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Article

Interval-Valued Pythagorean Fuzzy Similarity Measure-Based Complex Proportional Assessment Method for Waste-to-Energy Technology Selection

1
Department of Mathematics, Government College Raigaon, Satna 485441, India
2
Military Academy, University of Defense in Belgrade, 11000 Belgrade, Serbia
3
Department of Statistics & Operations Research, College of Sciences, King Saud University, Riyadh 11451, Saudi Arabia
4
School of Engineering and IT, UNSW Canberra at ADFA 2600, Campbell, ACT 2610, Australia
5
Department of Mathematics, Rajiv Gandhi National Institute of Youth Development, Sriperumbudur 602105, India
6
Faculty of Technical Sciences, University of Novi Sad, Trg Dositeja Obradovica-6, 21000 Novi Sad, Serbia
*
Author to whom correspondence should be addressed.
Submission received: 19 April 2022 / Revised: 6 May 2022 / Accepted: 17 May 2022 / Published: 19 May 2022
(This article belongs to the Section Process Control and Monitoring)

Abstract

:
This study introduces an integrated decision-making methodology to choose the best “waste-to-energy (WTE)” technology for “municipal solid waste (MSW)” treatment under the “interval-valued Pythagorean fuzzy sets (IPFSs)”. In this line, first, a new similarity measure is developed for IPFSs. To show the utility of the developed similarity measure, a comparison is presented with some extant similarity measures. Next, a weighting procedure based on the presented similarity measures is proposed to obtain the criteria weight. Second, an integrated approach called the “interval-valued Pythagorean fuzzy-complex proportional assessment (IPF-COPRAS)” is introduced using the similarity measure, linear programming model and the “complex proportional assessment (COPRAS)” method. Furthermore, a case study of WTE technologies selection for MSW treatment is taken to illustrate the applicability and usefulness of the presented IPF-COPRAS method. The comparative study is made to show the strength and stability of the presented methodology. Based on the results, the most important criteria are “greenhouse gas (GHG)” emissions (P3), microbial inactivation efficacy (P7), air emissions avoidance (P9) and public acceptance (P10) with the weight/significance degrees of 0.200, 0.100, 0.100 and 0.100, respectively. The evaluation results show that the most appropriate WTE technology for MSW treatment is plasma arc gasification (H4) with a maximum utility degree of 0.717 followed by anaerobic digestion (H7) with a utility degree of 0.656 over various considered criteria, which will assist with reducing the amount of waste and GHG emissions and also minimize and maintain the costs of landfills.

1. Introductions

From a global perception, urban regions have been proliferating because of accelerating population growth. Consequently, waste generation is increasing, which is taking into account water and air pollutions, and environmental deterioration. Severe ecological issues arise from several industrial and domestic solid wastes, mainly within urban societies [1,2]. India is fast growing from an agricultural-based country to an industrial and services-based nation. Approximately 31.2% of the population is currently living in urban regions. More than 377 million urban citizens live in 7935 villages/cities [3]. India has diverse climatic and geographic provinces (tropical wet and dry, subtropical humid) and four seasons (winter, summer, rain and autumn). Therefore, the people living in the shared zones have various waste generation and consumption patterns. Nevertheless, no actual process has been analyzed yet to examine provincial and geographical-precise waste generation prototypes for urban areas. Thus, this study relies on the limited information available according to the research accomplished by “Central Pollution Control Board (CPCB)”, New Delhi; “Central Institute of Plastics Engineering and Technology (CIPET)”, Chennai and “Federation of Indian Chambers of Commerce and Industry (FICCI)”, New Delhi [3,4].
The “municipal solid waste (MSW)” is a specific type of waste stemming from households, and it can comprise industrial and commercial wastes. At present, around 2.01 billion metric tons of MSW are generated yearly worldwide. The worldwide annual MSW production rate is expected to grow up to 2.59 “billion metric tons (BMTs)” by 2030 to 3.40 BMTs by 2050 [5,6]. This significant growth in MSW production is recognized as a consequence of diverse aspects, containing economic development, population growth, industrial expansion, urban development and relocation from rural to urban [6,7]. Accompanied by the filling up of waste capacities, the MSW composition is appealing, because it is more heterogeneous and multifaceted due to the expansion of advance economies that are vastly based on user lifestyle [8,9].
The heterogeneity and intricacy of MSW combination are causing excessive difficulty in the sustainable disposal of this enormous quantity of waste that causes several economic damages and shapes severe impacts on the atmosphere and human health [10,11]. It is documented that diverse income level groups produce diverse types of waste compositions and amounts [5,12]. The yearly MSW production growth rate for low to high-income nations has been projected as 2–3% to 3.2–4.5%, respectively [9]. This change among the MSW production growth rates of diverse income groups revealed that the nations with superior purchasing power produce more waste as emerging nations are quickly moving toward industrialization [6]. Regarding the waste collection, high-income nations produce the majority of dry waste, comprising papers, plastics, glasses, metals and others, which is relatively easy to recycle. In contrast, approximately 50% of the MSW production in low-income nations is biological waste, which is more challenging to handle [5]. Worldwide energy requirement has also increased with the multiple increased plight of MSW production and its sustainable management.
Around the world, power generation and transport sectors are two major energy-intensive regions all over the world. The majority of energy requirements in these regions are met by costly fossil fuels [13]. In addition, these “conventional energy resources (CERs)” are quickly diminishing and intimidating energy security worldwide [14,15]. Alternatively, the employment of “renewable energy resources (RESs)” for heat, power, and diverse forms of biofuels generation has reached higher significance in nationwide and worldwide energy plans [12]. Using MSW as an energy source can decrease the severe environmental effects of inappropriate waste management performance and fossil-based electricity power generation [16]. “Waste-to-energy (WTE)” plants can transform this economical and readily accessible RES into useful energy. Consequently, WTE can potentially ensure worldwide energy security by compensating for the dominance of fossil fuels in the global energy region [17]. The word ‘WTE’ describes treating the waste for energy retrieval in heat and electric or other fuels in different states. A variety of WTE procedures are accessible to generate such a different way of end-products from the multifaceted composed feedstock, i.e., “MSW” [12,18].
Assessment of an optimal WTE technology is an intricate “multi-criteria decision-making (MCDM)” procedure that contains various factors, for instance, “waste quality and quantity (WQQ)”, environmental, technological and economic aspects [1,12,19]. The assessment of the most desirable WTE technology recognized saves time and money and helps reduce the negative consequences on the environment [1,19]. Since selecting WTE technology option(s) for the conversion of waste into energy is a complicated decision-making problem, strategic decisions are vital for the efficient assessment and management of these sustainable energy schemes [12,20]. This paper develops an integrated MCDM method that accounts for uncertainty in decision making. In this regard, uncertainties in all steps, which are basically lacking in the preceding literature, were treated in this study. Uncertainty generally occurs in data collection, the data itself, and the evaluation procedure [21]. In this paper, uncertainty in data collection is reduced by conducting the questionnaires between the researchers, experts, and specialists. The interval-values Pythagorean fuzzy sets (IPFSs) are also applied to decrease data uncertainty. Furthermore, an integrated decision-making framework is utilized to address uncertainties related to the evaluation procedure. The combination of different assessment frameworks can help researchers find more accurate outcomes.
To deal with imprecise or uncertain information/data, Zadeh [22] pioneered the concept of “fuzzy sets (FSs)”. Afterwards, Atanassov [23] put forward the idea of “intuitionistic fuzzy sets (IFSs)”, which is related to each object of discourse set not only acquiring a “belongingness degree (BD)” but also “non-belongingness degree (NBD)” such that their sum is less than or equal to one. Consequently, IFSs are proved as a more valuable tool than FSs. The “interval-valued intuitionistic fuzzy sets (IIFSs)” theory was developed by Atanassov and Gargov [24] for treating the ambiguity in data and fuzziness in “decision expert’s (DE’s)” opinions in practical MCDM problems. In the theory of IIFS, both the BD and the NBD of an object are considered and taken in the form of interval values instead of exact numbers. Consequently, there is a substantial requirement to explore more productive and appropriate mathematical approaches utilizing the IIFSs successively to better handle MCDM problems with the high degrees of uncertainty and ambiguity.
Nonetheless, in various actual circumstances, the addition of BD and NBD to an element fulfilled and presented by a DE may be greater than one, whereas their squares addition is 1 . As a result, IFSs fail to tackle such a situation. In order to conquer such situations, Yager [25] commenced the theory of “Pythagorean fuzzy sets (PFSs)” in which the squares sum of BD and NBD is 1 . Therefore, the notion of PFS is considered as a more reliable tool to handle the practical MCDM problems with uncertain information [25]. PFS theory has been explored from several perspectives, including aggregation operators [26,27], decision-making technologies [28,29,30], and information measures [31,32].
Afterwards, the theory of “interval-valued Pythagorean fuzzy sets (IPFSs)” has been introduced by Peng and Yang [33]. As a generalization of PFSs and IIFSs, the IPFSs have wide applications in the discipline of MCDM, such as in emerging sustainable community-based tourism [34] and hospital-based post-acute care assessment [35]. Liang et al. [36] presented the maximizing deviation approach using an IPF-aggregation operator in order to deal with practical MCDM problems. The Bonferroni mean operator [37] and Einstein operator [38] for IPFSs were developed to aggregate the IPFSs for handling the group decision-making problems. In a study, numerous score and accuracy degrees of IPFSs were proposed by Garg [39] for addressing some comparative concerns to solve the MCDM problems. Chen [40] proposed a novel IPF “elimination et choix taduisant la realité (ELECTRE)” method by applying a risk assignment model for solving a financial decision-making problem under an IPFS environment. Peng and Li [41] developed novel IPF operators and established models to solve emergency problems. He et al. [34] designed an IPF information-based model for sustainable community-based tourism. Al-Barakati et al. [42] discussed the work in two folds. Firstly, they reviewed various RESs potential and then proposed an integrated method with the “weighted aggregated sum product assessment (WASPAS)” model and similarity measure for prioritizing the RESs on IPFSs.
Meanwhile, the “complex proportional assessment (COPRAS)” framework, presented by Zavadskas et al. [43], is the MCDM approach, which establishes an outcome and the ratio to the “ideal solution (IS)” and the “anti-ideal solution (AIS)”, and thus, it can be obtained as a compromising model. Recently, the COPRAS approach has been applied under IFSs [44], “picture fuzzy sets (PiFSs)” [45], interval-valued intuitionistic fuzzy sets (IIFSs) [46], “hesitant fuzzy sets (HFSs)” [47], “probabilistic hesitant fuzzy sets (PHFSs)” [48], “Pythagorean fuzzy sets (PFSs)” [49] and “single-valued neutrosophic sets (SVNSs)” [50] to tackle real-life decision-making applications. Furthermore, Roozbahani et al. [51] presented an integrated model by combining “fuzzy sets (FSs)” and a gray COPRAS model for treating the realistic MCDM problem. Mishra et al. [52] developed the idea of “interval-valued hesitant Fermatean fuzzy sets (IVHFFSs)”. Then, they extended the conventional COPRAS methodology to choose the “desalination technology (DT)” for treating the feed water on IVHFFSs. Rani et al. [53] proposed an approach by combining the “criteria interaction through inter-criteria correlation (CRITIC)” and the COPRAS methods to assess and rank the “sustainable community-based tourism (SCBT)” location problem.

Motivation and Novelty

With the rapid growth of the economy, increasing complexity, and society’s continuous progress, MCDM problems have become progressively complex with their noticeable uncertainty and fuzziness of human behavior. Consequently, in the MCDM process, unlike the proper representation of “crisp (precise) numbers (CNs)”, the representation of input parameters in terms of interval values is more appropriate in the recent decision-making settings. Inspired by this notion, the present work is focused on the IPFS environment. The concept of IPFSs is an extension of PFSs [33,34,35]. IPFSs are three-dimensional, and their BD, NBD and “hesitation degree (HD)” are given by an interval within [0, 1]. In the meantime, the only condition is that the squares sum of respective upper bounds of BD and NBD is 1 . On the other hand, to obtain the similarity degree between elements, the measure of similarity is extensively applied information measures in various disciplines and a vital tool in data analysis, decision analysis, medical treatment, and others. As the “similarity measure (SM)” has extensively been implemented in real-life problems, therefore, the SM-based weighting procedure is developed to obtain the weights of criteria. It is observed from the extant research that there is no study to extend the classical COPRAS to the IPF-COPRAS approach to evaluate and prioritize WTE technology for MSW management over various criteria. Thus, in this study, we have developed the IPF-similarity measure-based COPRAS method and implemented it to waste-to-energy technology selection for MSW treatment under IPFSs. Finally, to evaluate the criteria weights, a “linear programming model (LP-model)” is constructed based on similarity measures for IPFSs. The primary contributions stemming from this work are as follows:
-
This study proposes a new IPF similarity measure to evade the shortcomings of existing measures. Furthermore, we utilize it to compute the criteria weights for the waste-to-energy technology selection problem.
-
Corresponding to Liu and Wang [54] for IFSs, we develop a procedure under IPFSs to evaluate the DEs’ weights. In addition, a similarity measure-based LP-model is developed to assess the criteria weights.
-
To illustrate the WTE technology selection for MSW treatment with qualitative and quantitative criteria, an extended COPRAS method is introduced under IPFSs. Subsequently, a problem of waste-to-energy technology assessment is taken to exemplify the usefulness and stability of the proposed ones.
The organization of the paper is discussed as Section 2 elucidates some basic ideas about the IPFSs. Section 3 discusses a novel similarity measure for IPFSs with their properties. Section 4 proposes an IPF-COPRAS methodology based on similarity measures within the IPFSs setting. Section 5 reveals an application of WTE technology selection for the MSW treatment problem and compares the developed approach with existing ones. Finally, concluding remarks are in Section 6.

2. Basic Concepts

In this section, the elementary conceptions of PFSs, IPFSs and IPF similarity measures are discussed.
Definition 1
([25]). A PFS A ¯ on a fixed set Θ = { z 1 , z 2 , , z n } is described as
A ¯ = { z i , A ¯ ( μ A ¯ ( z i ) , ν A ¯ ( z i ) ) | z i Θ } ,
where μ A ¯ : Θ [ 0 , 1 ] and ν A ¯ : Θ [ 0 , 1 ] exemplify the BD and NBD of an element z i Θ to A ¯ , respectively, satisfying 0 ( μ A ¯ ( z i ) ) 2 + ( ν A ¯ ( z i ) ) 2 1 . For each z i Θ , the hesitancy degree is defined by π A ¯ ( z i ) = 1 μ A ¯ 2 ( z i ) ν A ¯ 2 ( z i ) . The notion of “Pythagorean fuzzy number (PFN)” is denoted by α ¯ = ( μ α ¯ , ν α ¯ ) which satisfies μ α ¯ , ν α ¯ [ 0 , 1 ] and 0 μ α ¯ 2 + ν α ¯ 2 1 [55].
Definition 2
([56]). Consider Θ = { z 1 , z 2 , , z n } is a fixed set and I n t [ 0 , 1 ] signifies the collection of all closed subintervals of [ 0 , 1 ] . Mathematically, an IPFS K in Θ is defined by
K = { z i , [ μ K ( z i ) , μ K + ( z i ) ] , [ ν K ( z i ) , ν K + ( z i ) ] : z i Θ } ,  
where 0 μ K ( z i ) μ K + ( z i ) 1 ,   0 ν K ( z i ) ν K + ( z i ) 1 and 0 ( μ K + ( z i ) ) 2 + ( ν K + ( z i ) ) 2 1 . Here, μ K ( z i ) = [ μ K ( z i ) , μ K + ( z i ) ] and ν K ( z i ) = [ ν K ( z i ) , ν K + ( z i ) ] define the BD and NBD of an element z i to Θ , respectively. There are two special cases of IPFS (see Figure 1). (i) An IPFS is changed to an IIFS if 0 μ K + ( z i ) + ν K + ( z i ) 1 . (ii) An IPFS is transformed to a PFS if μ K ( z i ) = μ K + ( z i ) and ν K ( z i ) = ν K + ( z i ) .
The function π K ( z i ) = [ π K ( z i ) , π K + ( z i ) ] represents the hesitancy degree of z i to K, wherein π K ( z i ) = 1 ( μ K + ( z i ) ) 2 ( ν K + ( z i ) ) 2 and π K + ( z i ) = 1 ( μ K ( z i ) ) 2 ( ν K ( z i ) ) 2 . For simplicity, the “interval-valued Pythagorean fuzzy number (IPFN)” is denoted by α = ( [ μ α , μ α + ] , [ ν α , ν α + ] ) , which fulfills 0 ( b α + ) 2 + ( n α + ) 2 1 .
Definition 3
([56]). Let α 1 = ( [ μ α 1 , μ α 1 + ] , [ ν α 1 , ν α 1 + ] ) , α 2 = ( [ μ α 2 , μ α 2 + ] , [ ν α 2 , ν α 2 + ] ) and α 3 = ( [ μ α 3 , μ α 3 + ] , [ ν α 3 , ν α 3 + ] ) be the IPFNs. Then, some fundamental operations are defined as
α 1 α 2 = ( [ ( μ α 1 ) 2 + ( μ α 2 ) 2 ( μ α 1 ) 2 ( μ α 2 ) 2 , ( μ α 1 + ) 2 + ( μ α 2 + ) 2 ( μ α 1 + ) 2 ( μ α 2 + ) 2 ] , [ ν α 1 ν α 2 , ν α 1 + ν α 2 + ] ) , α 1 α 2 = ( [ μ α 1 μ α 2 , μ α 1 + μ α 2 + ] , [ ( ν α 1 ) 2 + ( ν α 2 ) 2 ( ν α 1 ) 2 ( ν α 2 ) 2 , ( ν α 1 + ) 2 + ( ν α 2 + ) 2 ( ν α 1 + ) 2 ( ν α 2 + ) 2 ] ) , λ α 1 = ( [ 1 ( 1 ( μ α 1 ) 2 ) λ , 1 ( 1 ( μ α 1 + ) 2 ) λ ] , [ ( ν α 1 ) λ , ( ν α 1 + ) λ ] ) , ( α 1 ) λ = ( [ ( μ α 1 ) λ , ( μ α 1 ) λ ] , [ 1 ( 1 ( ν α 1 ) 2 ) λ , 1 ( 1 ( ν α 1 + ) 2 ) λ ] ) , ( α 1 ) c = ( [ ν α 1 , ν α 1 + ] , [ μ α 1 , μ α 1 + ] ) .
Definition 4
([33]). Assume α = ( [ μ α , μ α + ] , [ ν α , ν α + ] ) is an IPFN. Then
S ( α ) = 1 2 ( ( μ α ) 2 + ( μ α + ) 2 ( ν α ) 2 ( ν α + ) 2 )  
and
( α ) = 1 2 ( ( μ α ) 2 + ( μ α + ) 2 + ( ν α ) 2 + ( ν α + ) 2 ) ,
are given as the score and accuracy values of an IPFN α , respectively, where S ( α ) [ 1 , 1 ] and ( α ) [ 0 , 1 ] .
For any two IPFNs, the ranking principle using the score and accuracy functions and are defined by
(a)
If S ( α 1 ) < S ( α 2 ) then α 1 < α 2 ,
(b)
If S ( α 1 ) > S ( α 2 ) then α 1 < α 2 ,
(c)
If S ( α 1 ) = S ( α 2 ) then
  • If ( α 1 ) < ( α 2 ) then α 1 < α 2 ,
  • If ( α 1 ) > ( α 2 ) then α 1 < α 2 ,
  • If ( α 1 ) = ( α 2 ) then α 1 < α 2 .
Definition 5
([57]). Consider α = ( [ μ α , μ α + ] , [ ν α , ν α + ] ) being an IPFN. Then
S * ( α ) = ( ( μ α ) 2 ( ν α ) 2 ) ( 1 + 1 ( μ α ) 2 ( ν α ) 2 ) + ( ( μ α + ) 2 ( ν α + ) 2 ) ( 1 + 1 ( μ α + ) 2 ( ν α + ) 2 ) 2 ,
is said to be an improved score function of IPFN α and S * ( α ) [ 1 , 1 ] .
Definition 6
([56]). Let α 1 = ( [ μ α 1 , μ α 1 + ] , [ ν α 1 , ν α 1 + ] ) and α 2 = ( [ μ α 2 , μ α 2 + ] , [ ν α 2 , ν α 2 + ] ) be two IPFNs. Then, the following relations are satisfied:
α 1 = α 2 if and only if μ α 1 = μ α 2 ,   μ α 1 + = μ α 2 + ,   ν α 1 = ν α 2 and ν α 1 + = ν α 2 + .
α 1 α 2 if and only if μ α 1 μ α 2 ,   μ α 1 + μ α 2 + ,   ν α 1 ν α 2 and ν α 1 + ν α 2 + .
Definition 7
([56]). An IPF similarity measure S : I P F S s ( Θ ) × I P F S s ( Θ ) is a real-valued mapping that fulfills the given axioms as
(S1) 0 S ( K , L ) 1 ; K , L I P F S s ( Θ ) ,
(S2) S ( K , L ) = 1 if and only if K = L ; K , L I P F S s ( Θ ) ,
(S3) S ( K , L ) = S ( L , K ) ; K , L I P F S s ( Θ ) ,
(S4) S ( K , K c ) = 0 if and only if A is a crisp set,
(S5) If K L M , then S ( K , M ) S ( K , L ) and S ( K , M ) S ( L , M ) ; K , L , M I P F S s ( Θ ) .

3. Proposed Similarity Measure for IPFSs

The “Similarity Measure (SM)” is a very significant aspect for assessing the uncertain information. In FS theory, the concept of similarity measure describes the closeness degree between two FSs. Firstly, Zhang [56] initiated the concept of “Pythagorean Fuzzy SM (PF-SM)” and employed it to cope with the practical applications. Peng et al. [58] extended novel entropy, distance and similarity measures to solve the problems that arise in image segmentation and disease diagnosis. Later on, many research efforts have been made in the context of PF-SMs [31,59,60,61,62]. Further, Biswas and Sarkar [63] proposed a point operator based IPF-SMs using a weighted Minkowski distance of IPFNs and “IPF point operators (IPFPOs)” [33]. Peng and Li [41] developed novel similarity, distance and entropy measures for IPFSs and utilized them to discuss the “Weighted Discrimination-Based Approximation (WDBA)” model. Rani and Mishra [64] proposed a “combined compromise solution (CoCoSo)” model with the similarity measure on the “single-valued neutrosophic sets (SVNSs)”, and then, they applied it to treat the “waste electrical and electronics equipment (WEEE)” recycling partner selection problem. Mishra et al. [65] introduced the similarity measure-based “additive ratio assessment (ARAS)” model on SVNSs for assessing and prioritizing the sustainable “electric vehicle charging station (EVCS)” sites. Ünver et al. [66] developed various similarity measures using the Choquet integral for “spherical fuzzy sets (SFSs)”. They also performed these measures in pattern recognition problems to observe a comparative assessment of the proposed ones with some existing similarity measures.
In the current section, we propose new SM for IPFSs and further apply it in the development of the COPRAS method within the IPFSs setting.
Let K , L I P F S s ( Θ ) . Then, a new “interval-valued Pythagorean fuzzy similarity measure (IPF-SM)” is defined as
S 1 ( K , L ) = 1 1 exp [ 1 4 n i = 1 n ( | μ K 2 ( z i ) μ L 2 ( z i ) | + | μ K + 2 ( z i ) μ L + 2 ( z i ) | + | ν K 2 ( z i ) ν L 2 ( z i ) | + | ν K + 2 ( z i ) ν L + 2 ( z i ) | + | π K 2 ( z i ) π L 2 ( z i ) | + | π K + 2 ( z i ) π L + 2 ( z i ) | ) ] 1 exp ( 1 ) .
Lemma 1.
If g ( γ ) = 1 1 exp ( γ ) 1 exp ( 1 ) , then max γ [ 0 , n ] g ( γ ) = g ( 0 ) = 1 and min γ [ 0 , n ] g ( γ ) = g ( n ) = 0 .
Proof. 
Since g ( γ ) = exp ( γ ) 1 exp ( 1 ) < 0 , γ [ 0 , n ] , therefore, g ( γ ) is decreasing in [ 0 , n ] .
Theorem 1.
The measure S 1 ( K , L ) , defined in Equation (3), is a valid IPF-similarity measure.
Proof. 
To prove this, we have to validate the axioms (S1)–(S5) of Definition 7.
(S1). For K , L I P F S s ( Θ ) ,
γ = 1 4 n i = 1 n ( | μ K 2 ( z i ) μ L 2 ( z i ) | + | μ K + 2 ( z i ) μ L + 2 ( z i ) | + | ν K 2 ( z i ) ν L 2 ( z i ) | + | ν K + 2 ( z i ) ν L + 2 ( z i ) | + | π K 2 ( z i ) π L 2 ( z i ) | + | π K + 2 ( z i ) π L + 2 ( z i ) | ) .
Since β [ 0 , n ] , thus, S 1 ( K , L ) = g ( γ ) . From Lemma 1, we obtain 0 S i m 1 ( K , L ) 1 .
(S2). From Equation (3), if K = L , then S 1 ( K , L ) = 1 . Conversely, let S 1 ( K , L ) = 1 .
Conversely, let S 1 ( K , L ) = 1 . Then, from Equation (3), we obtain
1 1 exp [ 1 4 n i = 1 n ( | μ K 2 ( z i ) μ L 2 ( z i ) | + | μ K + 2 ( z i ) μ L + 2 ( z i ) | + | ν K 2 ( z i ) ν L 2 ( z i ) | + | ν K + 2 ( z i ) ν L + 2 ( z i ) | + | π K 2 ( z i ) π L 2 ( z i ) | + | π K + 2 ( z i ) π L + 2 ( z i ) | ) ] 1 exp ( 1 ) = 1 , z i Θ .
It implies that
( | μ K 2 ( z i ) μ L 2 ( z i ) | + | μ K + 2 ( z i ) μ L + 2 ( z i ) | + | ν K 2 ( z i ) ν L 2 ( z i ) | + | ν K + 2 ( z i ) ν L + 2 ( z i ) | + | π K 2 ( z i ) π L 2 ( z i ) | + | π K + 2 ( z i ) π L + 2 ( z i ) | ) = 0 .
Thus, μ K ( z i ) = μ L ( z i ) , μ K + ( z i ) = μ L + ( z i ) , ν K ( z i ) = ν L ( z i ) , ν K + ( z i ) = ν L + ( z i ) .
Hence, K = L .
(S3)–(S4). Both axioms are straightforward from Equation (3).
(S5). Let K L M , then μ K 2 ( z i ) μ L 2 ( z i ) μ M 2 ( z i ) ,   μ K + 2 ( z i ) μ L + 2 ( z i ) μ M + 2 ( z i ) ,   ν K 2 ( z i ) ν L 2 ( z i ) ν M 2 ( z i ) , and ν K + 2 ( z i ) ν L + 2 ( z i ) ν M + 2 ( z i ) , z i Θ .
Then,
γ 1 = 1 4 n i = 1 n ( | μ K 2 ( z i ) μ L 2 ( z i ) | + | μ K + 2 ( z i ) μ L + 2 ( z i ) | + | ν K 2 ( z i ) ν L 2 ( z i ) | + | ν K + 2 ( z i ) ν L + 2 ( z i ) | + | π K 2 ( z i ) π L 2 ( z i ) | + | π K + 2 ( z i ) π L + 2 ( z i ) | )
γ 2 = 1 4 n i = 1 n ( | μ K 2 ( z i ) μ M 2 ( z i ) | + | μ K + 2 ( z i ) μ M + 2 ( z i ) | + | ν K 2 ( z i ) ν M 2 ( z i ) | + | ν K + 2 ( z i ) ν M + 2 ( z i ) | + | π K 2 ( z i ) π M 2 ( z i ) | + | π K + 2 ( z i ) π M + 2 ( z i ) | ) , z i Θ .
Therefore, by Lemma 1, we obtain S 1 ( K , L ) = g ( γ 1 ) g ( γ 2 ) = S 1 ( K , M ) . Similarly, we can verify that S 1 ( L , M ) S 1 ( K , M ) . [Proved] □
Moreover, a new IPF-SM is discussed using the association of S 1 ( K , L ) and a lattice. In general, a lattice of a non-empty set is a hierarchical system generated by the “partial order sets (POSETs)”. In a lattice, each pair of elements must contain a supremum and an infimum. Now, let K , L I P F S s ( Θ ) . Then, the proposed IPF similarity measure is presented as
S 2 ( K , L ) = S 1 ( K , P K L ) × S 1 ( L , P K L ) ,   where   P K L = K L .
Theorem 2.
The measure S 2 ( K , L ) , defined in Equation (4), is a valid IPF similarity measure.
Proof. (S1).
It is straightforward, so that we have omitted the proof.
(S2). Consider K , L I P F S s ( Θ ) and K = L . Given that P K L = K L , this implies that K = L = P K L and so, S 1 ( K , L ) fulfills the axiom (S2). Thus, S 2 ( K , L ) = 1 . Conversely, let S 2 ( K , L ) = 1 , that means that S 1 ( K , P K L ) = S 1 ( L , P K L ) = 1 , where P K L = K L and S 1 ( K , L ) satisfies (S2). Thus, K = L = P K L . Hence, measure S 2 ( K , L ) satisfies (S2).
(S3)–(S4): Both are straightforward from Equation (4).
(S5): Suppose K , L , M I P F S s ( Θ ) and K L M . Then. K L = L ,   K M = M and L M = M .
Now,
S 2 ( K , M ) = S 1 ( K , P K M ) × S 1 ( M , P K M ) .
It implies that
S 2 ( K , M ) = S 1 ( K , M ) × S 1 ( M , M ) .
Thus,
S 2 ( K , M ) = S 1 ( K , M ) .
Similarly, we can verify that
S 2 ( K , L ) = S 1 ( K , L ) .
Since S 1 ( K , M ) holds (S5), i.e., S 1 ( K , L ) S 1 ( K , M ) . Consequently, from Equation (5) and Equation (6), we obtain S 2 ( K , L ) S 2 ( K , M ) . In a similar line, we can show that S 2 ( L , M ) S 2 ( K , M ) . [Proved] □

Comparison with Existing SMs

Here, a comparative study between the introduced IPF-SM S 2 ( K , L ) and the existing measures [56,67] has been discussed to explore the benefits of the introduced IPF-SM in the form of distance measure. The extant SMs based on the combination of the Hausdorff, Euclidean, and Hamming distances on IPFNs have been illustrated as follows:
S H ( K , L ) = 1 D H ( K , L ) = 1 1 4 ( | μ K ( z i ) μ L ( z i ) | + | μ K + ( z i ) μ L + ( z i ) | + | ν K ( z i ) ν L ( z i ) | + | ν K + ( z i ) ν L + ( z i ) | ) .
S E ( K , L ) = 1 D E ( K , L ) = 1 1 4 ( ( μ K ( z i ) μ L ( z i ) ) 2 + ( μ K + ( z i ) μ L + ( z i ) ) 2 + ( ν K ( z i ) ν L ( z i ) ) 2 + ( ν K + ( z i ) ν L + ( z i ) ) 2 ) .
S H H ( K , L ) = 1 D H H ( K , L ) = 1 max ( | μ K ( z i ) μ L ( z i ) | , | μ K + ( z i ) μ L + ( z i ) | , | ν K ( z i ) ν L ( z i ) | , | ν K + ( z i ) ν L + ( z i ) | ) .
S H E ( K , L ) = 1 D H E ( K , L ) = 1 max ( ( μ K ( z i ) μ L ( z i ) ) 2 , ( μ K + ( z i ) μ L + ( z i ) ) 2 , ( ν K ( z i ) ν L ( z i ) ) 2 , ( ν K + ( z i ) ν L + ( z i ) ) 2 ) .
S Z ( K , L ) = 1 D Z ( K , L ) = 1 1 4 ( | ( μ K ( z i ) ) 2 ( μ L ( z i ) ) 2 | + | ( μ K + ( z i ) ) 2 ( μ L + ( z i ) ) 2 | + | ( ν K ( z i ) ) 2 ( ν L ( z i ) ) 2 | + | ( ν K + ( z i ) ) 2 ( ν L + ( z i ) ) 2 | + | ( π K ( z i ) ) 2 ( π L ( z i ) ) 2 | + | ( π K + ( z i ) ) 2 ( π L + ( z i ) ) 2 | ) .
Here, Table 1 demonstrates a comparison of similarity measures for IPFSs with different counter-intuitive examples.
Existing SMs ( S H , S E , S H H and S H E ) fall short of discriminating positive change from negative change. For example, S H ( K , L ) = 0.9 and S H ( K 1 , L 1 ) = 0.9 ;   S E ( K , L ) = 0.9 and S E ( K 1 , L 1 ) = 0.9 ;   S H H ( K , L ) = 0.9 ;   S H H ( K 1 , L 1 ) = 0.9 ;   S H E ( K , L ) = 0.9 ; and S H H ( K 1 , L 1 ) = 0.9 ; when K = ([0.26, 0.36], [0.26, 0.36]); L = ([0.36, 0.46], [0.36, 0.46]); K1 = ([0.26, 0.36], [0.36; 0.46]) and L1 = ([0.36, 0.46], [0.26, 0.36]). Alternatively, the proposed SM S2 can efficiently discriminate positive from negative changes on account of S 2 ( K , L ) = 0.9119 and S 2 ( K 1 , L 1 ) = 0.9425 in the same example. Additionally, another counter-intuitive case will occur in which S H ( K , L ) = 0.5 and S H ( K 1 , L 1 ) = 0.5 are equal if K = ([1.0, 1.0], [0.0, 0.0]); L = ([0.0, 0.0], [0.0, 0.0]). For IPFNs, K1 = ([0.5, 0.5], [0.5, 0.5]); L1 = ([0.0, 0.0], [0.0, 0.0]), the SMs S Z ( K , L ) = 0.6036 ,   S 2 ( K , L ) = 0.7155 and remaining extant SMs have counter-intuitive cases because other extant SMs do not contain the third parameter of IPFNs that means hesitancy or indeterminacy degree. Furthermore, the existing ones except the above have presented different outcomes, which are more rational.
Next, it is evident that the postulate of IPF-SM (S4) is not fulfilled by S H H , S H E and S Z . It means that only the third row for all SMs is equal to 0.
Finally, the last counter-intuitive state occurs when K = ([0.36, 0.46], [0.16, 0.26]); L = ([0.46, 0.56], [0.26, 0.36]); K1 = ([0.46, 0.56], [0.16, 0.26]), since IPFNs K, L and K1 are ranked as K 1 L K by Definition 5. Moreover, S H H ( K , L ) = S H H ( L , K 1 ) = 0.9 and S H E ( K , L ) = S H E ( L , K 1 ) = 0.9 are not reasonable. Hence, to investigate all the counter-intuitive cases, the SMs S Z ( K , L ) and S 2 is only one that validates the mentioned counter-intuitive cases, as depicted in Table 1.

4. IPF-COPRAS Methodology for MCDM Problems

In this section, the traditional COPRAS method is generalized to handle the MCDM problems on IPFSs, in which the criterion weight information is entirely unknown. The notions and operational laws of the IPFNs, IPF-SM and score function are employed to develop the IPF-COPRAS approach. The procedure of the IPF-COPRAS methodology is shown in Figure 2.
Step 1: Build the “IPF decision matrix (IPF-DM)”.
For an MCDM problem, assume that there is a set of s alternatives H = { H 1 , H 2 , , H s } assessed by t criteria P = { P 1 , P 2 , , P t } . The evaluation information of each alternative is given by IPFNs δ i j = [ μ i j , μ i j + ] , [ ν i j , ν i j + ] ; i = 1 ( 1 ) s ; j = 1 ( 1 ) t . Thus, the IPF-DM can be formulated as
P 1 P 2 P t Z = ( Z i j ) s × t = H 1 H 2 H s [ δ 11 δ 12 δ 1 t δ 21 δ 22 δ 2 t δ s 1 δ s 1 δ s t ] .
Step 2: Compute the DEs’ weights.
To reveal their relative significance in the MCDM process, we extend a procedure to calculate the numeric DEs’ weight as follows:
ϖ k = ( ( μ k ) 2 + ( μ k + ) 2 ) ( 2 + 1 ( μ k ) 2 ( ν k ) 2 + 1 ( μ k + ) 2 ( ν k + ) 2 ) k = 1 ( ( ( μ k ) 2 + ( μ k + ) 2 ) ( 2 + 1 ( μ k ) 2 ( ν k ) 2 + 1 ( μ k + ) 2 ( ν k + ) 2 ) ) .
Here, ϖ k 0 and k = 1 ϖ k = 1 .
Step 3: Compute the “aggregated IPF-DM (A-IPF-DM)”.
To create the A-IPF-DM, all single IPF-DMs need to be combined into single matrix in accordance with the DEs’ opinions. In this regard, “IPF-weighted averaging operator (IPFWAO)” is applied and obtained Z = ( δ i j ) m × n , such that
δ i j = ( [ 1 k = 1 ( 1 ( μ i j ) k 2 ) ϖ k , 1 k = 1 ( 1 ( μ i j + ) k 2 ) ϖ k ] , [ k = 1 ( ( ν i j ) k ) ϖ k , k = 1 ( ( ν i j + ) k ) ϖ k ] ) .
Step 4: Obtain the criteria weights.
The procedural steps for the computation of criteria weights are given by
Step 4a: The “IPF-ideal solution (IPF-IS)” and the “IPF-anti-ideal solution (IPF-A-IS)” are calculated by
Ψ + = { ( [ max i = 1 s μ i j , max i = 1 s μ i j + ] , [ min i = 1 s ν i j , min i = 1 s ν i j + ] ) if P j P b , ( [ min i = 1 s μ i j , min i = 1 s μ i j + ] , [ max i = 1 s ν i j , max i = 1 s ν i j + ] ) if P j P n .
and
Ψ = { ( [ min i = 1 s μ i j , min i = 1 s μ i j + ] , [ max i = 1 s ν i j , max i = 1 s ν i j + ] ) if P j P b , ( [ max i = 1 s μ i j , max i = 1 s μ i j + ] , [ min i = 1 s ν i j , min i = 1 s ν i j + ] ) if P j P n .
Again, from Equation (15) and Equation (16), we obtain
Ψ + = ( [ u j + , v j + ] , [ c j + , d j + ] )   and   Ψ = ( [ u j , v j ] , [ c j , d j ] ) , j = 1 ( 1 ) t .
The HDs can be defined according to the Ψ + and Ψ as
[ e j + , f j + ] = [ 1 ( v j + ) 2 ( d j + ) 2 , 1 ( u j + ) 2 ( c j + ) 2 ] ,
[ e j , f j ] = [ 1 ( v j ) 2 ( d j ) 2 , 1 ( u j ) 2 ( c j ) 2 ] .
Step 4b: From Equation (1), we evaluate the similarity degree S i + between the elements at the ith row of the decision matrix S ˜ ¯ = ( ζ i j ) s × t = ( [ μ i j , μ i j + ] , [ ν i j , ν i j + ] ) s × t and the elements in the IPF-IS Ψ + , which as
S i + = S 1 ( δ i j , P δ i j ψ + ) × S 1 ( ψ + , P δ i j ψ + ) ,
where P δ i j ψ + = δ i j ψ + and S i + [ 0 , 1 ] ; i = 1 , 2 , , s .
Similarly, we evaluate the similarity degree S i between the elements at the ith row of the decision matrix S ˜ ¯ = ( ζ i j ) s × t = ( [ b i j , b i j + ] , [ n i j , n i j + ] ) s × t and the elements in the IPF-AIS Ψ , which as
S i = S 1 ( δ i j , P δ i j ψ ) × S 1 ( ψ , P δ i j ψ ) ,
where P δ i j ψ = δ i j ψ and S i + [ 0 , 1 ] ; i = 1 , 2 , , s .
Step 4c: Construct the “linear programming model (LP-model)”, as shown below:
max T = i = 1 s ( S i + S i ) ,
subject to μ j w j * 1 ν j + , w j * [ 0 , 1 ] , j = 1 ( 1 ) t .
The feasible region of the LP-model is closed and bounded, and hence, an optimal solution exists. Simplifying the LP-model given in Equation (21), we evaluate the optimal weights w 1 * , w 2 * , , w t * of criteria P 1 , P 2 , , P t , respectively, such that the objective function T is maximal.
Step 5: Estimate the ratings for benefit-type and cost-type criteria.
In the IPF-COPRAS approach, each alternative is estimated with its sums maximizing the criteria, i , as measured to benefit-type and minimizing the criteria, i , as deemed to cost-type, and these are calculated as follows:
i = j = 1 r w j ζ i j , i = 1 ( 1 ) s .
i = j = r + 1 t w j ζ i j , i = 1 ( 1 ) s .
Here, r and t are the number of benefit-type and whole criteria, respectively. w j is the criteria weight estimated by Equation (21).
Step 6: Determine the “relative degree (RD)”.
The RD of the ith option is determined by
i = S * ( i ) + min i S * ( i ) i = 1 s S * ( i ) S * ( i ) i = 1 s min i S * ( i ) S * ( i ) , i = 1 ( 1 ) s .
In Equation (24), S * ( i ) and S * ( i ) symbolize the score values of i and i , respectively.
Another form of Equation (24) is
i = S * ( i ) + i = 1 s S * ( i ) S * ( i ) i = 1 s 1 S * ( i ) , i = 1 ( 1 ) s .
Step 7: Find the preference ranking of each option.
The alternative with highest RD has been considered as a higher priority rating, and it is considered as the best one as follows:
H * = { H i | max i i } , i = 1 ( 1 ) s .
Step 8: Determine the “utility degree (UD)” of each alternative.
The UD  ϑ i of each option is computed as follows:
ϑ i = i max × 100 % , i = 1 ( 1 ) s ,
where i and max are the RD presented by Equation (25).
The proposed IPF-COPRAS technique allows us to obtain the straight and comparative assurance of the RD and UD of alternatives over the criteria.

5. Waste-to-Energy Technologies Selection Problem

Here, the developed IPF-COPRAS methodology is implemented to solve an illustrative case of selecting the best process for MSW treatment in India, which expresses the practicality and applicability of the present methodology. In this respect, a group of four DEs D = { D 1 , D 2 , D 3 , D 4 } is formed to find a suitable MSW treatment alternative in India. The team of decision experts begins their work with expectations and a description of the assessment criteria. Thus, several sources have been studied to recognize aspects and criteria for MSW treatment alternatives [1,3,12,20,68,69]. Eight representative alternative scenarios of WTE technology for MSW treatment were investigated, and they are “Incineration (H1)”, “Gasification (H2)”, “Pyrolysis (H3)”, “Plasma arc gasification (H4)”, “Thermal de-polymerization (H5)”, “Hydrothermal carbonization (H6)”, “Anaerobic digestion (H7)”, and “Fermentation (H8)”. These eight alternatives are assessed based on twelve different criteria, which are given in Table 2 and Figure 3. In the present study, the DEs give the assessment values of the treatment options in terms of IPFNs concerning the referred 12 criteria. In this line, we discuss the procedure for the implementation of the proposed IPF-COPRAS model:
Table 3 presents the performance ratings of MSW treatment alternatives adopted from Al-Barakati et al. [42], He et al. [34] and Yanmaz et al. [70] in the form of IPFNs to predict the weight value of the assessment criteria in form of “Linguistic Values (LVs)”. Table 4 depicts the DE’s weight in accordance with Table 3. Table 5 explains the evaluation values of MSW options concerning the criteria based on DEs’ opinions. Table 6 presents the A-IPF-DM using Equation (14) and Table 5.
To calculate the criteria’s weights, the IPF-IS and IPF-A-IS for MSW treatment alternatives are given in Table 7 using Equations (15) and (16).
Based on Equation (21), we construct the LP model as follows:
max T = 0.0598 w 1 0.0517 w 2 0.1093 w 3 0.2748 w 4 0.1019 w 5 0.0879 w 6 + 0.0168 w 7 0.0448 w 8 + 0.2709 w 9 0.0223 w 10 0.0156 w 11 0.0016 w 12
s .   t .   = { 0.05 w 1 < 0.09 , 0.07 w 2 < 0.10 , 0.2 < w 3 0.25 , 0.04 w 4 < 0.08 , 0.08 w 5 < 0.10 , 0.01 < w 6 0.06 , 0.10 w 7 < 0.14 , 0.08 < w 8 0.12 , 0.07 < w 9 0.12 , 0.1 < w 10 0.12 , 0.09 < w 11 0.13 , 0.08 < w 12 0.11 , w j 0 , j = 1 12 w j = 1 , j = 1 ( 1 ) 12 .
After solving the model (27), the criteria weights are estimated and presented in Figure 4.
w 1 = 0.05 , w 2 = 0.07 , w 3 = 0.20 , w 4 = 0.04 , w 5 = 0.08 , w 6 = 0.01 , w 7 = 0.10 , w 8 = 0.08 , w 9 = 0.10 , w 10 = 0.10 , w 11 = 0.09 , w 12 = 0.08 .
Using (22)–(26), the assessment ratings of i ,   S * ( i ) ,   i ,   S * ( i ) ,   i and ϑ i of H i ( i = 1 ( 1 ) 8 ) are calculated with regard to the referred criteria P j ( j = 1 ( 1 ) 12 ) given in Table 8. Hence, plasma arc gasification ( H 4 ) is the best WTE technology for MSW treatment.

Comparison with Existing Methods

In the current part of the study, we discuss a comparison between the presented method and the extant IPF-TOPSIS model [57] for solving MCDM problems under IPFS context.
  • IPF-TOPSIS Approach
Steps 1–4: Follow the steps of the IPF-COPRAS method.
Step 5: Obtain the “normalized A-IPF-DM (N-A-IPF-DM)”.
The N-A-IPF-DM = [ ς i j ] s × t is assessed from Z = ( δ i j ) s × t , is given by
ς i j = { δ i j = ( [ μ i j , μ i j + ] , [ ν i j , ν i j + ] ) s × t , for benefit criterion , ( δ i j ) c = ( [ ν i j , ν i j + ] , [ μ i j , μ i j + ] ) s × t , for cos t criterion .
Step 6: Calculate the discriminations of each alternative from “interval-valued Pythagorean fuzzy-ideal solution (IPF-IS)” and “interval-valued Pythagorean fuzzy-anti ideal solution (IPF-A-IS)”.
Here, the interval-valued BD and NBD of IPF-IS are defined as 1 and 0, and they are given as follows θ + = [ 1 , 1 ] , [ 0 , 0 ] 1 × t . Similarly, IPF-A-IS is as follows θ = [ 0 , 0 ] , [ 1 , 1 ] 1 × n .
To obtain the diverse alternative(s) H i : i = 1 ( 1 ) s , compute the distance measures by
d ( H i , θ + ) = j = 1 n { w j ( S ( θ + ) S ( ς i j ) ) 2 } 2 ,
and
d ( H i , θ ) = j = 1 n { w j ( S ( ς i j ) S ( θ ) ) 2 } 2 ,
Step 7: Compute the “closeness index (CI)”.
The CI of an alternative is determined by
( H i ) = d ( H i , θ ) d ( H i , θ ) + d ( H i , θ + ) , i = 1 ( 1 ) s .
Step 8: Determine the prioritization of the options.
Corresponding to the preference ranking of ( H i ) : i = 1 ( 1 ) s , we prioritize the options, and thus, we obtain the most appropriate candidate(s).
Through the use of Table 6 and Equation (29), the N-A-IPF-DM is evaluated and given in Table 9. Now, the overall outcomes of the IPF-TOPSIS are given in Table 10.
The comparative results shown in Table 10 demonstrate that the most optimal WTE technology for MSW treatment option is H 4 , and ranking orders obtained by the proposed IPF-COPRAS model show great conformity with the IPF-TOPSIS [57] approach. As compared with the IPF-TOPSIS (Garg, 2017) approach, the ranking order is H 4 H 6 H 7 H 5 H 8 H 2 H 1 H 3 , whereas compared with the IPF-COPRAS method, the ranking order is H 4 H 7 H 6 H 5 H 8 H 2 H 3 H 1 . From Table 8 and Table 10, it is observed that the alternative plasma arc gasification ( H 4 ) has the highest UD in all the approaches.
As per the comparative study, the developed IPF-COPRAS approach has the following merits over the existing ones, as given in Figure 5:
In our approach, the weights of DEs are found with the help of the proposed formula based on Liu and Wang [54], ensuring a more accurate individual significance degree of DEs. Next, the optimal criteria weights in our methodology are obtained through the proposed similarity measure and LP optimization method, which results in outcomes that are more precise and optimal weights, unlike the arbitrarily chosen criteria’s weights by decision-makers in Garg [57].
In [57], the alternatives are prioritized using the relative closeness coefficient between the overall value of the alternative and the ideal alternative. In the IPF-COPRAS method, the benefit and the cost criteria are both considered. Considering that both the benefit and cost criteria with complex proportions contain more precise data than both the benefit criteria or cost criteria. Meanwhile, it increases the reliability of initial data and the precision of results as well.
In [57], the distance is calculated between the overall attribute value of an alternative and the IVP-IS ϑ + = [ 1 , 1 ] , [ 0 , 0 ] 1 × n and the IPF-AIS ϑ = [ 0 , 0 ] , [ 1 , 1 ] 1 × n to define the CI of each alternative on the given attributes. The IPF-IS and IPF-AIS may be treated as benchmarks against which the performance of the alternatives on each attribute is evaluated. Note that these benchmarks are too unrealistic to be achieved in practice. On the other hand, the COPRAS approach assumes both concerns of criteria according to the complex proportional evaluation, which holds more precise information than diverse existing methods basically considering the beneficial or non-beneficial attributes. Thus, in the process, the benchmarks are obtained on IPF-IS, IPF-AIS, similarity measure and compromise solution, which are more realistic in the sense that the decision-maker knows not only about the best and worst performance of alternatives on the given attributes but also a relative comparison of the performances among them.
When the number of criteria or options becomes very large, the IPF-COPRAS approach has more operability than the IPF-TOPSIS. In the IPF-COPRAS approach, there is no requirement to obtain the IPF-IS and the IPF-A-IS. The decision outcomes can be obtained through processing the realistic information, which allows the IPF-COPRAS approach to apply more intricate and realistic MCDM problems.

6. Conclusions

The present study introduces an “interval-valued Pythagorean fuzzy-complex proportional assessment (IPF-COPRAS)” method for assessing the “waste-to-energy (WTE)” technologies for “municipal solid waste (MSW)” treatment. This method is based on “similarity measure (SM)”, a linear programming model and the “complex proportional assessment (COPRAS)” approach within “interval-valued Pythagorean fuzzy sets (IPFSs)”. First, a novel formula has been introduced to estimate the “decision expert’s (DE’s)” weight. Second, in order to depict the criteria weights, a novel SM has been developed for “interval-valued Pythagorean fuzzy sets”. A comparison with extant similarity measures has been made to show the utility of the proposed similarity IPF-SM. A linear programming model has been developed using the proposed similarity measure to compute the criteria’s weights. In addition, a case study of WTE selection technologies for MSW treatment has been taken to show the feasibility of the presented IPF-COPRAS method. A comparison with extant method has been given to verify the outcomes found by the presented methodology. Thus, to handle with the “multi-criteria decision-making (MCDM)” problems, the IPF-COPRAS method provides an easy procedure of calculation with efficient and precise outcomes. Based on the analysis, the considered criteria are categorized in two dimensions, namely qualitative and quantitative dimensions. The most important criteria for selecting the appropriate WTE technology for MSW treatment are “greenhouse gas (GHG)” emissions, microbial inactivation efficacy, air emissions avoidance and public acceptance with the significance degree of 0.200 and 0.100, respectively. The evaluation results showed that the most appropriate WTE technology for MSW treatment is plasma arc gasification with a maximum utility degree of 0.717 followed by anaerobic digestion with a utility degree of 0.656 based on the identified criteria, which will assist with reducing the amount of waste and GHG emissions as well as minimizing and maintaining the costs of landfills.
The certain limitations of the developed framework are important to be aware of. A practical difficulty is that decision experts must be trained with the preference style to properly utilize the flexibility and potential of IPFSs. In the following, we present the limitations of the introduced decision-making methodology. (a) An objective weighting procedure is applied to obtain the significance weight value of criteria that is determined from the decision matrices and is derived according to the knowledge presented by experts. (b) As the waste-to-energy technology selection problem becomes increasingly serious, more dimensions of sustainability should be considered in waste-to-energy technology assessment. Furthermore, the developed methodology will be extended to “intuitionistic fuzzy hypersoft sets”, “complex spherical fuzzy N-soft sets” and “semiring-valued fuzzy sets”.
The MSW management is a concern for the environmental engineers, township developers and the local community due to its increasing amount and limited land resources. This leads to the objective whereby most of the latest efforts concentrate on “zero waste” and/or “zero landfilling”, which is indeed expensive [71] for less economy. Around 55% capacity on MSW landfills can be reduced using the “refuse derived fuel (RDF)” in the cement firms. It is a better choice for the eco-friendly disposal and for improving its energy potential, but it has area restrictions. The comprehensive procedure of MSW management is not viable for the small local community because of a lack of financial supports [72]. Hence, developing nations should find area-specific solutions to their concerns [73] in the MSW management. The application of a “plasma gasification process (PGP)” in “waste-to-energy” relieves the pressure on distressed landfills and provides an environmentally benign procedure of disposing MSW [74]. The MSW is considered as a “renewable energy source”, and the “plasma gasification technology” is one of the leading-edge procedures available to harness this energy.
In the recent past, the “United States (US)” government officially stated the MSW as a “renewable source of energy”, and power generation with the use of MSW is considered green power and capable for all suitable incentives. The elucidation is described as “Prescription for the planet: the painless remedy for our energy & environmental crises” [74]. Plasma technology purports to be an economic and ample source of energy as well as a reliable source of power. Viewing to various implementations of the plasma gasification procedure, the profit potential of plasma conversion is tremendous [74]. Private firms could construct facilities in developing nations, and it would naturally be in their financial best interest to create the garbage collection infrastructure to assist their business; indirectly, the collection process will be upgraded. This is an impeccable niche for the oil firms. Plasma converters characterize the ultimate in recycling, building virtually 100% of the waste a household usually generates into usable and even valuable end products [74]. There would be no requirement to have two garbage pickups every week, one for trash and one for recyclables that societies have become accustomed to separating. The plasma gasification procedure of MSW has all the qualities of implementation; while there are several divergences among scientists and policy-makers on these concerns, there is, however, agreement that option sources of energy that are sustainable, environmentally friendly and locally accessible must be the best alternative.
The sustainability of any MSW management scheme depends on various factors [75]; however, the most significant one is the will of the people/society to change the extant procedure and create something better. The acceptance of latest technologies has to be taken into account as well as the selection of a waste management system. However, for any MSW management to be successful, the government or firms should step up and take the vital initiatives. Although financial restraints are a part of the scheme, the government can make a proper and sincere assurance for eradicating garbage from the planet. There is a requirement to create environmental awareness and change the behavior of people/societies regarding waste for sustainable waste management organizations. Now, the government and societies of India are trying to take several actions concerning MSW management and to produce energy from waste.

Author Contributions

Conceptualization, A.R.M., D.P., I.M.H., R.K.C. and P.R.; methodology, A.R.M., D.P., I.M.H., R.K.C. and P.R.; software, D.B. and G.Ć.; validation, A.R.M., D.P. and I.M.H.; formal analysis, A.R.M., D.P., D.B. and G.Ć.; investigation, A.R.M., D.P., I.M.H., R.K.C. and P.R.; writing—original draft preparation, A.R.M., D.P., I.M.H., R.K.C., P.R., D.B. and G.Ć.; writing—review and editing, A.R.M., D.P., I.M.H., R.K.C., P.R., D.B. and G.Ć.; supervision, A.R.M. and D.P. All authors have read and agreed to the published version of the manuscript.

Funding

This paper is supported by the Researchers Supporting Project number (RSP-2021/389), King Saud University, Riyadh, Saudi Arabia.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Informed consent was obtained from all subjects involved in the study.

Data Availability Statement

Not applicable.

Acknowledgments

The authors are grateful for the anonymous reviewers for their valuable comments and suggestions.

Conflicts of Interest

The authors declare no conflict of interest.

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Figure 1. Geometrical representations of IF/IIFNs and PF/IPFNs with spaces of (a) IFNs and PFNs, (b) IIFNs and IPFNs.
Figure 1. Geometrical representations of IF/IIFNs and PF/IPFNs with spaces of (a) IFNs and PFNs, (b) IIFNs and IPFNs.
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Figure 2. Performance structure of the proposed IPF-COPRAS approach.
Figure 2. Performance structure of the proposed IPF-COPRAS approach.
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Figure 3. Hierarchical structure of WTE technology for MSW treatment assessment.
Figure 3. Hierarchical structure of WTE technology for MSW treatment assessment.
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Figure 4. Criteria weight of WTE technology for MSW treatment assessment.
Figure 4. Criteria weight of WTE technology for MSW treatment assessment.
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Figure 5. Comparison of utility degree/closeness index of each for MSW treatment.
Figure 5. Comparison of utility degree/closeness index of each for MSW treatment.
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Table 1. Comparison results of introduced IPF-SM with extant ones.
Table 1. Comparison results of introduced IPF-SM with extant ones.
K
L
S H ( K , L ) S E ( K , L ) S H H ( K , L ) S H E ( K , L ) S Z ( K , L ) S 2 ( K , L )
( [ 0.26 , 0.36 ] , [ 0.26 , 0.36 ] ) ( [ 0.36 , 0.46 ] , [ 0.36 , 0.46 ] ) 0.90.90.90.90.88540.9119
( [ 0.26 , 0.36 ] , [ 0.36 , 0.46 ] ) ( [ 0.36 , 0.46 ] , [ 0.26 , 0.36 ] ) 0.90.90.90.90.9280.9425
( [ 1.00 , 1.00 ] , [ 0.00 , 0.00 ] ) ( [ 0.00 , 0.00 ] , [ 1.00 , 1.00 ] ) 0.00.00.00.00.00.0
( [ 1.00 , 1.00 ] , [ 0.00 , 0.00 ] ) ( [ 0.00 , 0.00 ] , [ 0.00 , 0.00 ] ) 0.50.29290.00.00.00.3133
( [ 0.50 , 0.0 ] , [ 0.50 , 0.50 ] ) ( [ 0.00 , 0.00 ] , [ 0.00 , 0.00 ] ) 0.50.50.50.50.60360.7155
( [ 0.36 , 0.46 ] , [ 0.16 , 0.26 ] ) ( [ 0.46 , 0.56 ] , [ 0.26 , 0.36 ] ) 0.90.90.90.90.88480.9113
( [ 0.36 , 0.46 ] , [ 0.16 , 0.26 ] ) ( [ 0.46 , 0.56 ] , [ 0.16 , 0.26 ] ) 0.950.92930.90.90.92700.9427
Note: “Bold” symbolizes an unreasonable result that means counter-intuitive cases.
Table 2. Assessment criteria for the WTE technology selection for MSW treatment.
Table 2. Assessment criteria for the WTE technology selection for MSW treatment.
Criteria DimensionCriteriaTypeAlternatives
Quantitative criteriaTreatment cost (P1)Cost
Disposal cost (P2)Cost
GHG emissions (P3)BenefitIncineration (H1)
Reduction in volume (P4)BenefitGasification (H2)
Water use (P5)BenefitPyrolysis (H3)
Pathogen inactivation (P6)BenefitPlasma arc gasification (H4)
Qualitative criteriaMicrobial inactivation efficacy (P7)BenefitThermal de-polymerization(H5)
Types of waste treated (P8)BenefitHydrothermal carbonization (H6)
Air emissions avoidance (P9)BenefitAnaerobic digestion (H7)
Public acceptance (P10)BenefitFermentation (H8)
Treatment effectiveness (P11)Benefit
Ease of operation (P12)Benefit
Table 3. Performance ratings of alternatives in terms of linguistic values.
Table 3. Performance ratings of alternatives in terms of linguistic values.
Linguistic ValuesIPFNs
Perfectly Good (PG/PH)([0.90, 0.95], [0.05, 0.10])
Very Good (VG/VH)([0.80, 0.90], [0.20, 0.35])
Good (G/H)([0.65, 0.80], [0.40, 0.50])
Moderate Good (MG/MH)([0.50, 0.65], [0.50, 0.60])
Fair (F/H)([0.40, 0.50], [0.60, 0.70])
Moderate Low (ML)([0.30, 0.40], [0.70, 0.80])
Low (L)([0.20, 0.30], [0.80, 0.85])
Very low (VL)([0.10, 0.20], [0.85, 0.90])
Very low (VVL)([0.05, 0.10], [0.90, 0.95])
Table 4. Assessment of DEs’ weight.
Table 4. Assessment of DEs’ weight.
DEsD1D2D3D4
IPFNs([0.65, 0.80], [0.40, 0.50])([0.50, 0.65], [0.50, 0.60])([0.40, 0.50], [0.60, 0.70])([0.30, 0.40], [0.70, 0.80])
Weights0.42840.28900.17780.1048
Table 5. LVs of WTE technology for MSW treatment method selection with respect to DEs.
Table 5. LVs of WTE technology for MSW treatment method selection with respect to DEs.
H1H2H3H4H5H6H7H8
P1(L,VL,L,L)(ML,L,L,ML)(F,ML,L,F)(F,MG,F,G)(ML,M,M,MG)(MG,F,ML,L)(L,VL,VL,VL)(VL,L,L,VL)
P2(F,F,ML,L)(VL,M,ML,M)(MG,ML,M,ML)(ML,M,ML,L)(MG,ML,L,M)(L,M,ML,ML)(L,L,VL,VL)(L,ML,ML, ML)
P3(F,MG,MG,G)(G,MG,F,G)(ML,MG,MG,G)(VG,M,VG,G)(G,F,MG,G)(VG,F,MG,G)(MG,F,F,F)(L,F,G,G)
P4(F,MG,F,G)(MG,F,G,G)(G,F,MG,G)(VG,VG,VG,G)(ML,MG,MG,G)(G,MG,MG,G)(G,MG,G,ML)(MG,MG,G,ML)
P5(MG,F,F,G)(VG,F,F,MG)(F,G,G,MG)(G,MG,F,G)(MG,F,L,G)(G,ML,F,G)(G,VG,VG,G)(G,G,ML,ML)
P6(G,MG,G,ML)(MG,MG,G,M)(G,VG,VG,ML)(G,F,MG,MG)(F,MG,F,MG)(F,F,ML,G)(F,F,F,G)(VG,ML,G,G)
P7(F,MG,G,MG)(MG,MG,VG,ML)(G,MG,G,ML)(M,ML,G,MG)(F,MG,G,G)(F,MG,G,ML)(F,MG,G,VG)(MG,MG,VG,MG)
P8(F,MG,G,L)(MG,F,VG,ML)(G,G,L,MG)(G,VG,G,ML)(MG,G,G,L)(MG,G,G,MG)(G,L,G,ML)(M,L,G,G)
P9(MG,M,G,M)(VL,ML,L,MG)(M,L,MG,ML)(VH,VH,H,H)(VH,H,M,MG)(VH,L,MH,ML)(VH,VH,H,ML)(ML,MG,G,G)
P10(G,MG.F,H)(F,F,G,G)(F,F,G,H)(G,VG,F,L)(VG,G,MG,M)VG,G,MG,MG)(F,MG,G,G)(MG,F,VG,G)
P11(F,MG,MG,G)(G,MG,G,L)(G,ML,MG,L)(VG,MG,VG,MG)(G,F,MG,ML)(G,MG,G,ML)(G,G,G,ML)(F,VG,G,L)
P12(F,MG,F,G)(MG,F,G,F)(G,F,MG,G)(VG,L,VG,ML)(G,MG,ML,MG)(G,G,ML,ML)(MG,G,G,ML)(G,VG,F,F)
Table 6. A-IPF-DM of WTE technology for MSW treatment alternatives.
Table 6. A-IPF-DM of WTE technology for MSW treatment alternatives.
H1H2H3H4H5H6H7H8
P1([0.177, 0.275], [0.814, 0.864]) ([0.259, 0.358], [0.745, 0.823]) ([0.346, 0.445], [0.660, 0.753]) ([0.467, 0.597], [0.546, 0.646])([0.375, 0.484], [0.629, 0.729]) ([0.421, 0.549], [0.588, 0.685]) ([0.152, 0.248], [0.782, 0.856]) ([0.155, 0.252], [0.826, 0.876])
P2([0.369, 0.468], [0.636, 0.732]) ([0.293, 0.386], [0.716, 0.798]) ([0.417, 0.547], [0.590, 0.691]) ([0.325, 0.425], [0.679, 0.775])([0.402, 0.532], [0.611, 0.705]) ([0.300, 0.398], [0.709, 0.790]) ([0.178, 0.276], [0.814, 0.864]) ([0.263, 0.362], [0.741, 0.821])
P3([0.484, 0.621], [0.528, 0.629]) ([0.578, 0.728], [0.459, 0.560]) ([0.455, 0.596], [0.564, 0.666]) ([0.719, 0.835], [0.295, 0.444])([0.571, 0.718], [0.468, 0.569]) ([0.670, 0.795], [0.348, 0.489]) ([0.447, 0.574], [0.555, 0.655]) ([0.447, 0.581], [0.605, 0.692])
P4([0.467, 0.597], [0.546, 0.646]) ([0.529, 0.675], [0.495, 0.596]) ([0.571, 0.718], [0.468, 0.569]) ([0.788, 0.893], [0.215, 0.363])([0.455, 0.596], [0.564, 0.666]) ([0.590, 0.742], [0.444, 0.544]) ([0.589, 0.741], [0.452, 0.554]) ([0.519, 0.669], [0.498, 0.599])
P5([0.480, 0.616], [0.532, 0.633]) ([0.650, 0.771], [0.368, 0.512]) ([0.551, 0.694], [0.487, 0.589]) ([0.578, 0.728], [0.459, 0.560])([0.461, 0.598], [0.560, 0.655]) ([0.544, 0.690], [0.505, 0.608]) ([0.733, 0.856], [0.289, 0.423]) ([0.586, 0.737], [0.469, 0.571])
P6([0.589, 0.741], [0.452, 0.554]) ([0.525, 0.674], [0.490, 0.590]) ([0.717, 0.841], [0.307, 0.445]) ([0.554, 0.701], [0.479, 0.580])([0.443, 0.569], [0.558, 0.659]) ([0.425, 0.540], [0.591, 0.692]) ([0.439, 0.553], [0.575, 0.676]) ([0.680, 0.806], [0.349, 0.492])
P7([0.498, 0.637], [0.520, 0.621]) ([0.573, 0.712], [0.440, 0.562]) ([0.589, 0.741], [0.452, 0.554]) ([0.453, 0.582], [0.573, 0.674])([0.518, 0.659], [0.508, 0.609]) ([0.483, 0.618], [0.538, 0.640]) ([0.551, 0.687], [0.472, 0.586]) ([0.585, 0.725], [0.425, 0.545])
P8([0.478, 0.614], [0.546, 0.644]) ([0.553, 0.684], [0.464, 0.587]) ([0.592, 0.744], [0.463, 0.560]) ([0.687, 0.820], [0.347, 0.474])([0.565, 0.717], [0.473, 0.572]) ([0.580, 0.733], [0.451, 0.551]) ([0.546, 0.697], [0.518, 0.612]) ([0.463, 0.596], [0.581, 0.673])
P9([0.501, 0.641], [0.516, 0.617]) ([0.258, 0.364], [0.752, 0.825]) ([0.370, 0.484], [0.641, 0.731]) ([0.767, 0.879], [0.243, 0.387])([0.694, 0.820], [0.327, 0.464]) ([0.628, 0.754], [0.408, 0.552]) ([0.754, 0.867], [0.258, 0.407]) ([0.493, 0.638], [0.542, 0.645])
P10([0.578, 0.728], [0.459, 0.560]) ([0.494, 0.625], [0.535, 0.637]) ([0.494, 0.625], [0.535, 0.637]) ([0.657, 0.790], [0.378, 0.506])([0.697, 0.824], [0.323, 0.459]) ([0.702, 0.829], [0.317, 0.452]) ([0.518, 0.659], [0.508, 0.609]) ([0.582, 0.717], [0.437, 0.559])
P11([0.484, 0.621], [0.528, 0.629]) ([0.586, 0.738], [0.459, 0.557]) ([0.522, 0.670], [0.526, 0.625]) ([0.721, 0.840], [0.287, 0.433])([0.541, 0.686], [0.496, 0.598]) ([0.589, 0.741], [0.452, 0.554]) ([0.628, 0.779], [0.424, 0.525]) ([0.613, 0.740], [0.419, 0.551])
P12([0.467, 0.597], [0.546, 0.646]) ([0.501, 0.641], [0.516, 0.617]) ([0.571, 0.718], [0.468, 0.569]) ([0.688, 0.807], [0.340, 0.493])([0.553, 0.704], [0.482, 0.584]) ([0.586, 0.737], [0.469, 0.571]) ([0.568, 0.720], [0.467, 0.568]) ([0.663, 0.795], [0.367, 0.496])
Table 7. IPF-IS and IPF-A-IS WTE technology for MSW treatment alternatives.
Table 7. IPF-IS and IPF-A-IS WTE technology for MSW treatment alternatives.
Criteria Ψ + Ψ
P1([0.152, 0.248], [0.826, 0.876])([0.467, 0.597], [0.546, 0.646])
P2([0.178, 0.276], [0.814, 0.864])([0.417, 0.547], [0.590, 0.691])
P3([0.719, 0.835], [0.295, 0.444])([0.447, 0.574], [0.605, 0.692])
P4([0.788, 0.893], [0.215, 0.363])([0.455, 0.596], [0.564, 0.666])
P5([0.733, 0.856], [0.289, 0.423])([0.461, 0.598], [0.560, 0.655])
P6([0.717, 0.841], [0.307, 0.445])([0.425, 0.540], [0.591, 0.692])
P7([0.589, 0.741], [0.425, 0.545])([0.453, 0.582], [0.573, 0.674])
P8([0.687, 0.820], [0.347, 0.474])([0.463, 0.596], [0.581, 0.673])
P9([0.767, 0.879], [0.243, 0.387])([0.258, 0.364], [0.752, 0.825])
P10([0.702, 0.829], [0.317, 0.452])([0.494, 0.625], [0.535, 0.637])
P11([0.721, 0.840], [0.287, 0.433])([0.484, 0.621], [0.528, 0.629])
P12([0.688, 0.807], [0.340, 0.493])([0.467, 0.597], [0.546, 0.646])
Table 8. The evaluation results of the IPF-COPRAS approach.
Table 8. The evaluation results of the IPF-COPRAS approach.
Options i S * ( i ) i S * ( i ) i ϑ i Ranking
H1([0.471, 0.607], [0.563, 0.658]) 0.477 ([0.108, 0.145], [0.959, 0.971])0.0430.522 72.774 8
H2([0.514, 0.651], [0.533, 0.637]) 0.520 ([0.099, 0.134], [0.963, 0.975])0.0380.571 79.593 6
H3([0.493, 0.634], [0.559, 0.655]) 0.494 ([0.140, 0.188], [0.944, 0.961])0.0600.526 73.369 7
H4([0.654, 0.781], [0.386, 0.523]) 0.685 ([0.141, 0.188], [0.944, 0.961])0.0600.717 100.00 1
H5([0.552, 0.693], [0.496, 0.603]) 0.567 ([0.140, 0.190], [0.944, 0.961])0.0610.59983.474 4
H6([0.583, 0.720], [0.465, 0.583]) 0.602 ([0.127, 0.172], [0.951, 0.965])0.0530.638 89.0203
H7([0.563, 0.701], [0.485, 0.597]) 0.579 ([0.058, 0.093], [0.974, 0.982])0.0250.656 91.506 2
H8([0.521, 0.657], [0.532, 0.638]) 0.523 ([0.079, 0.114], [0.970, 0.980])0.0300.58781.9025
Table 9. The N-A-IPF-DM of WTE technology for MSW treatment alternatives.
Table 9. The N-A-IPF-DM of WTE technology for MSW treatment alternatives.
H1H2H3H4H5H6H7H8
P1([0.814,0.864], [0.177, 0.275]) ([0.745, 0.823], [0.259, 0.358]) ([0.660,0.753], [0.346, 0.445]) ([0.546, 0.646], [0.467, 0.597])([0.629, 0.729], [0.375, 0.484]) ([0.588, 0.685], [0.421, 0.549]) ([0.782, 0.856], [0.152, 0.248]) ([0.826, 0.876], [0.155, 0.252])
P2([0.636,0.732], [0.369, 0.468]) ([0.716, 0.798], [0.293, 0.386]) ([0.590,0.691], [0.417, 0.547]) ([0.679, 0.775], [0.325, 0.425])([0.611, 0.705], [0.402, 0.532]) ([0.709, 0.790], [0.300, 0.398]) ([0.814, 0.864], [0.178, 0.276]) ([0.741, 0.821], [0.263, 0.362])
P3([0.484,0.621], [0.528, 0.629]) ([0.578, 0.728], [0.459, 0.560]) ([0.455,0.596], [0.564, 0.666]) ([0.719, 0.835], [0.295, 0.444])([0.571, 0.718], [0.468, 0.569]) ([0.670, 0.795], [0.348, 0.489]) ([0.447, 0.574], [0.555, 0.655]) ([0.447, 0.581], [0.605, 0.692])
P4([0.467,0.597], [0.546, 0.646]) ([0.529, 0.675], [0.495, 0.596]) ([0.571,0.718], [0.468, 0.569]) ([0.788, 0.893], [0.215, 0.363])([0.455, 0.596], [0.564, 0.666]) ([0.590, 0.742], [0.444, 0.544]) ([0.589, 0.741], [0.452, 0.554]) ([0.519, 0.669], [0.498, 0.599])
P5([0.480,0.616], [0.532, 0.633]) ([0.650, 0.771], [0.368, 0.512]) ([0.551,0.694], [0.487, 0.589]) ([0.578, 0.728], [0.459, 0.560])([0.461, 0.598], [0.560, 0.655]) ([0.544, 0.690], [0.505, 0.608]) ([0.733, 0.856], [0.289, 0.423]) ([0.586, 0.737], [0.469, 0.571])
P6([0.589,0.741], [0.452, 0.554]) ([0.525, 0.674], [0.490, 0.590]) ([0.717,0.841], [0.307, 0.445]) ([0.554, 0.701], [0.479, 0.580])([0.443, 0.569], [0.558, 0.659]) ([0.425, 0.540], [0.591, 0.692]) ([0.439, 0.553], [0.575, 0.676]) ([0.680, 0.806], [0.349, 0.492])
P7([0.498,0.637], [0.520, 0.621]) ([0.573, 0.712], [0.440, 0.562]) ([0.589,0.741], [0.452, 0.554]) ([0.453, 0.582], [0.573, 0.674])([0.518, 0.659], [0.508, 0.609]) ([0.483, 0.618], [0.538, 0.640]) ([0.551, 0.687], [0.472, 0.586]) ([0.585, 0.725], [0.425, 0.545])
P8([0.478,0.614], [0.546, 0.644]) ([0.553, 0.684], [0.464, 0.587]) ([0.592,0.744], [0.463, 0.560]) ([0.687, 0.820], [0.347, 0.474])([0.565, 0.717], [0.473, 0.572]) ([0.580, 0.733], [0.451, 0.551]) ([0.546, 0.697], [0.518, 0.612]) ([0.463, 0.596], [0.581, 0.673])
P9([0.501,0.641], [0.516, 0.617]) ([0.258, 0.364], [0.752, 0.825]) ([0.370,0.484], [0.641, 0.731]) ([0.767, 0.879], [0.243, 0.387])([0.694, 0.820], [0.327, 0.464]) ([0.628, 0.754], [0.408, 0.552]) ([0.754, 0.867], [0.258, 0.407]) ([0.493, 0.638], [0.542, 0.645])
P10([0.578,0.728], [0.459, 0.560]) ([0.494, 0.625], [0.535, 0.637]) ([0.494,0.625], [0.535, 0.637]) ([0.657, 0.790], [0.378, 0.506])([0.697, 0.824], [0.323, 0.459]) ([0.702, 0.829], [0.317, 0.452]) ([0.518, 0.659], [0.508, 0.609]) ([0.582, 0.717], [0.437, 0.559])
P11([0.484,0.621], [0.528, 0.629]) ([0.586, 0.738], [0.459, 0.557]) ([0.522,0.670], [0.526, 0.625]) ([0.721, 0.840], [0.287, 0.433])([0.541, 0.686], [0.496, 0.598]) ([0.589, 0.741], [0.452, 0.554]) ([0.628, 0.779], [0.424, 0.525]) ([0.613, 0.740], [0.419, 0.551])
P12([0.467,0.597], [0.546, 0.646]) ([0.501, 0.641], [0.516, 0.617]) ([0.571,0.718], [0.468, 0.569]) ([0.688, 0.807], [0.340, 0.493])([0.553, 0.704], [0.482, 0.584]) ([0.586, 0.737], [0.469, 0.571]) ([0.568, 0.720], [0.467, 0.568]) ([0.663, 0.795], [0.367, 0.496])
Table 10. Ranking orders of IPF-TOPSIS for MSW treatment alternatives.
Table 10. Ranking orders of IPF-TOPSIS for MSW treatment alternatives.
Options Ranking
H11.36371.55840.53337
H21.30521.73130.57026
H31.37311.55040.53038
H40.81292.17360.72781
H51.12401.78700.61394
H60.97541.93400.66472
H71.11691.93280.63383
H81.24311.76210.58645
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Mishra, A.R.; Pamučar, D.; Hezam, I.M.; Chakrabortty, R.K.; Rani, P.; Božanić, D.; Ćirović, G. Interval-Valued Pythagorean Fuzzy Similarity Measure-Based Complex Proportional Assessment Method for Waste-to-Energy Technology Selection. Processes 2022, 10, 1015. https://0-doi-org.brum.beds.ac.uk/10.3390/pr10051015

AMA Style

Mishra AR, Pamučar D, Hezam IM, Chakrabortty RK, Rani P, Božanić D, Ćirović G. Interval-Valued Pythagorean Fuzzy Similarity Measure-Based Complex Proportional Assessment Method for Waste-to-Energy Technology Selection. Processes. 2022; 10(5):1015. https://0-doi-org.brum.beds.ac.uk/10.3390/pr10051015

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Mishra, Arunodaya Raj, Dragan Pamučar, Ibrahim M. Hezam, Ripon K. Chakrabortty, Pratibha Rani, Darko Božanić, and Goran Ćirović. 2022. "Interval-Valued Pythagorean Fuzzy Similarity Measure-Based Complex Proportional Assessment Method for Waste-to-Energy Technology Selection" Processes 10, no. 5: 1015. https://0-doi-org.brum.beds.ac.uk/10.3390/pr10051015

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