteria; AHP; TOPSIS; ELECTRE
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TRI.
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1. Introduction
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Nowadays, the commitment to carrying out sustainable development to satisfy the present
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needs of the population without compromising those of future generations is a difficult
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challenge to achieve. From an energy point of view, forecasts indicate that world energy
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consumption will grow by 56 % between 2010 and 2040, although a gradual increase in prices
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of both oil and natural gas is expected (U.S. Energy Information Administration, 2013). The
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required containment of growth in emissions of greenhouse gases (Arrhenius, 1896),
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established by the World Meteorological Organization and United Nations (Working Group I-
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II-III 1990; United Nations, 1992/1997/2013) in compliance with the objectives set out in the
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various energy policies of the European Union (European Commission, 1996, 1997; European
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Parliament, 2009), were the main reasons that sustainable development strategies were
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promoted (Jegatheesan et al, 2009; Engelbrecht et al, 2013; Dovì et al, 2009) and the
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implementation of renewable energy (RE) installations was endorsed (Espey, 2001; Menz and
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Vachon, 2006; Foxon et al, 2005). The current economic and financial crisis affecting a large
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number of countries has led to the reduction in the support for renewable energy installations,
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ACCEPTED MANUSCRIPT causing significant negative aspects (Avril et al, 2012). However, economies of scale and the
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development of these technologies have helped reduce production costs so that, although
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governments have failed to support and stimulate this type of facility, private investors have
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taken the reins with implementation in order to continue with renewable energy installations
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(Wünteshagen and Menichetti, 2012).
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In Spain, in order to meet the objectives set by the European Union and to promote the
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implementation of renewable energy facilities, the government energy plans were developed
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to cover two periods of action between the years 2005-2010 (IDAE, 2005) and 2011-2020
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(IDAE, 2010). In the latter period renewable energy was earmarked to represent at least 20%
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of final energy consumption by 2020. Among the various renewable sources which grew most
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as a result of energy policies elaborated in the first period (Royal Decree 436/2004; Royal
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Decree 661/2007) solar photovoltaic (PV) stood out above the rest (Bürer and Wüstenhagen,
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2009); its growth was such that in 2009 Spain was ranked as the second country in the world
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in terms of photovoltaic power regarding overall cumulative installed capacity, with 3.5 GW
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(European Commission, 2010). Although subsequent energy policies have not encouraged its
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expansion (Royal Decree-Law 14/2010; Royal Decree-Law 1/2012), the decrease in
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production costs of photovoltaic technology as well as the excellent climatic conditions of the
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country have allowed investors to continue supporting the implementation of solar
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photovoltaic farms in Spain (EPIA, 2013).
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The Spanish PV potential is huge because Spain receives on average, in the horizontal plane,
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a global radiation of 1,600 kWh/m2 per year, with the Mediterranean coast being the area with
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the highest PV potential, hence the interest in studying this particular area to implement such
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technology (Figure 1). It is thus appropriate to continue promoting and encouraging the
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implementation of solar photovoltaic energy in order to comply with the international
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specific target for 2020 (IDAE, 2010).
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Among the several advantages of solar technology, it should be recalled that the sun is an
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inexhaustible source of energy. It is therefore a technology that could provide significant
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support to current energy technologies allowing to reduce consumption of fossil fuels. In
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addition, an adequate and responsible implementation of this technology not only allows new
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jobs to be created but also promotes the economic and industrial development of the zones
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where they are located. However, this technology is not without drawbacks. The
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indiscriminate implementation of large grid-connected photovoltaic systems (more than 100
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kWp of installed capacity), also called “Solar farms”, can lead to environmental problems
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such as the movement of migratory birds, deforestation, creation of physical barriers which
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damage the earth’s wildlife, etc. It is therefore necessary to choose very carefully which areas
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are suitable for implementing this technology, because it must not only seek the maximum
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energy efficiency (areas with high solar radiation potential) but it must also be situated in
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places where they may cause less damage to the environment, to ensure balanced and
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sustainable development.
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Figure 1. Global irradiation and solar electricity potential of Spain (European Commission, 2012; Huld et al, 2012; Súri et al, 2007)
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The Region of Murcia, located in the southeast of Spain, has become one such area where
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many solar photovoltaic farms have been introduced. One of the main reasons that PV
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promoters prefer this region is because it has one of the highest levels of solar radiation
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potential in the country. According to the Solar Radiation and Atmospheric Temperature
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Atlas of the Autonomous Community of the Region of Murcia (Vera et al, 2007), the majority
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of its territory has more than 5.0 kWh/m2·day. However, it should be noted that it is not easy
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to implement such facilities anywhere in the Region of Murcia, and in areas far from the coast
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ACCEPTED MANUSCRIPT the level of urban and residential occupancy is low compared with the level reached in areas
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near the sea (Gómez-López et al, 2010) which further increases the difficulty facing any
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promoter of renewable energy installations to find suitable areas which are nearshore. In
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addition to technical factors such as solar radiation or land use, it is also necessary to take into
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account economic factors (grid proximity, land slope, etc.) or environmental factors (sensitive
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areas, nature reserves, etc.) which affect the optimum location for PV farms (Charabi and
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Gastli, 2011). Among the environmental factors worth mentioning is the impact of PV farms
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on birds, which is why in this paper restrictions will be taken into account, such as the areas
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of special protection for birds which are protected through the Directive 92/43/EEC of 21
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May 1992 on the conservation of natural habitats and of wild fauna and flora (European
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Parliament, 2009). One of the main points of that Directive is the designation of special
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conservation areas in order to create a coherent European ecological network. In this way the
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restoration or maintenance of natural habitats and species of Community interest at a
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favourable conservation status can be ensured. Therefore, performing an in-depth analysis of
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the coast of Murcia, allowing to locate areas that are not subject to any restrictions and are
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thus feasible to implement photovoltaic solar farms is extremely important, and it is precisely
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for this reason that the management of visualization tools and cartographic editing such as
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Geographic Information Systems (GIS) is useful. GIS offer the possibility of finding viable
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locations to implement this type of facility, and are able to show the earth’s surface through
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thematic layers which provide maps (visual analysis), and alphanumeric information in a
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database form (qualitative and / or quantitative values) of these locations such as their
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designation, area, slope, distance to cities, etc. This alphanumeric information can be
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extracted in a spreadsheet format. Therefore, it can be useful to make any subsequent analysis
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of decision-making.
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ACCEPTED MANUSCRIPT Among the numerous applications of GIS analysis special mention should be made to
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territorial planning of any kind (Kaijuka, 2007), managing available resources (Wallsten et al,
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2013), environmental analysis (Yousefi-Sahzabi et al, 2011) and studies to implement
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renewable energy facilities. The use of GIS to solve the localization of renewable energy
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facilities began to develop in the late twentieth century (Voivontas et al, 1998; Sorensen and
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Meibom, 1999) and it has become more widespread since then (Yue and Wang, 2006; Byrne
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et al, 2007; Domínguez Bravo et al, 2007).
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The literature contains numerous decision-making methods and particularly multi-criteria
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ones that can be applied to problems in general and more specifically to those that consider
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renewable energy (Kahraman et al, 2009; Kaya and Kahraman, 2010; Cavallaro, 2010;
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García-Cascales et al, 2012; Khalili-Damghani and Sadi-Nezhad, 2013).
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However, one of the main advantages offered by the GIS are their excellent ability to perform
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analysis of optimal locations for renewable energy facilities (Van Haaren and Fthenakis,
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2011; Janke, 2010) since through their multiple edition tools (buffer, difference, filter, logical
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operators, etc.) complex location problems can be solved.
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The literature provides a large number of examples where GIS are combined with multi-
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criteria decision-making methods (MCDM), multi-objective optimization, or probabilistic
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approaches. In this way (Zhang et al, 2010) evaluated the productivity and sustainability of
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biofuel crop production systems through GIS and an evolutionary multi-objective
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optimization algorithm. In order to optimize the design and strategic operation of district
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energy systems, GIS were not only combined with these types of optimization model
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(Fazlollahi et al, 2013), but also with k-means clustering techniques (Fazlollahi et al, 2014).
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Recently, and from an energy point of view, the renewable energy potential has been assessed
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in Romania using k-means clustering algorithm and GIS (Grigoras and Scarlatache, 2015).
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the criteria which involve the decision problem are multiple. In such cases, combining GIS
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with MCDM allows for very precise and exhaustive analysis, since the alphanumeric
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information, which is provided by the GIS software, can be extracted in a spreadsheet format
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which can then be used in order to apply multi-criteria decision methods (Al-Yahyai et al,
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2012; Zubaryeva et al, 2012; Uyan, 2013).
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Although recently studies have been carried out to evaluate the best locations of solar
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facilities in the southeast of Spain combining, on the one hand GIS with TOPSIS and AHP
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methods (Sánchez-Lozano et al, 2013a), and through the ELECTRE TRI method on the other
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(Sánchez-Lozano et al, 2014), there are important differences that make its application in the
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present study especially novel. The main differences between this paper and the cited
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references are not only in the methodologies applied but also in the goal. (Sánchez Lozano et
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al, 2014) applied the pessimistic ELECTRE TRI procedure; however in the proposed paper
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the optimistic ELECTRE TRI procedure will be applied. The goal to reach is not the same;
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this study seeks to carry out a comparison between two multi-criteria decision methods. There
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are also differences in the way of applying the methodologies. In (Sánchez Lozano et al,
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2014) an iterative process of the IRIS software was carried out in which an expert classifies a
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small number of alternatives according to his/her opinion. Another difference is the software
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used, in this paper a calculation process through Excel spreadsheets has been carried out to
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apply the TOPSIS method, the ELECTRE TRI methods, and in order to obtain the weight of
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the criteria. In this way it is possible to analyze a large number of alternatives.
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Through this short review of the applications of GIS and MCDM to renewable energy, it
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becomes clear that they are very useful tools for solving problems of location and their
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subsequent evaluation. Thus, in this paper a GIS and a comparison of MCDM will be used in
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order to find the most feasible locations for a solar photovoltaic farm (Figure 2). Section 2
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ACCEPTED MANUSCRIPT details the models and techniques that were employed in the work to obtain the desired
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results. In Section 3, the surfaces obtained were evaluated by the two methods of multi-
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criteria decision making (TOPSIS and ELECTRE TRI); the weights of the criteria were
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previously calculated using the analytic hierarchy process (AHP). Finally, Section 4 will
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reflect both the conclusions and possible limitations of the study.
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2. Methodology
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As has been noted, the first goal is to obtain the suitable locations and this will be done using
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a geographical information system. Subsequently a multi-criteria decision model should
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evaluate these alternatives. In our case and due to the importance of the project we will
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compare two differently designed methods: TOPSIS and ELECTRE TRI. All the above is
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reflected in Figure 2.
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Figure 2. Process scheme
2.1. GIS
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The first part of the problem will be solved using a GIS in which thematic layers that
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represent and define the study area and those areas where it is impossible to implement solar
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photovoltaic farms will be introduced (restrictions). Such restrictions may be due to either the
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current state of the ground preventing it or due to the legislative framework in force
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prohibiting it. Once this surface has been obtained, GIS thematic layers such as the criteria
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that influence the selection of the best locations are inserted so as to complete the database.
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This will then serve as the starting point for the subsequent decision analysis, which allows
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the best locations to be determined. The selected GIS is called gvSIG (www.gvSIG.org)
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which has been driven by the Regional Ministry of Infrastructure and Transport of Valencia
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(Spain).
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Once the study area is known (Coast of the Region of Murcia), the next step is to identify
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constraints (Table 1), i.e., those areas where, due to the laws in force on the one hand
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(European standards, national, regional and local laws) and the current status of the territory
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on the other hand (roads, railways, towns, etc...), make it impossible to implement solar
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photovoltaic farms.
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Once the thematic layers of restrictions have been inserted in GIS they will be deducted from
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the initial surface area occupied by the restrictions imposed by the legislative framework with
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the editing commands of the software. Finally, to obtain viable locations, it will require only a
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filter to be performed that removes those parcels of less than 1000 m2 or those which have
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some buildings inside. Once the editing process has been conducted with GIS, it will have
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created a thematic layer which will display the locations to implement any feasible solar
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photovoltaic farms (Figure 3) and which will also provide alphanumeric information as an
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attribute table with the cartographic and cadastral information for such locations. This
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cadastral information is the way of identifying the rural properties in Spain, each of these
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properties is designed as plots.
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Figure 3. Suitable locations
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2.1.2. Criteria Layer
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To finalize the database, it will be necessary to define the criteria that influence the decision;
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that is to say, those that will opt for one location rather than another. These criteria are
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defined not only through the study of the literature (Janke, 2010; Gastli and Charabi, 2010; Jo
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experts in solar photovoltaic farms.
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In order to do this, the participation of three experts was received, specifically with a doctor
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of physics, who is an expert on photovoltaic technologies with more than 10 years of
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experience; a doctor of engineering also specialising in photovoltaic systems and technologies
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and a promoter of renewable energy facilities with over 8 years of experience in the sector.
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The experts defined the main criteria which must be taken into account to find optimal
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locations of solar farms in this study area. These criteria are briefly described
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• g1: Agrological capacity (Classes): Suitability of land for agricultural development, if
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a zone has excellent agrological capacity, it will not be ideal to host the facility, and
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vice versa.
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• g2: Slope (%): Land slope, the higher percentage of having a surface inclination, the worse aptitude to hold a solar plant.
• g3: Area (m²): surface contained within a perimeter of land that can accommodate an RE plant.
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• g4: Field Orientation (Classes): Position or direction of the ground to a cardinal point.
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• g5: Distance to main roads (m): Space or interval between the nearest road and the
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different possible sites.
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• g6: Distance to power lines (m): Space or interval between the nearest power line and the different possible sites.
• g7: Distance to cities (m): Space or interval between cities (cities or towns) and the different possible sites. • g8: Distance to electricity transformer substations (m): Space or interval between transformer substations of electric power and the different possible sites.
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• g9: Potential solar radiation (kJ·m²/day): This corresponds to the amount of solar energy a ground surface receives over a period of time (day). • g10: Average temperature (ºC): Average temperatures measured on the ground in the course of one year.
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Once the database has been extracted in Excel spreadsheet format, it is necessary to analyze
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and evaluate it. This problem can be considered as a multi-criteria decision making problem
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MCDM (Chen and Hwang, 1992; Hwang and Yoon, 1981; Keeney and Raiffa, 1976; Luce
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and Raiffa, 1957), where it is sought to choose the best alternative Ai, i=1,2,…,n with n≥2
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when considering the criteria gj, j=1,2,…,m with m≥2 and experts Ek, k=1,2,…,r with r≥2; it is
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considered that n, r and m are finite.
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To solve the problem proposed a comparison between TOPSIS (Hwang and Yoon, 1981) and
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ELECTRE TRI (Roy and Bouyssou, 1991; Yu, 1992a; Yu, 1992b) methodologies is
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performed. Prior to doing so it is necessary to determine the weight of criteria and for this the
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AHP methodology is applied (Saaty, 1980). These methods have been chosen because their
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focuses differ. Whereas TOPSIS works as a continuous model, other methods such as
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ELECTRE TRI work in a discreet manner. In order to demonstrate this, a comparative
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between both methods will be developed in this paper. The weights of the criteria are
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unknown since there are no similar studies. For this purpose and due to its simplicity, the
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AHP method will be applied. Furthermore, the TOPSIS method is used because its logic is
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rational and understandable, the process is simple and organized in an algorithm. It is able to
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seek the best alternatives through simple mathematical operations in which the process of
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calculation takes into account the values of the weights of each criterion and if the criterion is
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a cost or a profit.
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ELECTRE TRI method is a helpful method for multi-criteria decisions, specially designed to
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address classification or segmentation problems. Acceptance of any alternative is based on
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comparing it with alternative reference through overcoming relations. This is one of the main
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reasons why it was decided to make the comparison between TOPSIS and ELECTRE TRI
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methods, since the former compensates the lack or excesses in the criteria in a continuous
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manner, whereas the latter works in a discreet manner. Therefore, carrying out a comparative
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between both methods could be of great interest.
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This is a pairwise comparisons method, development by Saaty 1980. The criteria will be
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denoted by “g1, g2, …, gn”, their actual weights by “w1, w2, …, wn” and the matrix of the ratios
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“W = [wi / wj]”. The matrix of pairwise comparisons “A = [aij]” represents the expert’s
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preference between individual pairs of alternatives. The elements “aij” are considered to be
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estimates of the ratios “wi / wj”. The values aij € [1/9,..,1,…,9], are positive and satisfy the
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reciprocity property: aij = 1/aji (i,j = 1, 2, …, n).
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The vector of weights is the eigenvector corresponding to the maximum eigenvalue “λmax” of
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the matrix A. The traditional eigenvector method of estimating weights in AHP yields a way
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of measuring the consistency of the referee’s preferences arranged in the comparison matrix.
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The consistency index (CI) is given by CI = (λmax – n)/(n-1).
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If the referee shows some minor inconsistency, then λmax > n and Saaty proposes the
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following measure of the consistency index: CR = CI / RI where RI is the average value of CI
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obtained in Alonso and Lamata (2006).
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Table 2. Random index for different matrix orders.
Based on these comparisons, AHP computes the importance of the criteria. 12
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The TOPSIS method, which was proposed by Hwang and Yoon (1981), is one of the best
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known classical MCDM. It is based upon the concept that the chosen alternative should have
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the shortest distance from the positive ideal solution (PIS), and the farthest from the negative
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ideal solution (NIS).
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The computational steps of the TOPSIS method are the following:
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Step 1.- Establish a performance decision matrix
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Step 2.- Normalize the decision matrix by means of
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nij = xij
j =1
ij
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Step 3.- Calculate the weighted normalized decision matrix
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vij = w j ⊗ nij , j = 1,K , n, i = 1,K , m,
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Step 4.-Determine the positive ideal solution (PIS) and negative ideal solution (NIS)
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A+ = v1+ ,K , vn+ =
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A− = v1− ,K , vn− =
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Step 5.- Calculate the separation measures.
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n 2 2 d = ∑ ( vij − v +j ) , i = 1,…, m j =1
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Step 6.- Calculate the relative closeness to the ideal solution
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The ranking score Ri is calculated using the equation:
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Ri =
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Such that: If Ri = 1 → Ai = A+ and if Ri = 0 → Ai = A−
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Step 7.- Rank the preference order
{
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{( max v , j ∈ J ) ( min v , j ∈ J ')}
i = 1, 2,..., m
{
}
{( min v , j ∈ J ) ( max v , j ∈ J ')}
i = 1, 2,..., m
1
ij
i
(2)
(3)
1
n 2 2 d = ∑ ( vij − v −j ) , i = 1,…, m j =1 − i
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ELECTRE TRI (Roy and Bouyssou, 1991; Yu, 1992a; Yu, 1992b) is a method that assigns a
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set of alternatives to previously defined categories. In this context a category is defined as a
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way of classifying the different alternatives between two limits (upper and lower limit),
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according to some aptitude or capacity. The assignment of an alternative a to one category or
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another is obtained by comparing the alternative with the limits of the predefined categories.
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ELECTRE TRI builds an outranking relationship S i.e., to validate or invalidate the assertion
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aSbh (and bhSa) whose meaning is “alternative a is at least as good as bh”.
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Step 1.- Definition of reference actions
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Actions referred to as the limits of the various categories for classifying potential actions are
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defined, and preference thresholds pj(bh) and indifference qj(bh) such that qj(bh) represents the
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greatest difference gj(a)-gj(bh) that maintains indifference between a and bh to the criterion gj
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and, pj(bh) represents the smallest difference gj(a)-gj(bh) compatible with a preference a on the
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criterion gj.
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Step 2.- Determination of concordance indexes by criteria
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cj(ai,bh) = 0 pj ≤ gj(bh)-gj(ai)
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0 < cj(ai,bh) <1 qj < gj(bh)-gj(ai) ≤ pj ⇒ c j (ai , bh ) = g j (ai ) + p j − g j (bh )
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cj(ai,bh) = 1 gj(bh)-gj(ai) ≤ qj
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Step 3.- Calculation of the overall concordance
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C (ai , bh ) =
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∑ j∈F k j
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Step 4.- Determination of the discordance indexes by criteria
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dj(ai,bh) = 0 gj(ai) ≥ gj(bh) - pj
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0 < dj(ai,bh) < 1 gj(bh) – vj< gj(ai) ≤ gj(bh) - pj ⇒ d j (ai , bh ) = g j (bh ) − g j (ai ) − p j vj − pj
(8)
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dj(ai,bh) = 1 gj(bh) - vj(bh) ≥ gj(ai)
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Step 5.- Obtaining the degree of credibility
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σ s ( ai , bh ) = C ( ai , bh ) ⋅ ∏ j∈F
1 − C ( ai , bh )
where F = { j ∈ F / d j ( ai , bh ) > C ( ai , bh )}
(9)
Step 6.- Determination of the “outranking” relationship
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1 − d j ( ai , bh )
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3. Results and Discussion
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After identifying the criteria that influence the location of these types of facilities as stated, it
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is necessary to know their weights, and for this the AHP method is used. These weights were
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obtained (table 3) through a survey of a group of three experts and using the AHP method.
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Table 3. Weight vector for the location problem for solar installations
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Knowing the weights of the criteria it is possible to assess the alternatives using the
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methodologies described. The problem is to assess locations (alternatives) obtained by GIS,
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they are divided by municipalities so that the database is divided into 13 decision matrices
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(Table 4). These matrices would have been defined in a single matrix, nevertheless in order to
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facilitate the development of the methodology described previously; a municipality will be
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selected which contains an intermediate number of alternatives.
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Table 4. Locations available by municipality
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TOPSIS
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Applying the TOPSIS method to the alternatives of each of the municipalities that are
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included in the study area through a spreadsheet, a ranking is obtained, based on the value of
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R. The best alternatives are those whose values of R are closer to unity, i.e. closer to the
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positive ideal solution.
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To develop the model, it has been applied to the municipality of San Javier, which has an
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intermediate number of plots (alternatives).
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The decision matrix is represented by 3,114 rows for total alternatives, which in Table 5
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represent only the top 10 according to the final ranking.
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The steps of the TOPSIS method allow to obtain the weighted normalized decision matrix.
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This theoretical development has not been included herein due to a lack of space. The next
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step consists in determining the positive ideal solution (PIS) and negative ideal solution
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(NIS), their values are obtained through the expression 3 (Table 6).
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Table 6. Ideal solution (PIS) and anti-ideal solution (NIS) in the municipality of San Javier
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The final steps of TOPSIS provide the separation of each alternative with respect to the PIS
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and NIS values (d+ and d- respectively) and a ranking score of alternatives (Table 7). The best
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alternative must have the closest value to 1, therefore in this case it corresponds to alternative
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A2147.
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Table 7. Measure of PIS and NIS distances and relative closeness to the ideal solution
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Figure 4 shows all the alternatives to be assessed in the municipality of San Javier (3,144),
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with the top 10 being indicated in blue, according to the TOPSIS method.
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Figure 4. Representation of the 3,144 alternatives of the municipality of San Javier and the top 10 according to
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TOPSIS
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ACCEPTED MANUSCRIPT Proceeding similarly with other municipalities that comprise the study area, all of the maps
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representing the evaluation of locations available will be obtained according to the TOPSIS
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method.
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In order to enable comparisons with other multi-criteria methodology, the alternatives were
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also assessed by the ELECTRE TRI method.
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ELECTRE TRI.
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The first step is to define the references actions that will be defined in a similar way as
399
described in Sánchez-Lozano et al (2014) i.e., by an expert who is a promoter of renewable
400
energy facilities with over 10 years of experience in the sector. All necessary parameters are
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defined in order to apply the ELECTRE TRI method (Table 8).
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Table 8. Reference actions
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Developing each of the ELECTRE TRI method steps for each municipality through a
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spreadsheet, each of the alternatives to evaluate will be classified into categories (category 1,
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2, 3 and 4). As an example, the values of the degrees of credibility and the category on the top
407
10 alternatives of the municipality of San Javier are represented in Table 9 and the indicative
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map (Figure 5) shows the classification of all the alternatives according to the ELECTRE TRI
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method for this municipality.
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Table 9. Top 10 alternatives degrees of credibility and categories
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Figure 5. Classification by categories in the municipality of San Javier according to ELECTRE TRI
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ACCEPTED MANUSCRIPT Comparative analyses
418
Although upon simple observation of Figures 5 and 6 it can seem that the results are similar
419
for the best alternatives, for a more exhaustive comparison of the top 10 alternatives in the
420
municipality chosen, these will be selected according to the TOPSIS method by identifying
421
and showing the locations (UTM Zone 30 coordinate system). These will then be compared
422
with the results obtained with the ELECTRE TRI method (Table 10). Furthermore, since the
423
ELECTRE TRI method allows a categorization without actually providing a review thereof,
424
as a measure of comparison, the value of the degree of credibility (σs) of each alternative will
425
be compared by the category to which it belongs (specified values will be shown in brackets)
426
i.e., by the value it is known to what extent each alternative exceeds the limit of the category
427
to which it belongs.
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Table 10. Comparative between TOPSIS and ELECTRE TRI methods
430
(*) This is the score obtained through the value of the degree of credibility for each category
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Considering the 3,144 alternatives of the municipality, according to calculations made by
432
ELECTRE TRI there are seven alternatives located in the best category (category 4). When
433
comparing the results (Table 5 and Table 10) it is seen that although the values obtained by
434
TOPSIS do not totally coincide with the classification provided by ELECTRE, the seven
435
alternatives classed in the best category by ELECTRE are located among the ten best rated by
436
TOPSIS. The best alternative rated according to ELECTRE TRI (A2147) coincides with the
437
highest score according to TOPSIS, while the second best alternative according to ELECTRE
438
TRI (A1989) is in sixth position according to TOPSIS. To a certain extent, it is logical that
439
the results obtained for the best alternatives are similar because both methods take into
440
account all the criteria that influence the decision of such location problems.
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The same thing happens with the rest of the better alternatives, i.e., they have good scores in
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the criteria which have high weight and, if they have some poor value for those criteria, this
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ACCEPTED MANUSCRIPT value is compensated by the values of the rest of better criteria. For example, the second best
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alternative according to ELECTRE TRI (A1989) has a poor value for the best criterion
445
(criterion g7), however this value is compensated by the good scores in the following better
446
criteria (criteria g6 and g8).
447
The results show that, although the ELECTRE TRI method works in a discreet manner and
448
benefits those alternatives which are slightly above each category and is detrimental for those
449
alternatives which are slightly below each category, the weights of the criteria are
450
fundamental to sort any alternative into its corresponding category. Alternative A1989 is a
451
clear example.
452
Then, a deep analysis will be carried out with the rest of the alternatives located in category 3.
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It should be pointed out that there is only one alternative (A994) which has veto to achieve
454
the category 4 in criteria g1 and g6, however this alternative does not have the lowest
455
credibility degree (its value is 0.90). In comparison with alternative A2674, it is worth noting
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that in spite of not having veto to achieve the best category; the credibility degree value of
457
alternative A2674 is lower than that of alternative A994. Therefore, it is demonstrated that
458
although there is veto for some criteria of one alternative, the weights of the rest of the criteria
459
are able to compensate this alternative and thus allow it to improve its credibility degree
460
value.
461
4. Conclusions
462
From the study conducted it was found that the GIS software are not only supporting tools
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that can help to address a PV farm location problem (in particular, site selection), but they can
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also generate databases in spreadsheet format which provide an ideal starting point to address
465
any issues of territorial nature.
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ACCEPTED MANUSCRIPT In our example it has been concluded that the coast of the Region of Murcia is an optimal
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place to implement solar photovoltaic farms because, once all constraints have been
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considered, it has obtained a high percentage of suitable surface available (21.25 %). In
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addition, a very useful database has been obtained for solving complex locations such as the
470
evaluation and selection of viable locations, obtained using multi-criteria decision making
471
methodologies.
472
A comparison has been made between two methods of multi-criteria decision making
473
(ELECTRE TRI and the TOPSIS method) and, although the results do not completely
474
coincide, some similarity can be seen between the best alternatives ranked with the TOPSIS
475
method and the best classified with the ELECTRE TRI method.
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It has been demonstrated that although the ELECTRE TRI method assigns a set of
477
alternatives to previously defined categories, and the TOPSIS method provides a ranking of
478
these alternatives, it is possible to make a more exhaustive comparison between both methods
479
through the value of the degree of credibility defined by ELECTRE TRI for each of the
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alternatives.
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Regarding future work of this study, economic studies could be considered such as a viability
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analysis which allows the alternatives to be assessed not only from the technical and
483
environmental point of view but also from an economic point of view. Certain limitations of
484
this study could also be countered by increasing the number of renewable technologies to
485
implement (biomass, biogas, etc.) or by applying other decision methodologies.
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Acknowledgement
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This work is partially supported by FEDER funds, the DGICYT and Junta de Andalucía
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under projects TIN2014-55024-P and P11-TIC-8001, respectively.
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ACCEPTED MANUSCRIPT Table 1. Legal Restrictions
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3 4 5 6 7 8
Urban, protected and undeveloped lands Areas of high landscape value, water infrastructure, military zones and cattle trails Watercourses and streams Archaeological, paleontological and cultural heritage sites Roads and railroad network Community interest sites (LICs) Areas of special protection for birds (ZEPAs) Mediterranean coast and mountains
RI PT
1
Denomination of the restrictions
ACCEPTED MANUSCRIPT Table 2. Random index for different matrix orders.
4
5
6
7
8
9
10
0,00
0.5247
0.8816
1.1086
1.2479
1.3417
1.4057
1.4499
1.4854
EP
TE D
M AN U
SC
RI PT
3
AC C
RI
1-2
ACCEPTED MANUSCRIPT Table 3. Weight vector for the location problem for solar installations
Criteria to implement solar photovoltaic plants w2
w3
w4
w5
w6
w7
w8
w9
w10
0.0419
0.0586
0.1271
0.0513
0.0493
0.1449
0.1855
0.1680
0.1195
0.05384
AC C
EP
TE D
M AN U
SC
RI PT
w1
ACCEPTED MANUSCRIPT Table 4. Locations available by municipality
SC
5,308 437 6,733 391 286 25,396 148 9,243 5,634 4,371 3,144 538 5,216 66,845
AC C
EP
TE D
M AN U
Águilas Alcantarilla Cartagena Fuente Alamo La Unión Lorca Los Alcázares Mazarrón Murcia Puerto Lumbreras San Javier San Pedro del Pinatar Torre Pacheco TOTAL
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Suitable locations Municipalities Alternatives
ACCEPTED Table 5. Decision Matrix of the best 10 MANUSCRIPT locations in the municipality of San Javier
g2
g3
g4
g5
g6
g7
g8
g9
g 10
(m²)
(m)
(m)
(m)
(m)
(KJ/m²·día)
(%)
(Classes)
(ºC)
a2147
1.85
397301.24
25.00
1.00
1951.40
1230.51
2040.69
0.44
4.00
17.42
a1060
4.00
245835.68
268.38
2.95
5036.51
1133.57
2048.16
1.52
5.00
17.66
a1266
3.00
139810.84
63.17
1.00
4343.95
1302.96
2045.04
0.94
6.00
17.70
a445
3.00
132862.28
153.11
1.00
5041.24
1450.61
2042.97
0.38
6.00
17.70
a2674
1.33
123041.29
176.74
94.98
2027.28
209.53
a1989
5.67
117771.77
25.00
1.00
465.84
48.74
a2754
1.50
118080.17
361.88
1.00
361.94
539.58
a705
2.00
118220.92
82.45
1.00
2402.73
574.02
a800
2.00
114530.21
120.63
31.57
2418.71
410.66
a994
0.67
122049.28
425.17
1162.65
2961.10
…
…
…
…
…
…
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g1 (Classes)
0.72
4.00
17.70
2043.97
0.49
6.00
17.60
2043.25
0.78
4.00
17.59
2042.38
0.13
8.00
17.61
2041.46
0.64
4.00
17.61
395.06
2042.59
1.08
8.00
17.70
…
…
…
…
…
AC C
EP
TE D
M AN U
SC
2043.33
ACCEPTED MANUSCRIPT Table 6. Ideal solution (PIS) and anti-ideal solution (NIS) in the municipality of San Javier 0.05409
0.00002
0.00000
0.00007
0.00713
0.00214
0.00000
0.00195
0.00097
0.00000
0.00013
0.00347
0.00883
0.00632
0.00000
0.00211
0.00413
0.00024
0.00093
EP
TE D
M AN U
SC
RI PT
0.00210
AC C
A+ A-
ACCEPTED MANUSCRIPT Table 7. Measure of PIS and NIS distances and relative closeness to the ideal solution
a1266 a445 a2674 a1989 a2754 a705 a800
0.055206
0.021591
0.034959
0.035491
0.021870
0.036460
0.021141
0.038009
0.019810
0.038703
0.019918
0.038483
0.019803
0.038485
0.019561
0.039066
0.018913
0.038281
0.018305
R 0.9249 0.6182 0.3813 0.3670
AC C
EP
TE D
M AN U
a994
0.004481
RI PT
a1060
d-
SC
a2147
d+
0.3426 0.3398 0.3398 0.3370 0.3262 0.3235
ACCEPTED MANUSCRIPT Table 8. Reference actions
AC C
EP
TE D
M AN U
SC
RI PT
g1 g2 g3 g4 g5 g6 g7 g8 g9 g10 b1 2 -30 25000 5 -1000 -10000 100 -6250 1200 16.00 4 -20 50000 8 -500 -1000 500 -2500 1700 18.00 b2 b3 7 -10 100000 10 -25 -100 750 -500 2000 20.00 Pj 0.0419 0.0586 0.1271 0.0513 0.0493 0.1449 0.1855 0.1680 0.1195 0.05384 1 5 3 4 100 100 100 150 0 17.50 qj(b) pj(b) 4 15 1000 7 200 300 300 3000 1500 17.60 6 40 25000 9 650 500 800 10000 2050 17.70 vj(b)
MANUSCRIPT Table 9. TopACCEPTED 10 alternatives degrees of credibility and categories
σs(ai,b2) 0.98 0.86 0.90 0.86 0.80 0.81 0.98 0.99 0.99 0.90
σs(ai,b3) 0.85 0.74 0.79 0.78 0.28 0.81 0.77 0.78 0.63 0.00
Category Category 4 Category 4 Category 4 Category 4 Category 3 Category 4 Category 4 Category 4 Category 3 Category 3
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σs(ai,b1) 1.00 1.00 1.00 1.00 1.00 1.00 1.00 1.00 1.00 1.00
AC C
EP
TE D
M AN U
SC
A2147 A1060 A1266 A445 A2674 A1989 A2754 A705 A800 A994
ACCEPTED MANUSCRIPT Table 10. Comparative between TOPSIS and ELECTRE-TRI methods
Coord. Y
Polygon
Plot
Subplot
A2147 A1060 A1266 A445 A2674 A1989 A2754 A705 A800 A994
691494.73 684650.28 685340.94 684587.94 689323.43 689594.93 688625.94 690543.93 692313.95 688005.95
4184050.73 4190765.84 4190072.15 4190307.66 4190124.10 4185160.10 4188111.15 4183132.10 4187014.07 4191037.62
017 001 001 001 008 019 021 016 012 003
29 13 33 13 71 22 178 28 32 25
a a a b a a a a a a
Ranking TOPSIS 0.9249 0.6182 0.3813 0.3670 0.3426 0.3398 0.3398 0.3370 0.3262 0.3235
M AN U TE D EP AC C
Category ELECTRE-TRI Category 4 (0.85) Category 4 (0.74) Category 4 (0.79) Category 4 (0.78) Category 3 (0.80) Category 4 (0.81) Category 4 (0.77) Category 4 (0.78) Category 3 (0.99) Category 3 (0.90)
RI PT
Coord. X
SC
Alternatives
AC C
EP
TE D
M AN U
SC
RI PT
ACCEPTED MANUSCRIPT
AC C
EP
TE D
M AN U
SC
RI PT
ACCEPTED MANUSCRIPT
AC C
EP
TE D
M AN U
SC
RI PT
ACCEPTED MANUSCRIPT
AC C
EP
TE D
M AN U
SC
RI PT
ACCEPTED MANUSCRIPT
AC C
EP
TE D
M AN U
SC
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ACCEPTED MANUSCRIPT
ACCEPTED MANUSCRIPT Highlights: Evaluation of optimal sites to implant optimal sites for photovoltaic solar farms. Combination of Geographic Information Systems (GIS) and Multicriteria Decision Making Method (MCDM).
RI PT
MCDM applied: Analitical Hierachy Process (AHP) method, TOPSIS method and ELECTRE TRI method.
SC
Comparative TOPSIS-ELECTRE TRI methods
GIS
TOPSIS Method Vs ELECTRE-TRI Method
M AN U
Criteria
Suitable Locations
Coast of the Region of Murcia
AC C
EP
TE D
- Restrictions
AHP
Optimal Locations