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Revista Chapingo serie ciencias forestales y del ambiente

versión On-line ISSN 2007-4018versión impresa ISSN 2007-3828

Rev. Chapingo ser. cienc. for. ambient vol.27 no.2 Chapingo may./ago. 2021  Epub 26-Ene-2024

https://doi.org/10.5154/r.rchscfa.2020.06.043 

Scientific articles

Application of a multigranular approach based on the 2-tuple fuzzy linguistic model for the evaluation of forestry policy indicators

José L. Romo-Lozano1 

Rosa M. Rodríguez*  2 

Roberto Rendón-Medel1 

Álvaro Labella2 

1 Universidad Autónoma Chapingo. km 38.5 Carretera México-Texcoco, Chapingo. C. P. 56230. Texcoco, Estado de México, México.

2 Universidad de Jaén, Campus Las Lagunillas. C. P. 23071. Jaén, España.


Abstract

Introduction:

The need for quality indicators is well recognized by users and proponents of public policy evaluation. Indicators recurrently include qualitative attributes for which there are few studies assessing the level of compliance.

Objective:

To apply a multigranular approach, based on the 2-tuple fuzzy linguistic model, to evaluate 13 indicators of the National Forestry Program, established in the system of social policy indicators derived from the National Development Plan 2012-2018 of Mexico.

Materials and methods:

The method uses the 2-tuple fuzzy linguistic representation model and an extension called extended linguistic hierarchies, designed to solve problems with multigranular linguistic information. The indicators' level of compliance was evaluated based on four criteria: clarity, relevance, monitoring, and adequacy.

Results and discussion:

The structure defined in evaluating social policy indicators corresponds appropriately to that used with the 2-tuple fuzzy linguistic model. The evaluation resulted in a sorted list in which the indicator “Rate of change of timber forest production” had the best rating with a “very high” level of compliance; 10 other indicators had the “high” level of compliance, and the remaining two indicators were rated with “moderate” compliance.

Conclusions:

The 2-tuple fuzzy linguistic model allowed the appropriate evaluation of the level of compliance with the desirable attributes of indicators.

Keywords: National Forest Program; qualitative assessment; fuzzy sets; linguistic hierarchies; expert panels

Resumen

Introducción:

La necesidad de indicadores de calidad es notoriamente reconocida por usuarios y proponentes en el tema de evaluación de políticas públicas. Los indicadores incluyen, de manera recurrente, atributos cualitativos para los cuales hay pocos estudios que evalúen el nivel de cumplimiento.

Objetivo:

Aplicar un enfoque multigranular, basado en el modelo lingüístico difuso 2-tupla, a la evaluación de 13 indicadores del Programa Nacional Forestal, establecidos en el sistema de indicadores de la política social derivados del Plan Nacional de Desarrollo 2012-2018 de México.

Materiales y métodos:

El método utiliza el modelo de representación lingüístico difuso 2-tupla y una extensión llamada jerarquías lingüísticas extendidas, diseñada para resolver problemas con información lingüística multigranular. El nivel de cumplimiento de los indicadores se evaluó con base en cuatro criterios: claridad, relevancia, monitoreo y adecuación.

Resultados y discusión:

La estructura que se define en el proceso de evaluación de indicadores de política social corresponde de manera apropiada a la utilizada con el modelo lingüístico difuso 2-tupla. La evaluación resultó en una lista ordenada en la que el indicador “Tasa de variación de la producción forestal maderable” obtuvo la mejor calificación con un nivel de cumplimiento “muy alto”; otros 10 indicadores tuvieron el nivel de cumplimiento “alto” y los dos indicadores restantes se calificaron con un cumplimiento “medio”.

Conclusiones:

El modelo lingüístico difuso 2-tupla permitió la evaluación apropiada del nivel de cumplimiento de los atributos deseables en los indicadores.

Palabras clave: Programa Nacional Forestal; evaluación cualitativa; conjuntos difusos; jerarquías lingüísticas; paneles de expertos.

Highlights:

  • Thirteen indicators of the National Forest Program (2012-2018) were evaluated qualitatively.

  • Level of compliance for the following criteria was evaluated: clarity, relevance, monitoring and adequacy.

  • Compliance with the criteria of the indicators was assessed appropriately using fuzzy logic.

  • The indicator "Rate of change of timber forest production" had the best evaluation.

Introduction

In the area of public policy, there is a variety of indicators used for the evaluation of different stages and outcomes of interest (De la Cuesta, Pardo, & Paredes, 2015; Guayanlema, Fernández, & Arias, 2017; Guillen, Badi, Garza, & Acuña, 2015). Users and proponents notoriously recognize the need for quality indicators. In Mexico, the literature reports very few studies that address compliance levels that the criteria must satisfy. One of these studies was conducted by the National Council for the Evaluation of Social Development Policy (CONEVAL, 2014), and another was performed by the World Bank (2016).

The CONEVAL's evaluation proposal consists of two stages: integral assessment and specific assessment of results indicators. This process involves the participation of public servants, those responsible for the programs to which the indicators correspond, and representatives of the federal public sector. The first stage consists of determining whether indicators meet the minimum design criteria: clarity, relevance, monitoring, and adequacy. Two methodological support sheets are used: the results indicator matrix sheet and the indicator evaluation sheet. All questions used in the sections of these sheets are binary (yes/no). The second stage (specific assessment) is intended to determine the compliance with the indicators' minimum consistency criteria. Questions included are also binary, and the evaluator is asked to add the reason for his/her answer. Furthermore, the CONEVAL performs a statistical validation by applying a Rasch metric model used in a wide range of situations to measure subjective valuation. Finally, based on the results of these two stages and observations derived from statistical validation, an approval report is issued, if applicable, for the set of indicators of the corresponding program.

On the other hand, the instrument proposed by a World Bank Group, “Tool for evaluating the quality of indicators,” like the CONEVAL evaluation process, involves a broad group of invitees with sufficient experience in the sector to which the programs being evaluated with the indicators in question correspond. The process includes three parts: (a) evaluation of the quality of indicators, (b) evaluation of the quality of indicator targets, and (c) evaluation of the quality of information sources. Most of the data collection forms have four response options: 0 when the question's assumption is not satisfied, 3 when there is an intermediate level of satisfaction, 5 when the level of satisfaction is null, and 99 when it is not applicable. Finally, averages are calculated and converted to percentages with which the quality of the indicators analyzed is rated.

Evaluations and analyses of indicators have been conducted in several areas of knowledge. For example, Kühnen and Hahn (2017) reviewed trends, consistencies, inconsistencies, and gaps in investigating social life cycle assessment indicators. Whitehead (2017) analyzed and prioritized a list of sustainability indicators. Vignesh et al. (2017) evaluated a set of pollution indicators. The list of this type of indicator assessment includes Evans, Strezov, and Evans (2009), and Chenoweth (2008).

Evaluation processes that frequently use quantitative and qualitative information commonly correspond to a complex framework with a high degree of uncertainty. which has traditionally been approached from probabilistic models in classical decision theory; however, uncertainty involves aspects with a non-probabilistic character, because they are related to imprecision and vagueness of the meaning perceived by those performing the evaluation (Martínez, Rodríguez, & Herrera, 2015; Torres & Tranchita, 2014). When the information used in the evaluation process is qualitative, the use of linguistic variables represents a good option to model it (Herrera & Martínez, 2001a). In this respect, “Human beings possess two remarkable capabilities; the first is the ability to communicate, reason, and make rational decisions in an environment of imprecision, uncertainty, and incomplete information. The second is the ability to execute a wide variety of physical and mental tasks without any measurement and no calculations” (Mendel et al., 2010). Also, there are examples of successful applications in different fields where assessments have been performed using fuzzy logic (Gothwal & Raj, 2019; Montignac et al., 2015; Pirlot, Teghem, Ulungu, Bulens, & Goffin, 2015; Wang, Yang, & Cheng, 2019).

The present research objective was to apply a multigranular approach based on the 2-tuple fuzzy linguistic model to the evaluation of 13 indicators of the National Forestry Program established in the system of social policy indicators derived from the National Development Plan 2012-2018 of Mexico.

Materials and methods

The method proposed in this study for the evaluation of indicators differs from those already mentioned. It uses tools developed in the framework of fuzzy logic, specifically, the 2-tuple fuzzy linguistic representation model proposed by Herrera and Martinez (2000) and the extended linguistic hierarchy approach (ELH) developed by Espinilla, Liu, and Martínez (2011).

The evaluation of indicators is framed in a decision-making process. In this sense, Martínez et al. (2015) consider that such a process comprises at least the following five phases: intelligence, modeling, information gathering, analysis, and selection. Figure 1 describes the proposed process for evaluating forest policy indicators based fundamentally on the phases mentioned above with some modifications.

Figure 1 Forest policy indicator evaluation process used in this study. Source: Modified from Martínez et al. (2015). 

Forestry indicators evaluation process

Defining indicators

The definition must be clear and include at least the objective to which the indicator is grouped within the public policy to which it corresponds, calculation method, clearly specified units, and source of information. The indicators evaluated in this study are shown in Figure 2.

Figure 2 Objectives and indicators of Mexico’s National Forestry Program established in the National Development Plan 2012-2018. Source: CONEVAL (2017). 

Model of evaluation

The development considers the 2-tuple fuzzy linguistic fuzzy representation model and the JLE approach designed to solve problems with multigranular linguistic information.

The 2-tuple fuzzy linguistic representation model proposed by Herrera and Martinez (2000) is symbolic and is defined under computing with words approach where the linguistic results are obtained starting from linguistic premises. While other linguistic approaches carry out approximation processes to obtain the results, which implies a loss of information and precision in the results, the 2-tuple fuzzy linguistic model provides a continuous fuzzy representation for linguistic values, overcoming precision limitations of previous models (Pei, Ruan, Liu, & Xu, 2009). The model represents the linguistic information using a pair of values known as 2-tuple (s, α), where s is a linguistic term, and α is a numerical value representing the symbolic translation (Herrera & Martínez, 2001a).

Definition 1 (Herrera & Martínez, 2000): Let β be the result of an aggregation of the indices of a set of labels evaluated on a set of linguistic terms S; that is, the result of a symbolic aggregation operation β0, g, where g + 1 is the cardinality of S. Let i = round(β) and α = β ─ i be two values such that i0, g and α-0.5, 0.5 then α is called a symbolic translation.

The model also defines a set of functions to make transformations between 2-tuple values and numeric values.

Definition 2 (Herrera & Martínez, 2000): Let S=s0, , sg be a linguistic term set and β0, g a value that supports the result of a symbolic aggregation operation. Then, the 2-tuple value expressing the information equivalent to β is obtained by the following function  =0,gS×-0.5, 0.5; β={si round β; α=β-i     α-0.5, 0.5, where “round” is the usual rounding operation, s i has the index of the label closest to β, and α is the value of the symbolic translation.

The literature indicates several advantages in the computing with words approach in favor of the 2-tuple fuzzy linguistic representation method (Martínez et al., 2015; Rodríguez & Martínez, 2013). One of the most important is that the linguistic domain can be treated as continuous, whereas it is treated as discrete in classical models. The 2-tuple-based computational linguistic model easily performs computing with words processes without loss of information; the results of the computing with words processes are constantly exposed in the initial domain expression; and the aggregation of multi-granular linguistic information is possible in an easy way.

On the other hand, the JLE approach arises in the context of evaluation processes. The participating experts have different levels of knowledge of the variable of interest, which justifies using different sets of linguistic terms, i.e., a multi-granular approach. In addition to the JLE approach, multi-granular approach methods based on the 2-tuple fuzzy linguistic model include the fusion approach to multi-granular linguistic information management (Herrera, Herrera-Viedma, & Martínez, 2000) and linguistic hierarchies (LH) (Herrera & Martínez, 2001b).

The JLE approach solves the limitation shown in the granularity of the basic set of linguistic terms proposed by the fusion approach in the unification phase, which would be larger than the other term sets; it also solves the disadvantages related to precision and domain of expression for the computed results.

Following the methodology proposed by Espinilla et al. (2011), the JLE approach is based on LH, which are understood as the union of all levels, i.e. t: JL = U t l(t,n(t)), where each level t of LH corresponds to the set of linguistic terms with an uncertainty granularity of n(t) denoted as: Snt=s0nt, , snt-1nt. However, the JLE approach includes several aspects that make it different and more efficient:

  1. It defines the set of previous nodal points of level t such as FPt=fpt0, , fpti, , fpt2δt, where each previous nodal point fpti0, 1 is located at fpti=i2δt0,1, where δt=nt-1N.

  2. It replaces the two basic rules of the LH approach by forcing to keep the previous nodal points from one level t to the next, t + 1. According to Espinilla et al. (2011), the extended hierarchical rules are: (a) to build a JLE with a finite number of levels l(t,n(t)) with t = 1,…, m that defines the multigranular F MS structure required by the experts to express their knowledge (it is necessary to maintain the previous nodal points between them); and b) to have a JLE, where a new level l(t*,n(t*)) with t* = m + 1 must be added to keep all nodal points of all previous levels l(t,n(t)), t = 1,…, m within this new level.

  3. To build a JLE, the m linguistic scales are given to the experts to express their information. Then the term set l(t*,n(t*)) with t* = m + 1 will be aggregated according to the following theorem (Espinilla et al., 2011): Let {Sn1, , Snm} be the set of m linguistic term sets, where the granularity n(t) with t = 1, …,m is a odd value. A new linguistic term set Sn(t*) with t*=m+1, which keeps all previous nodal points of the m term sets can have the following granularity: nt*=t=1t=mδt+1,where δt=nt-1N.

  4. It proposes an optimised structure minimising the granularity of t*, which can keep all the above nodal points, using the least common multiple (LCM) as follows: nt*=MCMδ1,, δm+1,  t=1, ,m.

  5. Within the unification phase, the JLE approach uses the transformation functions defined in the LH approach, TFt´t, i.e. TFt´tsint, αnt=-1(sint,αnt)(nt´-1nt-1, where t and can be any pair of sets of terms in the LH. Then the JLE approach unifies the information at level t*, which holds all nodal points using the transformation function TFt*t, where t is any level in {1…, m} and t* = m + 1. Using this process, a new transformation function is developed between any pair of term sets, t and t', in the JLE without loss of information. Thus, assuming t and as any part of term sets in the JLE and t* as level l(tm+1, n(tm+1)) in the JLE, the new extended transformation function ETFt´t is defined as: ETFt´t:lt, ntlt´, nt´; ETFt´t=TFt*t o TFt´t*,where TFt*t and TFt´t*are the transformation functions defined in the same way as in LH.

  6. Because the transformation is unified by means of 2-tuple linguistic values, the computational phase is executed using the 2-tuple linguistic representation model. The results obtained are expressed by means of 2-tuple linguistic values in a unified Snt´; however, they can also be expressed (translated) in one of the JLE scales without loss of information.

Framework

In this step, the structure of the problem, preferences, and uncertainty is established. The components are the criteria C=c1, , cn that qualify the indicators I={i1, ..., in}. The set of participating experts who will express their ratings on each indicator criterion, E=e1,,  en. The granularity structure; and the semantics of the established granularity components.

The criteria assessed are those used by CONEVAL (2014):

Clarity (c1). It refers to whether there are doubts about what is intended to be measured, whether the indicator has any ambiguous terms or technical aspects that could be interpreted differently.

Relevance (c2). It should be verified that the most important elements of the indicator are directly related to some fundamental aspect of the objective (relevant factors).

Monitoring (c3). The clarity of the means of verification and the calculation method are analyzed to determine whether the indicator can be subject to independent verification.

Adequacy (c4). It refers to whether the indicator provides a sufficient basis for making a judgment about the program’s performance and whether the information that the indicator provides is relevant and appropriate to describe the program’s achievements over a period.

Experts: Regarding the multi-granular nature of the assessment, the participation of six experts grouped in two sets is considered: forest administrative sector, E1={e1,e2,e3}, and forest academic sector E1={e4,e5,e6}. Although the experts' sample is small, it can be considered acceptable given that the selected participants are of vast and recognized expertise in their respective sectors.

Granularity structure. Given the participation of two groups of experts with different levels of knowledge, a linguistic hierarchy composed of two linguistic term sets with granularity of five and seven terms is used. The group of experts from the forestry administrative sector expresses its assessment of the linguistic variable compliance in S 5 , and the group of experts from the academic sector in S 7 ; i.e., E1=S5={S05,  S15, S25,  S35, S45} corresponding to the linguistic term set {very low, low, moderate, high, very high} and E2=S7={S07,  S17, S27,  S37,  S47,  S57,  S67} corresponding to the linguistic term set {null, very low, low, low, moderate, high, very high, excellent}.

Semantics. The linguistic terms were defined by means of a triangular membership function µ A (u), which is represented by a 3-tuple (a, b, c) where b indicates the point at which the membership value is equal to 1, and a and c indicate the left and right boundaries, respectively, of the domain of the membership function, where, μA~u0 if ua;  u-ab-a if ua. b, c-uc-b sif ub, c;0 if uc. 

Thus, we have finite, ordered sets of linguistic terms with an odd cardinality (g + 1), where each term is equally informative. The mean linguistic term is the intermediate term and represents an approximate rating of 0.5 (Figure 3).

Figure 3 The semantics of linguistic term sets of linguistic hierarchies with granularity of five (S5) and seven (S7) terms. 

Once all the ratings are obtained, and making use of the two extended rules of the JLE approach, the new set (level) l(t*, n(t*)) with t* = m + 1 is added to the linguistic hierarchy, that is: n(t*,n(t*)) = n(t 3 ,n(t 3 )), where the granularity of (n(t 3 )) is defined by applying the theorem 1 nt3=t=1t=2δt+1,and optimization by nt3=LCMδ1, δ2+1; n(t 3) = LCM (2, 6) + 1 = 12 + 1 = 13; i.e., the set of terms added to the JLE is S 13 (Figure 4).

Figure 4 Linguistic term set aggregated to the extended linguistic hierarchy l(t * , n(t * )) = S 13

Assuming that, within each group, the experts have the same importance in the decision process, the aggregation operator used is the 2-tuple arithmetic mean defined as x-=i=1n-1si,αin.

The assessments were collected using designed formats (questionnaires of five [Appendix 1] and seven linguistic terms [Appendix 2]) and each respondent e i was provided with all relevant information: 1) objective, 2) name of the indicator, 3) description of the indicator, 4) method of calculation, 4) sources of information and 5) definition of the criteria.

All calculations were performed using the transformation equations defined in the resolution method, using the FLINTSTONES software (Estrella, Espinilla, Herrera, & Martínez, 2014). A decision support system developed within the Intelligent Systems Based on Fuzzy Decision Analysis (SINBAD) research group at the University of Jaén, Spain. The acronym FLINTSTONES stands for Fuzzy LINguisTic deciSion TOols eNhacemEnt Suite. The program was designed to solve decision-making problems under uncertainty, following a computing with words approach, which allows obtaining, starting from linguistic premises, results also represented linguistically, which facilitates interpretation of the results. Therefore, through FLINTSTONES, it is possible to model decision-making problems of any nature, specifying experts involved, alternatives or possible solutions to the problem, and evaluating those alternatives. Furthermore, the tool allows the definition of domains of expression of different nature that experts can use to elicit their opinions; therefore, they can be modelled by numerical or linguistic values. Once the problem has been defined, FLINTSTONES includes decision models widely used in decision-making literature that allow to obtain the solution. In this study, the 2-tuple linguistic fuzzy model was selected under a complex multigranularity uncertainty framework. FLINTSTONES is available for download at https://sinbad2.ujaen.es/flintstones/eshttp://sinbad2.ujaen.es/es

Analysis

The information collected is analysed and aggregated according to the objectives and constraints. The results are reported for consideration in the selection phase.

Selection or prioritization

Based on the analysis phase results, a selection process is developed in which decision-makers can choose the alternatives as solution to the problem.

Results

The ratings expressed by the group of experts from the official administrative sector are presented in Table 1. Table 2 shows the same information, but the ratings correspond to the group of experts from the academic sector and are expressed in the set of seven linguistic terms (S 7 ).

Table 1 Ratings expressed by the experts from the official administrative sector, provided in the linguistic term set S 5 , for assessing the criteria of indicators of the National Forest Program 2012-2018. 

Indicator Criteria
Expert 1 Expert 2 Expert 3
C1 C2 C3 C4 C1 C2 C3 C4 C1 C2 C3 C4
i1 (s4 5) (s3 5) (s3 5) (s3 5) (s3 5) (s4 5) (s4 5) (s3 5) (s4 5) (s4 5) (s4 5) (s3 5)
i2 (s0 5) (s3 5) (s3 5) (s3 5) (s2 5) (s4 5) (s4 5) (s3 5) (s2 5) (s3 5) (s4 5) (s3 5)
i3 (s0 5) (s2 5) (s3 5) (s3 5) (s2 5) (s3 5) (s3 5) (s3 5) (s4 5) (s4 5) (s4 5) (s3 5)
i4 (s3 5) (s2 5) (s3 5) (s3 5) (s2 5) (s3 5) (s3 5) (s3 5) (s2 5) (s3 5) (s4 5) (s3 5)
i5 (s3 5) (s2 5) (s3 5) (s3 5) (s3 5) (s4 5) (s4 5) (s3 5) (s1 5) (s2 5) (s2 5) (s3 5)
i6 (s3 5) (s2 5) (s3 5) (s3 5) (s3 5) (s3 5) (s3 5) (s3 5) (s4 5) (s4 5) (s3 5) (s3 5)
i7 (s3 5) (s2 5) (s3 5) (s3 5) (s3 5) (s4 5) (s4 5) (s3 5) (s3 5) (s3 5) (s4 5) (s3 5)
i8 (s3 5) (s2 5) (s3 5) (s3 5) (s2 5) (s2 5) (s2 5) (s3 5) (s2 5) (s1 5) (s3 5) (s3 5)
i9 (s3 5) (s2 5) (s3 5) (s3 5) (s2 5) (s3 5) (s3 5) (s3 5) (s3 5) (s4 5) (s3 5) (s3 5)
i10 (s2 5) (s1 5) (s2 5) (s2 5) (s2 5) (s2 5) (s2 5) (s2 5) (s2 5) (s3 5) (s2 5) (s3 5)
i11 (s2 5) (s1 5) (s2 5) (s2 5) (s2 5) (s2 5) (s2 5) (s2 5) (s2 5) (s1 5) (s2 5) (s3 5)
i12 (s3 5) (s2 5) (s3 5) (s3 5) (s3 5) (s3 5) (s4 5) (s4 5) (s1 5) (s1 5) (s2 5) (s3 5)
i13 (s3 5) (s2 5) (s3 5) (s3 5) (s1 5) (s2 5) (s2 5) (s1 5) (s3 5) (s1 5) (s3 5) (s3 5)

The indicators correspond to those shown in Figure 2. S5=S05,  S15,  S25,  S35, S45 correspond to the set of linguistic terms {very low, low, moderate, high, very high}. Criteria: c1 = clarity, c2 = relevance, c3 = monitoring and c4 = adequacy.

Table 2 Ratings expressed by experts from the academic sector, provided in the linguistic term set S 7 , evaluate the criteria of indicators of the National Forest Program 2012-2018. 

Indicator Criteria
Expert 1 Expert 2 Expert 3
C1 C2 C3 C4 C1 C2 C3 C4 C1 C2 C3 C4
i1 (s3 7) (s4 7) (s3 7) (s4 7) (s6 7) (s5 7) (s5 7) (s4 7) (s6 7) (s6 7) (s6 7) (s6 7)
i2 (s3 7) (s4 7) (s3 7) (s2 7) (s6 7) (s6 7) (s5 7) (s4 7) (s5 7) (s6 7) (s4 7) (s6 7)
i3 (s2 7) (s4 7) (s2 7) (s4 7) (s6 7) (s5 7) (s6 7) (s5 7) (s4 7) (s6 7) (s5 7) (s6 7)
i4 (s3 7) (s4 7) (s2 7) (s4 7) (s3 7) (s6 7) (s6 7) (s4 7) (s5 7) (s5 7) (s6 7) (s6 7)
i5 (s4 7) (s4 7) (s2 7) (s4 7) (s6 7) (s6 7) (s6 7) (s3 7) (s5 7) (s5 7) (s6 7) (s6 7)
i6 (s2 7) (s3 7) (s3 7) (s3 7) (s4 7) (s4 7) (s5 7) (s3 7) (s5 7) (s5 7) (s6 7) (s5 7)
i7 (s4 7) (s3 7) (s2 7) (s2 7) (s6 7) (s6 7) (s4 7) (s3 7) (s4 7) (s6 7) (s3 7) (s5 7)
i8 (s2 7) (s2 7) (s3 7) (s2 7) (s6 7) (s5 7) (s2 7) (s2 7) (s5 7) (s6 7) (s3 7) (s5 7)
i9 (s2 7) (s4 7) (s2 7) (s4 7) (s6 7) (s6 7) (s6 7) (s6 7) (s5 7) (s5 7) (s4 7) (s4 7)
i10 (s2 7) (s3 7) (s1 7) (s3 7) (s5 7) (s5 7) (s5 7) (s5 7) (s3 7) (s4 7) (s4 7) (s4 7)
i11 (s2 7) (s3 7) (s2 7) (s3 7) (s4 7) (s5 7) (s5 7) (s5 7) (s3 7) (s4 7) (s3 7) (s4 7)
i12 (s2 7) (s2 7) (s2 7) (s3 7) (s6 7) (s6 7) (s5 7) (s2 7) (s4 7) (s5 7) (s3 7) (s4 7)
i13 (s4 7) (s4 7) (s4 7) (s4 7) (s6 7) (s6 7) (s6 7) (s6 7) (s5 7) (s4 7) (s6 7) (s4 7)

The indicators correspond to those shown in Figure 2. S7={S07,  S17, S27,  S37,  S47,  S57,  S67} correspond to the set of linguistic terms {null, very low, low, moderate, high, very high, excellent}. Criteria: c1 = clarity, c2 = relevance, c3 = monitoring and c4 = adequacy.

Following the JLE approach, the values expressed by the experts in the two linguistic term sets (S 5 and S 7) were unified (transferred) to the linguistic term set added to the linguistic hierarchy (S 13). Table 3 shows the transformation of the results for the academic experts. The same procedure was used for the ratings of the experts from the forest administrative sector.

Table 3 Values expressed by experts from the forestry academic sector, transferred to the aggregated linguistic term set S 13 and represented by 2-tuple values for the assessment of the criteria of indicators of the National Forest Program 2012-2018. 

Indicator Criteria
Expert 4 Expert 5 Expert 6
C1 C2 C3 C4 C1 C2 C3 C4 C1 C2 C3 C4
i1 (s6 13,0) (s8 13,0) (s6 13,0) (s8 13,0) (s12 13,0) (s12 13,0) (s10 13,0) (s8 13,0) (s12 13,0) (s12 13,0) (s12 13,0) (s12 13,0)
i2 (s6 13,0) (s8 13,0) (s6 13,0) (s4 13,0) (s12 13,0) (s12 13,0) (s10 13,0) (s8 13,0) (s10 13,0) (s12 13,0) (s8 13,0) (s12 13,0)
i3 (s4 13,0) (s8 13,0) (s4 13,0) (s8 13,0) (s12 13,0) (s10 13,0) (s12 13,0) (s10 13,0) (s8 13,0) (s12 13,0) (s10 13,0) (s12 13,0)
i4 (s6 13,0) (s8 13,0) (s4 13,0) (s8 13,0) (s6 13,0) (s12 13,0) (s12 13,0) (s8 13,0) (s10 13,0) (s10 13,0) (s12 13,0) (s12 13,0)
i5 (s8 13,0) (s8 13,0) (s4 13,0) (s8 13,0) (s12 13,0) (s12 13,0) (s12 13,0) (s6 13,0) (s10 13,0) (s10 13,0) (s10 13,0) (s12 13,0)
i6 (s4 13,0) (s8 13,0) (s6 13,0) (s6 13,0) (s8 13,0) (s8 13,0) (s10 13,0) (s6 13,0) (s10 13,0) (s10 13,0) (s10 13,0) (s10 13,0)
i7 (s8 13,0) (s6 13,0) (s4 13,0) (s4 13,0) (s12 13,0) (s12 13,0) (s8 13,0) (s6 13,0) (s8 13,0) (s12 13,0) (s6 13,0) (s10 13,0)
i8 (s4 13,0) (s4 13,0) (s6 13,0) (s4 13,0) (s12 13,0) (s10 13,0) (s4 13,0) (s4 13,0) (s10 13,0) (s12 13,0) (s6 13,0) (s10 13,0)
i9 (s4 13,0) (s8 13,0) (s4 13,0) (s8 13,0) (s12 13,0) (s12 13,0) (s12 13,0) (s12 13,0) (s10 13,0) (s10 13,0) (s8 13,0) (s8 13,0)
i10 (s4 13,0) (s6 13,0) (s2 13,0) (s6 13,0) (s10 13,0) (s10 13,0) (s10 13,0) (s10 13,0) (s6 13,0) (s8 13,0) (s8 13,0) (s8 13,0)
i11 (s4 13,0) (s6 13,0) (s4 13,0) (s6 13,0) (s8 13,0) (s10 13,0) (s10 13,0) (s10 13,0) (s6 13,0) (s8 13,0) (s6 13,0) (s8 13,0)
i12 (s4 13,0) (s4 13,0) (s4 13,0) (s6 13,0) (s12 13,0) (s12 13,0) (s10 13,0) (s4 13,0) (s8 13,0) (s10 13,0) (s6 13,0) (s8 13,0)
i13 (s8 13,0) (s6 13,0) (s8 13,0) (s8 13,0) (s12 13,0) (s12 13,0) (s12 13,0) (s12 13,0) (s10 13,0) (s8 13,0) (s12 13,0) (s8 13,0)

The indicators correspond to those shown in Figure 2. Criteria: c1 = clarity, c2 = relevance, c3 = monitoring and c4 = adequacy).

As the collective ratings were calculated using the 2-tuple fuzzy linguistic model, they were expressed in the aggregated linguistic term set S 13, including the ranking order of indicators according to the experts' ratings (Table 4).

Table 4 Collective assessments expressed in the linguistic term set S 13 for evaluating the criteria of indicators of the National Forest Program 2012-2018. 

Indicator Criteria
Expert 1 Expert 2 Expert 3
C1 C2 C3 C4 C1 C2 C3 C4 C1 C2 C3 C4
i1 (s4 5) (s3 5) (s3 5) (s3 5) (s3 5) (s4 5) (s4 5) (s3 5) (s4 5) (s4 5) (s4 5) (s3 5)
i2 (s0 5) (s3 5) (s3 5) (s3 5) (s2 5) (s4 5) (s4 5) (s3 5) (s2 5) (s3 5) (s4 5) (s3 5)
i3 (s0 5) (s2 5) (s3 5) (s3 5) (s2 5) (s3 5) (s3 5) (s3 5) (s4 5) (s4 5) (s4 5) (s3 5)
i4 (s3 5) (s2 5) (s3 5) (s3 5) (s2 5) (s3 5) (s3 5) (s3 5) (s2 5) (s3 5) (s4 5) (s3 5)
i5 (s3 5) (s2 5) (s3 5) (s3 5) (s3 5) (s4 5) (s4 5) (s3 5) (s1 5) (s2 5) (s2 5) (s3 5)
i6 (s3 5) (s2 5) (s3 5) (s3 5) (s3 5) (s3 5) (s3 5) (s3 5) (s4 5) (s4 5) (s3 5) (s3 5)
i7 (s3 5) (s2 5) (s3 5) (s3 5) (s3 5) (s4 5) (s4 5) (s3 5) (s3 5) (s3 5) (s4 5) (s3 5)
i8 (s3 5) (s2 5) (s3 5) (s3 5) (s2 5) (s2 5) (s2 5) (s3 5) (s2 5) (s1 5) (s3 5) (s3 5)
i9 (s3 5) (s2 5) (s3 5) (s3 5) (s2 5) (s3 5) (s3 5) (s3 5) (s3 5) (s4 5) (s3 5) (s3 5)
i10 (s2 5) (s1 5) (s2 5) (s2 5) (s2 5) (s2 5) (s2 5) (s2 5) (s2 5) (s3 5) (s2 5) (s3 5)
i11 (s2 5) (s1 5) (s2 5) (s2 5) (s2 5) (s2 5) (s2 5) (s2 5) (s2 5) (s1 5) (s2 5) (s3 5)
i12 (s3 5) (s2 5) (s3 5) (s3 5) (s3 5) (s3 5) (s4 5) (s4 5) (s1 5) (s1 5) (s2 5) (s3 5)
i13 (s3 5) (s2 5) (s3 5) (s3 5) (s1 5) (s2 5) (s2 5) (s1 5) (s3 5) (s1 5) (s3 5) (s3 5)

Finally, the collective values were retranslated into one of the two linguistic term sets used (Table 5); in this case, the linguistic term set used was S 7. As can be seen, this process of retranslation did not change the ranking order of indicators and it was necessary because usually the set t * added to the linguistic hierarchy corresponds to a high degree of granularity, which makes it difficult to interpret. The expression of the values is more interpretable because linguistic terms are closer to the usual rating scales and experts get results represented in any of the linguistic term sets used.

Table 5 Collective assessments expressed in the linguistic term set S 7, for the evaluation of the criteria of indicators of the National Forest Program 2012-2018. 

Indicator Name Classification Collective assessment
i1 Rate of change of timber wood production 1 (very high, 0.042)
i9 Percentage of ejidos and communities changing to a higher typology of producers by increasing organizational capacities. 2 (high, 0.438)
i3 Rate of change of certified area under good forest management practices 3 (high, 0.417)
i5 Percentage of coverage of reinstated or restored 4 (high, 0.396)
i4 Rate of change in area conserved via payments for environmental services 5 (high, 0.375)
i2 Percentage of value of production derived from sustainable harvesting of natural resources 5 (high, 0.375)
i7 Rate of change in the average annual area of adult and regrowth trees affected by forest fires 6 (high, 0.313)
i6 Annual net deforestation rate of forests and rainforests 7 (high, 0.270)
i13 Rate of change of financial resources granted to the forestry sector by the development bank 8 (high, 0.167)
i12 Avoided CO2 emissions by reduction of deforestation and forest degradation 9 (high, -0.104)
i8 Proportion of timber forest products belonging to the legal market 10 (high, -0.333)
i10 Index of social participation in forestry sector 11 (moderate, 0.333)
i11 Index of the National REDD+ Strategy in operation 12 (moderate, 0.223)

Even though the 2-tuple fuzzy linguistic model is widely supported by results obtained by researchers who have addressed and solved several theoretical and real problems (Carmona, González, Gacto, & del Jesus, 2012; Doukas, Tsiousi, Marinakis, & Psarras, 2014; Herrera-Viedma, López-Herrera, Luque, & Porcel, 2007; Montes, Sánchez, Villar, & Herrera, 2015), there are so far no known applications in the evaluation of public policy indicators that would allow us to contrast the results obtained here. However, there is confidence in the quality of tools used and the proper character of the structure of information gathered in the process of evaluating indicators; therefore, it can be said that, according to the linguistic term and value of the symbolic translation α estimated for each of the indicators, indicator i 1 “Rate of change of timber forest production” is the one that had the best evaluations from the experts with “very high” level of compliance in the criteria considered. After this, indicators i 1 to i 9, including indicators i 12 and i 13, had a “high” level of compliance with differences in the value of the symbolic translation which, in this case, determined the differences in the ranking order (Table 5). Only i 10 and i 11 had the collective rating corresponding to the linguistic term “moderate”.

Conclusiones

The structure defined in evaluating social policy indicators corresponds appropriately to that used with the 2-tuple fuzzy linguistic model, which is relevant because it allows an adequate evaluation of the indicators considered. Furthermore, the multi-granular approach considers assessments beyond the traditional binary values (yes, no). Through the participation of experts with different levels of knowledge, it enriches the experts’ assessments expressed with greater precision. CONEVAL and the World Bank represent valuable contributions to assessing indicators and evaluating aspects beyond the four criteria considered in this study; however, such aspects are also susceptible to being evaluated through the approach used here. In the future, it is intended to extend the study to the assessment of all qualitative aspects considered in the attributes of the indicators.

Acknowledgments

This study is partially funded by the Spanish Ministry of Economy and Competitiveness through the research project (PGC2018- 099402-B-I00) and the Ramón y Cajal postdoctoral fellowship(RYC- 2017-21978). Moreover, funding was also received from the National Council of Science and Technology (CONACyT-Mexico) through the sabbatical stay 2018-2019 with CVU reference no. 64236.

References

Banco Mundial. (2016). Evaluación de la calidad de indicadores de proyectos prioritarios. Retrieved from https://www.hacienda.morelos.gob.mx/images/docu_planeacion/evaluacion/EvaluacionesBancoMundial/Herramienta_para_Evaluar_la_Calidad_de_los_Indicadores.pdfLinks ]

Carmona, C. J., González, P., Gacto, M. J., & del Jesus, M. J. (2012). Genetic lateral tuning for subgroup discovery with fuzzy rules using the algorithm NMEEF-SD. International Journal of Computational Intelligence Systems, 5(2), 355-367. doi: 10.1080/18756891.2012.685323 [ Links ]

Chenoweth, J. (2008). A re-assessment of indicators of national water scarcity. Water International, 33(1), 5-18. doi: 10.1080/02508060801927994 [ Links ]

Consejo Nacional de Evaluación de la Política Pública (CONEVAL). (2014). Metodología para la aprobación de indicadores de los programas sociales. Retrieved from https://www.coneval.org.mx/coordinacion/Documents/monitoreo/metodologia/Metodología para Aprobación de Indicadores 2014.pdfLinks ]

De la Cuesta, G. M., Pardo, H. E., & Paredes, G. J. D. (2015). Identificación de indicadores relevantes del desempeño RSE mediante la utilización de técnicas multicriterio. INNOVAR, 25(55), 75-88. doi: 10.15446/innovar.v25n55.47197 [ Links ]

Doukas, H., Tsiousi, A., Marinakis, V., & Psarras, J. (2014). Linguistic multi-criteria decision making for energy and environmental corporate policy. Information Sciences, 258, 328-338. doi: 10.1016/j.ins.2013.08.027 [ Links ]

Espinilla, M., Liu, J., & Martínez, L. (2011). An extended hierarchical linguistic model for decision-making problems. Computational Intelligence, 27(3), 489-512. doi: 10.1111/j.1467-8640.2011.00385.x [ Links ]

Estrella, F. J., Espinilla, M., Herrera, F., & Martínez, L. (2014). FLINTSTONES: A fuzzy linguistic decision tools enhancement suite based on the 2-tuple linguistic model and extensions. Information Sciences, 280, 152-170. doi: 10.1016/j.ins.2014.04.049 [ Links ]

Evans, A., Strezov, V., & Evans, T. J. (2009). Assessment of sustainability indicators for renewable energy technologies. Renewable and Sustainable Energy Reviews, 13(5), 1082-1088. doi: 10.1016/j.rser.2008.03.008 [ Links ]

Gothwal, S., & Raj, T. (2019). A comparative study of multi-criteria decision-making approaches for prioritising the manufacturing systems. International Journal of Process Management and Benchmarking, 9(3), 277-299. doi: 10.1504/IJPMB.2019.100962 [ Links ]

Guayanlema, V., Fernández, L., & Arias, K. (2017). Análisis de indicadores de desempeño energético del Ecuador. Enerlac, 1(2), 121-139. Retrieved from http://biblioteca.olade.org/opac-tmpl/Documentos/hm000684.pdfLinks ]

Guillen, A., Badii, M. H., Garza, F., & Acuña, M. (2015). Descripción y uso de indicadores de crecimiento económico. International Journal of Good Conscience, 10(1), 138-156. Retrieved from http://www.spentamexico.org/v10-n1/A10.10(1)138-156.pdfLinks ]

Herrera-Viedma, E., López-Herrera, A. G., Luque, M., & Porcel, C. (2007). A fuzzy linguistic IRS model based on a 2-tuple fuzzy linguistic approach. International Journal of Uncertainty, Fuzziness and Knowlege-Based Systems, 15(2), 225-250. doi: 10.1142/S0218488507004534 [ Links ]

Herrera, F., Herrera-Viedma, E., & Martínez, L. (2000). A fusion approach for managing multi-granularity linguistic term sets in decision making. Fuzzy Sets and Systems, 114(1), 43-58. doi: 10.1016/S0165-0114(98)00093-1 [ Links ]

Herrera, F., & Martínez, L. (2000). A 2-tuple fuzzy linguistic representation model for computing with words. IEEE Transactions on Fuzzy Systems, 8(6), 746-752. doi: 10.1109/91.890332 [ Links ]

Herrera, F., & Martínez, L. (2001a). The 2-tuple linguistic computational model. advantages of its linguistic consistency. International Journal of Uncertainty, Fuzziness and Knowledge-Based Systems, 9(1), 33-48. doi: 10.1142/S0218488501000971 [ Links ]

Herrera, F., & Martínez, L. (2001b). A model based on linguistic 2-tuples for dealing with multigranular hierarchical linguistic contexts in multi-expert decision-making. IEEE Transactions on Systems, Man, and Cybernetics, Part B: Cybernetics, 31(2), 227-234. doi: 10.1109/3477.915345 [ Links ]

Kühnen, M., & Hahn, R. (2017). Indicators in social life cycle assessment: a review of frameworks, theories, and empirical experience. Journal of Industrial Ecology, 21(6), 1547-1565. doi: 10.1111/jiec.12663 [ Links ]

Martínez, L., Rodríguez, R. M., & Herrera, F. (2015). The 2-tuple linguistic model. Computing with words in decision making. New York, USA: Springer. doi: 10.1007/978-3-319-24714-4 [ Links ]

Mendel, J. M., Zadeh, L. A., Trillas, E., Yager, R., Lawry, J., Hagras, H., & Guadarrama, S. (2010). What computing with words means to me: Discussion forum. IEEE Computational Intelligence Magazine, 5(1), 20-26. doi: 10.1109/MCI.2009.934561 [ Links ]

Montes, R., Sánchez, A. M., Villar, P., & Herrera, F. (2015). A web tool to support decision making in the housing market using hesitant fuzzy linguistic term sets. Applied Soft Computing Journal, 35, 949-957. doi: 10.1016/j.asoc.2015.01.030 [ Links ]

Montignac, F., Mousseau, V., Bouyssou, D., Aloulou, M. A., Rousval, B., & Damart, S. (2015). An MCDA approach for evaluating hydrogen storage systems for future vehicles. In R. Bisdorff, L. C. Dias, P. Meyer, V. Mousseau, & M. Pirlot (Eds.), Evaluation and decision models with multiple criteria (pp. 501-532). Switzerland: Springer. doi: 10.1007/978-3-662-46816-6 [ Links ]

Pei, Z., Ruan, D., Liu, J., & Xu, Y. (2009). Linguistic based intelligent information processing: Theory, mehtods, and applications. Amsterdam - Paris: Atlantis Press. [ Links ]

Pirlot, M., Teghem, J., Ulungu, D., Bulens, P., & Goffin, C. (2015). Choosing a cooling system for a power plant in Belgium. In R. Bisdorff , L. C. Dias , P. Meyer , V. Mousseau, & M. Pirlot (Eds.), Evaluation and decision models with multiple criteria (pp. 221-258). Switzerland: Springer . doi: 10.1007/978-3-662-46816-6 [ Links ]

Rodríguez, R. M., & Martínez, L. (2013). An analysis of symbolic linguistic computing models in decision making. International Journal of General Systems, 42(1), 121-136. doi: 10.1080/03081079.2012.710442 [ Links ]

Torres, A., & Tranchita, C. (2014). ¿Inferencia y razonamiento probabilístico o difuso? Revista de Ingeniería, 19, 158-166. Retrieved from https://ojsrevistaing.uniandes.edu.co/ojs/index.php/revista/article/view/450Links ]

Vignesh, S., Ali Elibaid, O. B., Mera, B., Arokiadoss, A. P., Muthukumar, K., Santhosh, M., & James, R. A. (2017). Assessment of pollution indicators and antibiotic resistant pattern on contaminated canned juice. In S. Vignesh & A. P. Arokiadoss (Eds.), Statistical approaches on multidisciplinary research (pp. 110-117). Surragh Publishers. doi: 10.5281/zenodo.262976 [ Links ]

Wang, C. N., Yang, C.-Y., & Cheng, H.-C. (2019). A Fuzzy Multicriteria Decision-Making (MCDM) model for sustainable supplier evaluation and selection based on triple bottom line approaches in the garment industry. Processes, 7(7), 1-13. doi: 10.3390/pr7070400 [ Links ]

Whitehead, J. (2017). Prioritizing sustainability indicators: Using materiality analysis to guide sustainability assessment and strategy. Bussiness Strategy and the Environment, 26(3), 399-412. doi: 10.1002/bse.1928 [ Links ]

Received: June 17, 2020; Accepted: March 11, 2021

*Corresponding author: rmrodrig@ujaen.es; tel.: +34 953212155.

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