Next Article in Journal
Assessment of the Sustainable Development Capacity with the Entropy Weight Coefficient Method
Previous Article in Journal
GHG Mitigation Potential of Different Grazing Strategies in the United States Southern Great Plains
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

An Integrated Decision-Making Model for the Location of a PV Solar Plant

1
Department of Technology Management, Chung Hua University, Hsinchu 300, Taiwan
2
Program of Technology Management-Industrial Management, Chung Hua University, Hsinchu 300, Taiwan
3
Department of Industrial Management, Chung Hua University, Hsinchu 300, Taiwan
4
Department of Industrial Engineering and Management, National Chin-Yi University of Technology, Taichung 411, Taiwan
*
Author to whom correspondence should be addressed.
Sustainability 2015, 7(10), 13522-13541; https://doi.org/10.3390/su71013522
Submission received: 13 August 2015 / Revised: 23 September 2015 / Accepted: 24 September 2015 / Published: 30 September 2015
(This article belongs to the Section Energy Sustainability)

Abstract

:
Due to the increasing demand for electricity, the depletion of fossil fuels and the increase in environmental consciousness, generating power from renewable energy resources has become necessary. How to select the most appropriate site is a critical and foremost decision that must be made when setting up a renewable energy plant. This research proposes a two-stage framework for evaluating the suitability of renewable energy plant site alternatives. In the first stage, a fuzzy analytic hierarchy process (FAHP) is adopted to set the assurance region (AR) of the quantitative factors, and the AR is incorporated into data envelopment analysis (DEA) to assess the efficiencies of plant site candidates. A few sites are selected for further analysis. In the second stage, experts are invited to evaluate the qualitative characteristics of the selected sites, and FAHP is used to calculate the priorities of these sites. Solar energy is one of the most promising renewable energy sources, because of its abundance, inexhaustibility, safety and cleanliness. Based on the proposed integrated decision-making model, a case study for selecting the most appropriate photovoltaic (PV) solar plant site is examined.

1. Introduction

Energy is essential for socio-economic development and improvement of the quality of life. The use of fossil oil and other natural resources has resulted in detrimental impacts on the environment, especially through damage to the air, climate, water, land and wildlife [1]. With increasing environmental consciousness and global demand for energy, the utilization of renewable and clean energy sources is necessary. Although the global economic recession has reduced the demand for energy currently, energy generation from renewable resources is still necessary for the environment and for the economy in the long term. Solar energy, one of the best renewable energy sources with the least negative impacts on the environment, is becoming a promising renewable energy source [2].
The setup of a renewable energy power plant is a long process, from the very beginning stage of land survey and plant site selection, to the final stage of implementing and starting-up of the plant [3]. Selecting a site for a renewable energy power plant is the very first and an important task. Some relevant studies are reviewed here. Azoumah et al. [4] listed six parameters for selecting a site for a concentrating solar power (CSP) plant: solar resource assessment, availability of water and cooling mode, soil structure and geology, land issues, geography and topography of the site, the energy demand profile and a grid-connected system. Aragonés-Beltrán et al. [3] used an analytic network process (ANP) to select the best photovoltaic (PV) solar power project based on risk minimization. Noone et al. [5] presented a tool for locating sites in hillside terrain for central receiver solar thermal plants based on field efficiency and average annual normal insolation. The calculation of field efficiency includes three factors: cosine efficiency, which is the ratio of the projected heliostat area in the direction of beam insolation to the surface area, shading and blocking losses. Halasah et al. [6] employed life-cycle assessment to evaluate the energy-related impacts of PV systems at different scales of integration. The input parameters included panel efficiency, temperature coefficient, shading losses, ground cover ratio and latitude, and the input data included hourly solar radiation, wind speed and temperature. Pavlovic et al. [2] studied the possibilities of generating electrical energy from on-grid PV solar systems of 1 kW in the Republic of Srpska, and the factors considered included yearly average values of the optimal panel inclination, solar irradiation on the horizontal, vertical and optimally-inclined plane, the ratio of diffuse to global solar irradiation, Linke turbidity, average daytime temperature and 24-h average temperature. Besarati et al. [7] assessed the potential of harnessing solar radiation in different regions of Iran by generating solar radiation maps for different surface tracking modes, and the result can be used for designing PV and CSP power plants. Phillips [8] evaluated the sustainability for PV solar power plants by applying a mathematical model to the results of a qualitative-based environmental impact evaluation of the installation and operation of solar power plants. The impact categories include human health and well-being, wildlife and habitat, land use and geohydrological resources and climate change. Xiao et al. [9] constructed a site selection model for desert PV power plants using an analytic hierarchy process (AHP) and a geographic information system (GIS) in China. The major indices include climate, terrain, land cover and location, and each index contains several factors.
The evaluation and selection of an appropriate renewable energy plant site is a very complicated task, which involves the consideration of various qualitative and quantitative factors. In addition, if there are many plant sites available, the collection of relevant data from each site can be tedious or even impossible. Thus, this research proposes a two-stage evaluation model to evaluate the expected performance of renewable energy plant sites. In the first stage, a method that considers quantitative factors that are usually collectible is used to extract a number of candidate plant sites from many available plant sites. In the second stage, these candidate plant sites are further evaluated to consider qualitative factors and/or quantitative factors that are difficult to collect. The most suitable plant site can be selected as a result. To accomplish this goal, the comprehensive evaluation model is developed by integrating the AHP, data envelopment analysis (DEA), assurance region (AR) and fuzzy set theory. In the first stage, the ARs of the inputs and outputs are determined using fuzzy analytic hierarchy process (FAHP), and the DEA incorporated with AR is applied to evaluate the quantitative data of different sites. Based on the evaluation, the candidate plant sites are extracted. In the second stage, the FAHP is used to consider other qualitative data (or quantitative data that are difficult to collect), and the site with the highest priority is recommended for constructing the renewable energy plant. The flowchart of the proposed model is depicted in Figure 1.
Figure 1. Flowchart of the proposed model. AR, assurance region; FAHP, fuzzy analytic hierarchy process.
Figure 1. Flowchart of the proposed model. AR, assurance region; FAHP, fuzzy analytic hierarchy process.
Sustainability 07 13522 g001
The rest of this paper is organized as follows. Section 2 introduces the methodologies that are used for the model for renewable energy plant site selection. Section 3 presents a case study in Taiwan to examine the practicality of the proposed model. Some concluding remarks are made in the last section.

2. Methodologies

2.1. Data Envelopment Analysis

Data envelopment analysis (DEA) generates comprehensive performance measurement indexes for decision-making units (DMUs) through the evaluation of multiple inputs and outputs without the pre-assignment of criteria weights [10]. A DMU is a unit under evaluation, for example a process, a product, a polity or an alternative. Generally speaking, a DMU produces outputs and uses up inputs. Under DEA, inputs are factors that are smaller the better, while outputs are factors that are larger the better. The DMUs that locate on the envelopment, also called the frontier, are considered to be the most efficient. The position of a DMU relative to the efficient frontier, the envelopment constituted, is measured as efficiency. That is, the efficiency, also called the efficiency score, of a DMU depends on the location of the DMU relative to its efficient reference point, which is given by the projection on the efficient frontier. Since an efficient DMU is located on the efficient frontier, the reference point of an efficient DMU onto the efficient frontier is the DMU itself [10].
CCR, developed by Charnes, Cooper and Rhodes [10], is one of most popular DEA models and is adopted in this paper. In an input orientation (input minimization), maximal movement toward the frontier through proportional reduction of inputs is the focus [11].
The DEA ratio form, first proposed by Charnes et al. [10], is designed to measure the DEA efficiency of a specific DMU k′ and can be expressed by [12,13,14]:
Max   r = 1 R u r Y r k q = 1 Q v q X q k
s.t.   r = 1 R u r Y r k q = 1 Q v q X q k 1
u r q = 1 Q v q X q k ε ,   r = 1 , r   , R
v q q = 1 Q v q X q k ε ,   q = 1 , q   , Q
where X q k is the amount of the q-th input (q = 1,… q …,Q) of the k -th DMU, Y r k is the amount of the r-th output (r = 1,… r …,R) of the k -th DMU, v q is the weight given to the q-th input, u r is the weight given to the r-th output, Q is the number of inputs, R is the number of outputs and K is the number of DMUs.
However, the ratio form can yield an infinite number of optimal solutions. For instance, if (u*, v*) is an optimal solution, then (γu*, γv*) is also optimal for γ > 0. The transformation developed by Charnes and Cooper [15] for linear fractional programming was utilized in the DEA study [10] to define an equivalent relation that partitioned the set of feasible solutions into equivalence classes. The transformed DEA model can be expressed as the following linear programming (LP) problem [12,13,14]:
Max   r = 1 R u r Y r k
s.t.   q = 1 Q v q X q k = 1
r = 1 R u r Y r k q = 1 Q v q X q k 0 ,   k = 1 , k , K
u r ε ,   r = 1 , r , R
v q ε ,   q = 1 , q , Q
The above primal model is difficult to solve, and the dual problem of the LP is proposed [12,13,14]:
Min   h k = θ k ε ( q = 1 Q s q + r = 1 R s r + )
s.t.   k = 1 K λ k X q k θ k X q k + s q = 0 ,   q = 1 , q , Q
k = 1 K λ k Y r k    s r + = Y r k ,   r = 1 , r , R
λ k 0 ,   k = 1 , k , K
s q 0 ,   q = 1 , q , Q
s r + 0 ,   r = 1 , r , R
θ k   u n c o n s t r a i n e d ,   k = 1 , k , K
where ε is a non-Archimedean (infinitesimal) constant, s q , s r + are the slack variables of inputs and outputs, respectively, λ k is the weight for DMUk and h k is the relative efficiency indicator of the k′-th DMU.
In Equation (10), the optimal h k * indicates a DEA efficiency score in a manner that h k * = 1 indicates the state of DEA efficiency, while h k * < 1 represents DEA inefficiency. Note that the primal model has K + R + Q + 1 constraints, whilst the dual model has Q + R constraints. Since K, the number of units, is usually considerably larger than Q + R, the number of inputs and outputs, the primal model has many more constraints than the dual model. Generally speaking, the more constraints there are in an LP, the more difficult it is to solve. Therefore, the dual DEA model rather than the primal is usually solved.

2.2. Weights of Inputs/Outputs in DEA

Under the conventional DEA, the weights given to inputs and outputs to evaluate a DMU are chosen in a manner to maximize the efficiency score of that DMU [16]. That is, the DEA model does not require a priori weights on inputs and outputs, and the weights are determined by solving the DEA models, such as the models developed by Charnes et al. [10], so-called CCR, when efficient production is characterized by constant returns to scale, or by Banker et al. [13,17], so-called BCC (Banker, Charnes and Cooper), when variable returns to scale are assumed [18]. Complete input/output weight flexibility can result in inappropriate efficiency estimation [18]. Therefore, a DMU may be efficient even if it performs best in one input (output) and performs inferior in other inputs (outputs). However, in real-world problems, some factors may be more important than others, and experts’ subjective opinions on the importance of the factors should be incorporated into the methodology. One of the common methods to do so in DEA is the assurance regions (ARs) model, in which the upper bound and lower bound of a ratio of the weights of two inputs (outputs) are pre-determined [19,20]. For every pair ( p x , p y ) of inputs/outputs, the ratio w p x / w p y must be bounded by L p x p y and U p x p y as [19,20,21]:
L p x p y w p x / w p y U p x p y
Even though many works have applied AHP to set AR, another problem with AR is that experts may have vagueness or ambiguity in expressing their opinions. Under such circumstances, the fuzzy set theory can be incorporated into the DEA/AR model. Liu [14] developed a fuzzy DEA/AR method to evaluate the performance of flexible manufacturing system (FMS) alternatives when the input and output data contained crisp and fuzzy data. A pair of two-level mathematical programs was formulated to calculate the lower and upper bounds of the fuzzy efficiency score of the alternatives based on the extension principle [22]. Liu and Chuang [23] applied the proposed fuzzy DEA/AR method to evaluate the performance of university libraries. Lee et al. [19] applied FAHP to set the AR of the factors, and then, DEA was carried out to assess the business performance of PV firms. That is, FAHP is used to extract experts’ opinions on the AR of the factors, which is represented by Equation (17). With the addition of Equation (17) to Equations (10) to (16), this DEA/AR method can be used to evaluate the performance of the firms.
In the first stage of this research, FAHP is applied to set the AR of the quantitative factors. The calculated AR is incorporated into DEA to assess the efficiencies of renewable plant site candidates, and the most suitable candidates are selected for further evaluations.

2.3. Fuzzy Analytic Hierarchy Process

AHP, a mathematically-based multi-criteria decision-making (MCDM) tool proposed by Saaty [24], has been adopted in various academic fields and in real practice. AHP decomposes a complex problem into several factors into hierarchical levels, and each factor can be decomposed into several sub-factors at a lower level. The factors (sub-factors) of the same hierarchical level are compared relative to their impact on their higher level factor. The incorporation of the fuzzy set theory with AHP, or so-called FAHP, has been adopted abundantly in recent years. This is due to the facts that decision-makers may not have complete information or a full understanding of all aspects of the problem and that the experiences and judgments of humans are not well defined [25,26]. As a result, pairwise comparison under the conventional AHP, which requires the selection of arbitrary values in the process, may not be appropriate. Under FAHP, uncertainty can be considered in pairwise comparison values.
Different models for the FAHP have been proposed by scholars. In this study, the major steps of the FAHP are as follows [27,28,29]:
Step 1: Define the unstructured problem: The problem should be stated clearly and be put into a broad context, including the objectives and the outcomes.
Step 2: Decompose the problem into a hierarchical structure: The problem is decomposed into a hierarchy, like a decision tree, with the overall objective of the problem at the top level and several criteria at a lower level. Each next lower level can contain sub-criteria, and the lowest level usually contains alternatives. A standard format for an FAHP decision model is illustrated in Figure 2.
Figure 2. A hierarchy for the AHP.
Figure 2. A hierarchy for the AHP.
Sustainability 07 13522 g002
Step 3: Employ questionnaires and pairwise comparisons: Experts are asked to pairwise compare the elements in a questionnaire using five linguistic levels, as shown in Table 1. The linguistic variables are transformed into triangular fuzzy numbers. For example, with pairwise comparison of criteria with respect to the objective, a matrix ( Λ ˜ e ) for expert e, is as follows:
Λ ˜ e = C 1 C 2 C n C 1 C 2 C n [ 1 a ˜ 12e ... a ˜ 1ne 1 / a ˜ 12e 1 ... a ˜ 2ne 1 1 / a ˜ 1ne 1 / a ˜ 2ne ... 1 ]
where n is the number of criteria.
Step 4: Aggregate experts’ opinions and build aggregated pairwise comparison matrices: If there are E experts, the geometric average approach is employed to aggregate experts’ responses, and a synthetic triangular fuzzy number is obtained:
r ˜ i j = ( a ˜ i j 1 a ˜ i j 2 ...... a ˜ i j E ) 1 / E
Each triangular fuzzy number is then defuzzified into a crisp number F i j by the center of gravity (COG) method. The crisp value for a triangular fuzzy number r ˜ i j = ( l i j ,   m i j ,   u i j ) is [30,31]:
F i j = [ ( u i j l i j ) + ( m i j l i j ) ] 3 + l i j = l i j + m i j + u i j 3
Then, the aggregated pairwise comparison matrix is:
Λ = [ 1 F 12 F 1 j 1 F 12 1 F 2 j 1 1 F i j 1 F i j 1 1 1 F 1 j 1 F 2 j 1 ]
Table 1. Membership functions of triangular fuzzy numbers.
Table 1. Membership functions of triangular fuzzy numbers.
Fuzzy NumberLinguistic VariableMembership Function of Fuzzy Number
1 ˜ Equally important(1, 1, 3)
3 ˜ Moderately important(1, 3, 5)
5 ˜ Important(3, 5, 7)
7 ˜ Very important(5, 7, 9)
9 ˜ Extremely important(7, 9, 9)
Step 5: Calculate the priority vector for each aggregated pairwise comparison matrix: Derive priority vectors for all aggregated comparison matrices by:
Λ w = λ max w
where Λ is the matrix of pairwise comparisons, w is the eigenvector and λ max is the largest eigenvalue of Λ .
Step 6: Check the consistency property of each aggregated pairwise comparison matrix: The consistency of judgments that experts demonstrate during the pairwise comparisons has an important impact on the quality of the outcomes. The consistency index (CI) and consistency ratio (CR) are defined as [24,32]:
C I = λ max n n 1
C R   =   C I RI
where RI is random index, as shown in Table 2 [24]. When CR is exceeding 0.1, it is an indication of inconsistent judgment. The experts need to revise the original values in the pairwise comparison matrix. The whole process needs to be repeated again.
Table 2. Random index (RI) [24].
Table 2. Random index (RI) [24].
Order of Matrix (n)2345678
RI0.000.580.901.121.241.321.41
Step 7: Calculate the overall rating for alternatives by aggregating the relative priorities of the elements: Based on Figure 1, establish the total ranking number, Φ , of the alternatives by multiplying the judgment matrix W 32 with the corresponding weight vector, w 21 .
Φ = W 32 w 21 = [ ϕ 1 ϕ 2 ϕ k ]
The priority vectors for the aggregated comparison matrices are synthesized to obtain overall priorities for alternatives. The alternative with a higher rating is considered to be preferable.

3. Case Study

A two-stage evaluation model by integrating DEA and FAHP is constructed to assess various feasible sites for a renewable energy plant. In the model, the renewable energy plant site selection problem is defined first, and the factors for evaluating the suitability of various sites are selected next. Stage I is a plant site screening stage. Among many available plants sites, several candidate plant sites are selected by considering quantitative factors. This is done by applying the DEA-fuzzy AR method. In Stage II, the candidate plant sites are further evaluated to consider qualitative factors. By applying the FAHP, the most suitable plant site can be selected. A case study of the solar plant site selection in Taiwan is carried out using the proposed model.
Step 1: Define the renewable energy plant site evaluation problem: Experts in the renewable energy industry are invited to define the problem.
Step 2: Select the factors for evaluating renewable energy plant sites: A literature review, including solar energy conversion and renewable energy site selection, is carried out first [33,34,35,36,37,38,39,40], and experts in the solar energy industry in Taiwan are then interviewed to identify critical factors. The critical factors are considered and categorized into quantitative and qualitative factors. In Stage I, only quantitative factors are considered. As stated before, when applying DEA, inputs are critical factors that are smaller the better, and outputs are critical factors that are larger the better. Due to the information accessibility of various sites and the importance of various factors, we select two inputs and two outputs for the quantitative factors. The two inputs are temperature (I1) and wind speed (I2). The two outputs are sunshine hours (O1) and elevation (O2). The definitions of the inputs and outputs are listed in Table 3. Because land is abundant and less expensive in southern Taiwan and sunshine is plentiful there, five counties (cities) with 15 towns/districts that are most suitable for setting PV solar plant sites are selected, namely A1 to A15, respectively. The data for these sites are listed in Table 4. The potential locations are shown in Figure 3.
Stage I: Selection of candidate solar plant sites using DEA-fuzzy AR: The CCR model is first applied on the case study. The results are shown in Table 5. Table 5 shows the efficiency and the rank of each DMU. The “Peers” column indicates the number of reference points that the DMU used to calculate its efficiency, and the “Reference set” lists the reference points to which the DMU is compared. Among the 15 DMUs, six of them are efficient with a value of one. For example, A4 is efficient. Thus, it ranks the first among all DMUs. Since A4 is located on the efficient frontier, its reference point is itself, and it does not have a peer to which to compare. A1 has an efficiency value of 87.13, and it is not efficient. Its rank is 10. Its reference set includes two peers, A9 and A11. This means that A1 is found inefficient when compared to A9 and A11.
Table 3. Definitions of inputs and outputs.
Table 3. Definitions of inputs and outputs.
FactorsDefinition
Inputs
Temperature (I1)A numerical measure of hot or cold by detection of heat radiation. According to Radziemska [34], temperature increases lead to a decrease of the output power and of the conversion efficiency of the PV module. That is, the more sunshine a panel receives, the hotter the panel gets, and in turn, the conversion efficiency decreases. The heat factor can reduce output power by 10% to 25%, depending on the location and the equipment [39].
Wind speed (I2)Wind is the flow of gases on a large scale. Wind causes small particles to be lifted, and the suspended particles may impact the solar panels and equipment, which need to resist wind loads and uplift. Wind may cause erosion and operation failures of solar plants.
Outputs
Sunshine hours (O1)A climatological indicator to measure the duration of sunshine in a period (here, a year) for a given location, typically expressed as an average of several years. The sunshine duration is the period during which direct solar irradiance exceeds a threshold value of 120 W/m² [35]. A longer sunshine duration can convert to a larger amount of output power.
Elevation(O2)The height of a geographic location above sea level. A higher elevation means a shorter distance for solar radiation to reach the ground and a higher intensity of solar irradiance. A higher intensity of solar irradiance converts to a larger amount of output power.
Table 4. Quantitative data of the solar plant sites.
Table 4. Quantitative data of the solar plant sites.
County/CityTown/DistrictTemperature (°C)Wind Speed (m/sec)Sunshine Hours (h/year)Elevation (m)
Yunlin CountyA123.801.501779.4731
A223.431.731915.534
A319.904.131452.008
Chiayi CountyA422.670.631588.63265
A516.870.40976.43130
A623.473.272378.6712
Tainan CityA723.430.871718.0021
A823.704.532332.637
A923.932.602320.0312
Kaohsiung CityA1024.130.731605.1751
A1123.600.231719.2775
A1222.800.431605.20253
Pingtung CountyA1325.173.472029.7027
A1424.570.601255.6028
A1524.570.101560.8016
Figure 3. The potential locations in Taiwan.
Figure 3. The potential locations in Taiwan.
Sustainability 07 13522 g003
Table 5. DEA performance results. DMU, decision-making unit.
Table 5. DEA performance results. DMU, decision-making unit.
DMUEfficiencyRankPeersReference Set
A410010A4
A610010A6
A910010A9
A1110010A11
A1210010A12
A1510010A15
A897.171A6
A292.482A9, A11
A792.2792A9, A11
A187.13102A9, A11
A1085.44112A9, A11
A1381.38122A4, A6
A580.05133A9, A11, A12
A372.08142A4, A6
A1466.9152A9, A11
As mentioned before, the conventional DEA cannot incorporate experts’ opinions on the importance of the inputs/outputs; thus, DEA-fuzzy AR is applied next to the case study. The FAHP is used to set the ARs for the inputs and outputs first, and then, the DEA/AR is applied to calculate the efficiencies of the solar plant sites. Eight experts in the solar industry were asked to pairwise compare the importance of the inputs/outputs. A question, such as “which input is more important in selecting the location of the solar plant site and how much more?” was asked, and a pairwise comparison with five linguistic terms was used. The comparison matrix for the inputs by the first expert by applying Equation (18) is shown as follows:
Λ ˜ I1 = I 1 I 2 [ (1, 1, 1) (  3, 5, 7 ) ( 1 / 7 , 1/5,1/3 ) ( 1, 1, 1) ]          I 1             I 2       
All experts’ opinions are synthesized using the geometric average method, and the fuzzy aggregated pairwise comparison matrix of the inputs by applying Equation (19) is:
Λ ˜ I = I 1 I 2 [ (1, 1, 1) ( 2.515 , 4.639 , 6.293 ) ( 0.159 , 0.216 , 0.398 ) ( 1, 1, 1) ]         I 1                           I 2       
The fuzzy aggregated pairwise comparison matrix of the inputs is transformed into a defuzzified aggregated pairwise comparison matrix using the center of gravity (COG) method (Equation (20)). By applying Equation (21), the aggregated pairwise comparison matrix is:
Λ I = I 1 I 2 [ 1 4.482 0.223 1 ]          I 1     I 2       
By applying Equation (22), the maximum eigenvalue and the eigenvector for the defuzzified aggregated pairwise comparison matrix of the inputs are:
w I = I 1 I 2 [ 0.818 0.182 ]
λ max = 2.00
Because there are only two inputs, the pairwise comparison is always consistent, and the CI and CR calculations are not necessary. If the number of inputs is equal to or more than three, the consistency test must be performed.
Two matrices are formed based on the fuzzy aggregated pairwise comparison matrix in Equation (27): one contains all low values in the fuzzy matrix, and the other contains all high values in the fuzzy matrix.
Λ I L = I 1 I 2 [ 1 2.515 0.398 1 ]          I 1         I 2       
Λ I U = I 1 I 2 [ 1 6.293 0.159 1 ]          I 1         I 2       
The priorities of the inputs under the two matrices are calculated using Equation (31), and they are:
w I L = I 1 I 2 [ 0.715 0.285 ]
w I U = I 1 I 2 [ 0.863 0.137 ]
The same procedure is carried out to calculate the priorities of the outputs, and they are:
w O L = O 1 O 2 [ 0.762 0.238 ]
w I U = O 1 O 2 [ 0.871 0.129 ]
For temperature (I1), the priority ranges from 0.715 to 0.863, i.e., I1 = [0.715, 0.863]. For wind speed (I2), the priority ranges from 0.138 to 0.285, i.e., I2 = [0.138, 0285]. For sunshine hours (O1), the priority ranges from 0.762 to 0.871, i.e., O1 = [0.762, 0.871]. For elevation (O2), the priority ranges from 0.129 to 0.238, i.e., O2 = [0.129, 0.238]. Based on the AR concept discussed before [21,22,25], the AR for each pair of inputs and each pair of outputs can be calculated as shown in Table 6 and Table 7.
Table 6. Assurance range (AR) for inputs.
Table 6. Assurance range (AR) for inputs.
Input RatioLower BoundUpper Bound
wI1/wI20.715/0.285 = 2.5090.863/0.138 = 6.254
Table 7. Assurance range (AR) for outputs.
Table 7. Assurance range (AR) for outputs.
Output RatioLower BoundUpper Bound
wO1/wO20.762/0.238 = 3.2020.871/0.129 = 6.752
Table 8. DEA-fuzzy AR performance results.
Table 8. DEA-fuzzy AR performance results.
DMUEfficiencyRankPeersReference Set
A1210010A12
A494.1121A12
A1191.1431A12
A576.5541A12
A1554.4351A12
A1053.2861A12
A139.6171A12
A1435.1281A12
A1334.2991A12
A732.21101A12
A620.19111A12
A919.92121A12
A314.99131A12
A812.26141A12
A27.44151A12
Using the ARs in Table 6 and Table 7, DEA is run to evaluate the efficiencies of the solar plant sites. As seen in Table 8, the result shows that, considering experts’ opinions on the importance of the inputs and outputs, only one plant site, A12, is efficient, instead of six under the conventional DEA. Under the DEA concept, only the DMU with an efficiency of 100% is treated as efficient. Therefore, all DMUs except A12 are inefficient. The results are generated from the DEA-fuzzy AR model, and only A12 is located on the efficient frontier. The other DMUs, when compared to A12 as a reference point, are found inefficient. Two other DMUs that have higher efficiency scores are A4 and A11, with efficiencies of 94.11 and 91.14, respectively. The efficiencies of all other solar plant sites are less than 77. Because the selection of solar plant site cannot only consider quantitative factors, many other qualitative factors need to be considered, too. Therefore, in this stage, three plant sites that have higher efficiency scores and that outperform others are selected for further analysis.
The selection of these three plant sites is done arbitrarily by the authors. If there are several DMUs that are 100% efficient, they will be automatically selected for the evaluation in the next stage. In this case, however, only one plant site is efficient under the first-stage analysis. Since both quantitative and qualitative factors should be considered in the problem, the selection of plant A12 is based on only quantitative factors, and completing the evaluation process without going through Stage II analysis is not recommended. Therefore, more efficient DMUs are selected in this stage. Since the efficiency difference between A11 (ranked third) and A5 (ranked fourth) is 14.59%, a rather large number, A5 is not selected for the next-stage evaluation.
Figure 4. The hierarchy.
Figure 4. The hierarchy.
Sustainability 07 13522 g004
Stage II: Selection of the most suitable solar plant site using FAHP: In Stage I, inputs and outputs are all quantitative factors. In Stage II, factors that are qualitative in nature or quantitative but difficult to measure or collect are considered here. With a comprehensive literature review and consultation with experts in the industry, the factors for determining the suitability of solar plant sites are collected, and a hierarchy is constructed, as shown in Figure 4. Under the goal, there are three criteria, each of which has several detailed criteria. For example, under criterion costs (C2), the detailed criteria are land cost (D21), construction cost (D22), equipment cost (D23), operation and maintenance cost (D24) and electric power transmission cost (D25). The definitions of the detailed criteria are listed in Table 9. The three solar plant sites generated in Stage I are the alternatives.
Table 9. Definitions of detailed criteria.
Table 9. Definitions of detailed criteria.
Detailed CriteriaDefinition
Support mechanisms (D11)Different government policy instruments have been implemented to support solar PV power plants. Some incentives include feed-in-tariffs, investment tax credits, subsidies and favorable financing. The incentives may be different at different locations.
Protection laws (D12)The existing laws and regulations might constrain the development of solar plants in different areas, such as farm land and inhabited areas.
Service life (D13)Expected useful life of PV solar plant. The electricity buy-back period may be different, and the weather and geological conditions, such as temperature, humidity, salt-laden air, may affect the service life of the solar plant.
Land cost (D21)The cost of obtaining the land required for setting up the solar plant.
Construction cost (D22)The total cost for constructing the solar plant, including all of the capital expenses related to the initial establishment of the plant, such as buildings, roads, etc.
Equipment cost (D23)Costs for the initial purchase and installation of the equipment and facilities.
Operation and maintenance cost (D24)Costs for everyday operation of the solar plant and repair and maintenance, including labor, material, etc.
Electric power transmission cost (D25)The transfer cost of electrical energy from the solar power plant to electrical substations located near demand centers.
Human well-being (D31)The negative impacts of the solar plant on the health of the residents and aesthetics in the area.
Wild life and habitat (D32)The negative impacts of the solar plant on the animal inhabitants and plants in the area.
Topography (D33)A description of relief or terrain, the three-dimensional quality of the surface, and the identification of specific landforms of a place. A solar plant needs to be built in a flat place where solar radiation can be reached easily.
Land availability (D34)The availability of land for setting up a solar plant with economies of scale and for future expansion.
A questionnaire is prepared, and the eight experts are invited to fill out the questionnaire; the results from each expert can then form pairwise comparison matrices. After the calculation, we can obtain the priorities of the eigenvectors for defuzzified aggregated pairwise comparison matrices, as shown in Table 10. Among the three criteria, costs (C2) have the highest priority with 0.493, followed by policies (C1) with 0.269 and environment conditions (C3) with 0.238. This implies that when selecting the most appropriate solar plant site, the overall costs for constructing and running the solar plant in a certain site are considered the most important criterion by the experts. Under the policies (C1) criterion, service life (D13), with a priority of 0.466, is the most important detailed criterion, followed by support mechanisms (D11) with a priority of 0.319 and protection laws (D12) with 0.215. Service life estimates the expected useful life of the PV solar plant and ultimately determines the duration and amount of power generation of the plant. Therefore, it is a rather important detailed criterion. Under the costs (C2) criterion, operation and maintenance cost (D24), with a priority of 0.382, is the most important detailed criterion. Land cost (D21) ranks the second (0.190), followed by electric power transmission cost (D25) with a priority of 0.177 and construction cost (D22) with a priority of 0.171. Operation and maintenance cost (D24) occurs continuously as long as the solar plant is under operation. The costs for everyday operation of the solar plant and repair and maintenance, including labor and material, depend on the transportation cost and the availability of human resources in that area. Therefore, a good plant site can reduce the expected long-term operation and maintenance cost. Under the environment conditions (C3) criterion, wild life and habitat (D32) has the highest priority with 0.432. Human well-being (D31) with a priority of 0.362 ranked the second. Due to the rise of environmental awareness, environment impact assessment is necessary before a solar plant is allowed to be constructed. Thus, the negative impacts of the solar plant on the animal inhabitants and plants and on human well-being in the area need to be considered seriously.
The synthesized priority of a detailed criterion, which is calculated by multiplying the priority of the detailed criterion by the priority of its upper-level criterion, shows the overall importance of the detailed criterion. The most important detailed criterion is operation and maintenance cost (D24), with a priority of 0.188, followed by service life (D13) and wild life and habitat (D32), with priorities of 0.125 and 0.103, respectively. Some other important detailed criteria include land cost (D21) (0.094), electric power transmission cost (D25) (0.087), support mechanisms (D11) (0.086) and human well-being (D31) (0.086).
Table 10. Priorities of factors.
Table 10. Priorities of factors.
CriteriaDetailed CriteriaPrioritiesRankSynthesized PrioritiesSynthesized Rank
Policies (C1) (0.269)Support mechanisms (D11)0.31920.0866
Protection laws (D12)0.21530.0589
Service life (D13)0.46610.1252
Costs (C2) (0.493)Land cost (D21)0.19020.0944
Construction cost (D22)0.17140.0848
Equipment cost (D23)0.08050.04010
Operation and maintenance cost (D24)0.38210.1881
Electric power transmission cost (D25)0.17730.0875
Environment conditions (C3) (0.238)Human well-being (D31)0.36220.0866
Wild life and habitat (D32)0.43210.1033
Topography (D33)0.14430.03411
Land availability (D34)0.06240.01512
Table 11 shows the expected performance of the solar plant sites under each criterion. For example, under support mechanisms (D11), A11 has the highest priority of 0.626, followed by A12 and A4, with priorities of 0.231 and 0.143, respectively. The solar plant site that performs the best under a sub-criterion is highlighted in gray in Table 11. Solar plant site A4 performs the best under five sub-criteria: service life (D13), land cost (D21), construction cost (D22), human well-being (D31) and wild life and habitat (D32). Solar plant site A11 performs the best under six sub-criteria: support mechanisms (D11), equipment cost (D23), operation and maintenance cost (D24), electric power transmission cost (D25), topography (D33) and land availability (D34). Solar plant site A12 performs the best under one sub-criterion only, i.e., protection laws (D12).
Finally, the overall priorities of the solar plant sites are obtained by synthesizing the priorities. For example, the overall priority of A4 is calculated as follows:
0.086 × 0.143 + 0.058 × 0.176 + 0.125 × 0.478 + 0.094 × 0.557 + 0.084 × 0.392 + 0.040 × 0.318 + 0.188 × 0.267 + 0.087 × 0.300 + 0.086 × 0.385 + 0.103 × 0.447 + 0.034 × 0.381 + 0.015 × 0.277 = 0.353
The priorities of A11 and A12 are 0.402 and 0.245, respectively. The result shows that A11 has the highest overall priority. Therefore, A11 should be selected for building the solar plant.
Table 11. Priorities of solar plant sites.
Table 11. Priorities of solar plant sites.
CriteriaDetailed CriteriaSynthesized PrioritiesA4A11A12
Policies (C1)Support mechanisms (D11)0.0860.1430.6260.231
Protection laws (D12)0.0580.1760.3750.449
Service life (D13)0.1250.4780.3330.189
Costs (C2)Land cost (D21)0.0940.5570.1880.255
Construction cost (D22)0.0840.3920.3740.233
Equipment cost (D23)0.0400.3180.4650.216
Operation and maintenance cost (D24)0.1880.2670.5390.195
Electric power transmission cost (D25)0.0870.3000.4250.275
Environment conditions (C3)Human well-being (D31)0.0860.3850.3110.304
Wild life and habitat (D32)0.1030.4470.3040.250
Topography (D33)0.0340.3810.3940.225
Land availability (D34)0.0150.2770.4810.241
Synthesized priorities--0.3530.4020.245

4. Conclusions

To accommodate the increasing demand for electricity while confronting the finite amounts of world fossil fuel resources and environmental concerns, many countries are putting a greater effort into generating power from renewable energies. To construct a renewable energy plant, the selection of the most appropriate renewable energy plant site is the first of a series of stages, and it is a very challenging job, since the decision has a great impact on the operation outcome of the renewable energy plant. In this paper, an evaluation framework by integrating AHP, DEA, AR and fuzzy set theory is constructed to evaluate the suitability of renewable energy plant sites. Because various sites may need to be considered, a screening process is necessary to select some candidate sites first. Thus, in the first stage of the model, FAHP is adopted to set the AR of the quantitative factors, and DEA with AR is then used to select the renewable energy plant site candidates. In the second stage, FAHP is applied to find the most suitable plant site from the selected candidates.
Solar energy, one of the best renewable energy sources, is becoming a prospect of unlimited clean and safe energy. The proposed framework is applied to evaluate different districts/towns in Taiwan for constructing a PV solar plant. In the case study, A12 is the most efficient plant site in Phase I, which applies DEA-fuzzy AR analysis to consider quantitative factors. However, the plant site performs inferior compared to the other two sites in Phase II, which adopts FAHP to consider qualitative factors. On the other hand, A11, which passes the Phase I analysis, performs rather outstanding in Phase II. Therefore, A11 is the most suitable plant site overall. In the future, a model that can be applied to select a specific site in a district/town will be constructed to consider more detailed factors.
Due to the size of Taiwan, and in this case only southern Taiwan is considered, the data of the inputs and outputs may not be representative enough to be decisive factors. For example, the temperature and wind speed values are rather similar in different locations. However, if the decision-making is done in a larger geographical area, more diverse data may be present, and the model can lead to a more significant result in obtaining potential solar plant locations.

Acknowledgements

This work was supported in part by the National Science Council in Taiwan under Grant NSC 100-2628-H-216-001-MY3.

Author Contributions

The research is designed and performed by Amy H. I. Lee and He-Yau Kang. The data was collected by Chun-Yu Lin and Kuan-Chin Shen. Analysis of data was performed by He-Yau Kang, Chun-Yu Lin and Kuan-Chin Shen. Finally, the paper is written by Amy H. I. Lee and He-Yau Kang. All authors read and approved the final manuscript.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Tsoutsos, T.; Frantzeskaki, N.; Gekas, V. Environmental impacts from the solar energy technologies. Energ. Pol. 2005, 33, 289–296. [Google Scholar] [CrossRef]
  2. Pavlovic, T.M.; Milosavljevic, D.D.; Mirjanic, D.; Pantic, L.S.; Radonjic, I.S.; Pirsl, D. Assessments and perspectives of PV solar power engineering in the Republic of Srpska (Bosnia and Herzegovina). Renew. Sustain. Energ. Rev. 2013, 18, 119–133. [Google Scholar] [CrossRef]
  3. Aragonés-Beltrán, P.; Chaparro-González, F.; Pastor-Ferrando, J.P.; Rodríguez-Pozo, F. An ANP-based approach for the selection of photovoltaic solar power plant investment projects. Renew. Sustain. Energ. Rev. 2010, 14, 249–264. [Google Scholar] [CrossRef]
  4. Azoumah, Y.; Ramdé, E.W.; Tapsoba, G.; Thiam, S. Siting guidelines for concentrating solar power plants in the Sahel: case study of Burkina Faso. Sol. Energ. 2010, 84, 1545–1553. [Google Scholar] [CrossRef]
  5. Noone, C.J.; Ghobeity, A.; Slocum, A.H.; Tzamtzis, G.; Mitsos, A. Site selection for hillside central receiver solar thermal plants. Sol. Energ. 2011, 85, 839–848. [Google Scholar] [CrossRef]
  6. Halasah, S.A.; Pearlmutter, D.; Feuermann, D. Field installation versus local integration of photovoltaic systems and their effect on energy evaluation metrics. Energ. Pol. 2013, 52, 462–471. [Google Scholar] [CrossRef]
  7. Besarati, S.M.; Padilla, R.V.; Goswami, D.Y.; Stefanakos, E. The potential of harnessing solar radiation in Iran: generating solar maps and viability study of PV power plants. Renew. Energ. 2013, 53, 193–199. [Google Scholar] [CrossRef]
  8. Phillips, J. Determining the sustainability of large-scale photovoltaic solar power plants. Renew. Sustain. Energ. Rev. 2013, 27, 435–444. [Google Scholar] [CrossRef]
  9. Xiao, J.; Yao, Z.; Qu, J.; Sun, J. Research on an optimal site selection model for desert photovoltaic power plants based on analytic hierarchy process and geographic information system. J. Renew. Sustain. Energ. 2013, 5, 1–15. [Google Scholar] [CrossRef]
  10. Charnes, A.; Cooper, W.W.; Rhodes, E. Measuring the efficiency of decision making units. Eur. J. Oper. Res. 1978, 2, 429–444. [Google Scholar] [CrossRef]
  11. Chung, S.H.; Pearn, W.L.; Lee, A.H.I. Measuring production performance with different product mixes in semiconductor fabricator using data envelopment analysis (DEA). Int. J. Ind. Eng. Appl. Pract. 2006, 13, 5–17. [Google Scholar]
  12. Shang, J.; Sueyoshi, T. A unified framework for the selection of a flexible manufacturing system. Eur. J. Oper. Res. 1995, 85, 297–315. [Google Scholar]
  13. Charnes, A.; Cooper, W.W.; Lewin, A.Y.; Seiford, L.M. Data Envelopment Analysis: Theory, Methodology, and Applications; Kluwer Academic Press: Norwell, MA, USA, 1996. [Google Scholar]
  14. Liu, S.T. A fuzzy DEA/AR approach to the selection of flexible manufacturing systems. Comput. Ind. Eng. 2008, 54, 66–76. [Google Scholar] [CrossRef]
  15. Charnes, A.; Cooper, W.W. Programming with linear fractional functions. Nav. Res. Logist Q 1962, 9, 181–186. [Google Scholar]
  16. Allen, R.; Athanassopoulos, A.; Dyson, R.G.; Thanassoulis, E. Weights restrictions and value judgments in data envelopment analysis: evolution, development and future directions. Ann. Oper. Res. 1997, 73, 13–34. [Google Scholar] [CrossRef]
  17. Banker, R.D.; Charnes, A.; Cooper, W.W. Some models for estimating technical and scale inefficiencies in data envelopment analysis. Manag. Sci. 1984, 30, 1078–1092. [Google Scholar] [CrossRef]
  18. Thanassoulis, E.; Allen, R. Simulating weights restrictions in data envelopment analysis by means of unobserved DMUs. Manag. Sci. 1998, 44, 586–594. [Google Scholar] [CrossRef]
  19. Lee, A.H.I.; Kang, H.Y.; Lin, C.Y. A performance evaluation model using FAHP/DEA and Malmquist productivity index to assess the photovoltaics industry in Taiwan. J. Test. Eval. 2014, 42, 211–228. [Google Scholar] [CrossRef]
  20. Thompson, R.G.; Langemeir, L.N.; Lee, C.; Lee, E.; Thrall, R.M. The role of multiplier bounds in efficiency analysis with application to Kansas farming. J. Econ. 1990, 1, 93–108. [Google Scholar] [CrossRef]
  21. Takamura, Y.; Tone, K. A comparative site evaluation study for relocating Japanese government agencies out of Tokyo. Soc. Econ. Plann. Sci. 2003, 37, 85–102. [Google Scholar] [CrossRef]
  22. Zadeh, L.A. Fuzzy sets. Inform. Contr. 1965, 8, 338–353. [Google Scholar] [CrossRef]
  23. Liu, S.T.; Chuang, M. Fuzzy efficiency measures in fuzzy DEA/AR with application. Expert. Syst. Appl. 2009, 36, 1105–1113. [Google Scholar] [CrossRef]
  24. Saaty, T.L. The Analytic Hierarchy Process; McGraw-Hill: New York, NY, USA, 1980. [Google Scholar]
  25. Chung, S.H.; Lee, A.H.I.; Pearn, W.L. Product mix optimization for semiconductor manufacturing based on AHP and ANP analysis. Int. J. Adv. Manuf. Tech. 2005, 25, 1144–1156. [Google Scholar] [CrossRef]
  26. Cheng, C.H. Evaluating weapon systems using ranking fuzzy numbers. Fuzzy Set. Syst. 1999, 107, 25–35. [Google Scholar] [CrossRef]
  27. Cheng, E.W.L.; Li, H.; Ho, D.C.K. Analytic hierarchy process (AHP). Measur. Bus. Excel. 2002, 6, 33–37. [Google Scholar] [CrossRef]
  28. Lee, A.H.I.; Kang, H.-Y.; Yang, C.Y.; Lin, C.Y. An evaluation framework for product planning using FANP, QFD and multi-choice goal programming. Int. J. Prod. Res. 2010, 48, 3977–3997. [Google Scholar] [CrossRef]
  29. Kang, H.-Y.; Lee-Amy, H.I.; Yang, C.-Y. A fuzzy ANP model for supplier selection as applied to IC packaging. J. Intell. Manuf. 2012, 23, 1477–1488. [Google Scholar] [CrossRef]
  30. Yagar, R.R. On a general class of fuzzy connectives. Fuzzy Set. Syst. 1980, 4, 235–242. [Google Scholar] [CrossRef]
  31. Klir, G.I.; Yuan, B. Fuzzy Sets and Fuzzy Logic Theory and Applications; Prentice-Hall International: London, UK, 1995. [Google Scholar]
  32. Saaty, T.L. Decision Making with Dependence and Feedback: The Analytic Network Process; RWS Publications: Pittsburgh, PA, USA, 1996. [Google Scholar]
  33. Radziemska, E.; Klugmann, E. Thermally affected parameters of the current—Voltage characteristics of silicon photocell. Energ. Convers. Manag. 2002, 43, 1889–1900. [Google Scholar] [CrossRef]
  34. Radziemska, E. The effect of temperature on the power drop in crystalline silicon solar cells. Renew. Energ. 2003, 28, 1–12. [Google Scholar] [CrossRef]
  35. Guide to Meteorological Instruments and Methods of Observation. Avalable online: http://www.wmo.int/pages/prog/gcos/documents/gruanmanuals/CIMO/CIMO_Guide-7th_Edition-2008.pdf (accessed on 23 September 2015).
  36. Green, M.A.; Emery, K.; Hishikawa, Y.; Warta, W. Solar cell efficiency tables. Prog. Photovoltaics: Res. Appl. 2011, 19, 84–92. [Google Scholar] [CrossRef]
  37. Lee, A.H.I.; Chen, H.H.; Kang, H.-Y. A model to analyze strategic products for photovoltaic silicon thin-film solar cell power industry. Renew. Sustain. Energ. Revs. 2011, 15, 1271–1283. [Google Scholar] [CrossRef]
  38. Luque, A.; Hegedus, S. Handbook of Photovoltaic Science and Engineering; John Wiley & Sons: New York, NY, USA, 2011. [Google Scholar]
  39. Solar Panel Temperature Affects Output—Here’s What You Need to Know. Available online: http://www.solar-facts-and-advice.com/solar-panel-temperature.html (accessed on 23 September 2015).
  40. Global Market Outlook for Photovoltaics. Available online: http://www.epia.org/fileadmin/user_upload/Publications/GMO_2013_-_Final_PDF.pdf (accessed on 23 September 2015).

Share and Cite

MDPI and ACS Style

Lee, A.H.I.; Kang, H.-Y.; Lin, C.-Y.; Shen, K.-C. An Integrated Decision-Making Model for the Location of a PV Solar Plant. Sustainability 2015, 7, 13522-13541. https://doi.org/10.3390/su71013522

AMA Style

Lee AHI, Kang H-Y, Lin C-Y, Shen K-C. An Integrated Decision-Making Model for the Location of a PV Solar Plant. Sustainability. 2015; 7(10):13522-13541. https://doi.org/10.3390/su71013522

Chicago/Turabian Style

Lee, Amy H. I., He-Yau Kang, Chun-Yu Lin, and Kuan-Chin Shen. 2015. "An Integrated Decision-Making Model for the Location of a PV Solar Plant" Sustainability 7, no. 10: 13522-13541. https://doi.org/10.3390/su71013522

APA Style

Lee, A. H. I., Kang, H. -Y., Lin, C. -Y., & Shen, K. -C. (2015). An Integrated Decision-Making Model for the Location of a PV Solar Plant. Sustainability, 7(10), 13522-13541. https://doi.org/10.3390/su71013522

Article Metrics

Back to TopTop