Journal Pre-proof Supplier sustainability performance evaluation using the analytic network process Mihalis Giannakis, Rameshwar Dubey, Ilias Vlachos, Yanbing Ju PII:
S0959-6526(19)34309-4
DOI:
https://doi.org/10.1016/j.jclepro.2019.119439
Reference:
JCLP 119439
To appear in:
Journal of Cleaner Production
Received Date: 7 March 2019 Revised Date:
31 October 2019
Accepted Date: 23 November 2019
Please cite this article as: Giannakis M, Dubey R, Vlachos I, Ju Y, Supplier sustainability performance evaluation using the analytic network process, Journal of Cleaner Production (2019), doi: https:// doi.org/10.1016/j.jclepro.2019.119439. This is a PDF file of an article that has undergone enhancements after acceptance, such as the addition of a cover page and metadata, and formatting for readability, but it is not yet the definitive version of record. This version will undergo additional copyediting, typesetting and review before it is published in its final form, but we are providing this version to give early visibility of the article. Please note that, during the production process, errors may be discovered which could affect the content, and all legal disclaimers that apply to the journal pertain. © 2019 Published by Elsevier Ltd.
Supplier Sustainability Performance Evaluation using the Analytical Network Process Mihalis Giannakis1*, Rameshwar Dubey2 Ilias Vlachos3, Yanbing Ju4
1*
Audencia Business School, Nantes, France (corresponding author) Email:
[email protected] 2 Montpellier Business School, Montpellier, France Email:
[email protected] 3 La Rochelle Business School, La Rochelle, France Email:
[email protected] 4 Beijing Institute of Technology, Beijing, China Email:
[email protected]
Abstract We develop a sustainability performance measurement framework for supplier evaluation and selection, using the Analytic Network Process (ANP) method. Even though the literature is rife with studies that deal with the supplier selection problem, companies that actively pursue sustainability strategies may need to add metrics that show suppliers’ sustainability performance. Existing models for measuring sustainability performance are limited in that they either evaluate the environmental and social performance separately, do not consider the inter-relationships between metrics across the three dimensions of sustainability, or utilize metrics that are difficult to obtain and evaluate accurately. To overcome this deficiency, we use the ANP method, that takes into account the interrelations between quantifiable and easy to obtain sustainability-related evaluation metrics. First, through an extensive literature review and feedback from an experts’ panel, we select and classify salient sustainability performance metrics related to supplier evaluation. With data collected through an extensive survey amongst 144 supply chain professionals in the UK and France, we develop the interdependencies between several sustainability metrics and determine the most critical metrics by calculating their relative weights. Results show that the selected socio-economic metrics carry the most relatively important role in supplier selection. Based on the findings of the study, we discuss implications for theory and practice. The proposed evaluation system can provide details on observing sustainable supply chain performance. It can also help to get a clearer insight into sustainability with a well-established quantitative decision-making process so that business strategies can be developed with more concerns on supply chain sustainability.
Keywords: Sustainable Supplier Selection, Sustainability Performance, Analytical Network Process
Supplier Sustainability Performance Evaluation using the Analytic Network Process Abstract We develop a sustainability performance measurement framework for supplier evaluation and selection, using the Analytic Network Process (ANP) method. Even though the literature is rife with studies that deal with the supplier selection problem, companies that actively pursue sustainability strategies may need to add metrics that show suppliers’ sustainability performance. Existing models for measuring sustainability performance are limited in that they either evaluate the environmental and social performance separately, do not consider the inter-relationships between metrics across the three dimensions of sustainability, or utilize metrics that are difficult to obtain and evaluate accurately. To overcome this deficiency, we use the ANP method, that takes into account the interrelations between quantifiable and easy to obtain sustainability-related evaluation metrics. First, through an extensive literature review and feedback from an experts’ panel, we select and classify salient sustainability performance metrics related to supplier evaluation. With data collected through an extensive survey amongst 144 supply chain professionals in the UK and France, we develop the interdependencies between several sustainability metrics and determine the most critical metrics by calculating their relative weights. Results show that the selected socioeconomic metrics carry the most relatively important role in supplier selection. Based on the findings of the study, we discuss implications for theory and practice. The proposed evaluation system can provide details on observing sustainable supply chain performance. It can also help to get a clearer insight into sustainability with a well-established quantitative decision-making process so that business strategies can be developed with more concerns on supply chain sustainability.
Keywords: Sustainable Supplier Selection, Sustainability Performance, Analytical Network Process
1. Introduction Over the past decade, a large number of companies have adopted (or claim to have adopted) sustainable management strategies (Hou et al. 2019). A growing body of literature has been established that developed useful sustainability metrics and sustainable performance management frameworks (Hassini et al., 2012, Morioka et al., 2016; Baxter et al. 2018, Osiro et al. 2018). The majority of studies consider sustainable performance management using environmental, social, as well as economic/financial measures (see, for example, Ahi and Searcy, 2015, Kuo et al. 2015, Dubey et al. 2017, dos Santos et al., 2019, Pislaru et al.
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2019). Amongst the developed methods for measurement of sustainability in corporations, sectors and even nations, notable contributions include the Global Reporting Initiative (2015), the world business council for sustainable development (2015), the development of standards (OECD 2004) and the Dow Jones sustainability index (Searcy et al., 2012). Sustainability has been integrated into the corporate strategy of many organisations. Yet, one of the main challenges is to develop models to guide decisions towards achieving the sustainability goals as they were originally defined by the Brundtland Commission report,that emphasizes the interrelationships among society, the environment, and economic development. In this direction, as organisations are increasingly dependent upon the performance of their suppliers, it is imperative for companies to monitor and evaluate not only the sustainable performance of their operations but also to extend this evaluation to their suppliers and other stakeholders. Therefore, problems such as the selection of sustainable suppliers (defined as suppliers with good sustainability performance) (Haeri and Rezaei, 2019), or the investment of a venture capital fund on a business based on its perceived sustainable performance, are of paramount importance for organisations in their pursuit of sustainable performance (Bai and Sarkis, 2010, Rashidi and Cullinane, 2019). The selection of sustainable suppliers constitutes one of the most important supply chain decisions towards a company’s sustainable performance (Chen et al., 2006, Chai et al. 2013), as the suppliers’ performance is directly correlated with vendors’ performance. For example, the Rana Plaza disaster in Bangladesh in 2013, which involved perilous working conditions at a garment supplier that lead to the death of more than 1100 people, tarnished the reputation of a large number of companies in the fashion industry Ehrgott et al. (2011). It turned out that the due diligence and supplier selection processes for the majority of vendors from that supplier were inadequate. As a result, the apparel companies were obliged to sign a legislation to be held accountable for monitoring their Bangladeshi suppliers (Jacobs and Singhal, 2017). There is a plethora of studies that deal with the supplier selection problem. A broad spectrum of different methods and techniques have been applied. They include multi-attribute decision analysis methods such as data envelopment analysis, total cost of ownership (Bhutta and Huq, 2002) weighted linear model approaches and weighted sum models, linear and goal programming models, case-based reasoning,
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clustering methods, human judgment models, or statistical analysis (de Boer et al., 2001; Ho et al., 2010). However, companies that actively incorporate sustainability into their strategy may need to add to their selection criteria, metrics that show suppliers’ sustainability performance (Govindan et al., 2015). The existing models for measuring sustainability performance are limited in that they focus on evaluating the environmental and social performance separately and do not consider the inter-relationships between different sustainability performance metrics (Singh et al., 2009, Bai and Sarkis 2010, Hassini et al, 2012) and more importantly the relative prioritization of these metrics (Luthra et al., 2017). For example, in the case where a global supplier has a low carbon footprint, but at the same its performance in terms of the working conditions for its employees or the tax contributions to the local economy is poor, it is essential to consider the vendor’s priorities in each of these dimensions and then determine a score for the overall sustainable performance of the supplier (Price and Sun, 2017). Similarly, a precise method for evaluating the sustainability performance based on prioritization of sustainability metrics is useful in the case where a supplier may have the process of ensuring financial transparency and providing value to local communities, but at the same time having an opaque relationship with regional governments which may undermine competition. Which of the sustainability indicators are more important for vendors, so that they can identify the best supplier based on their corporate strategy and vision for sustainability? In light of these observations, we set out two objectives: (1) To identify and select appropriate evaluation criteria for sustainable supplier selection, and (2) To develop a sustainability performance evaluation framework for sustainable supplier selection As the sustainability-related performance dimensions may be closely correlated, decision-makers would benefit from a method which: (i) guides them in selecting the most appropriate performance indicators by identifying which attributes of suppliers’ performance they need (or not need) to utilize, and (ii) assesses the perceived importance of each performance indicator so that the strategic objectives of the firm can be achieved (Ho et al., 2010). The paper proceeds as follows. In the 2nd section, we review pertinent literature on sustainable supplier evaluation and selection with a particular focus on the use of MCDM methods. We also discuss the ANP method and justify its usefulness in the sustainable supplier evaluation and problem. In the 3rd section, we present our proposed method for the development of a sustainability multi-criteria framework for supplier
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selection. Through a comprehensive literature review on the use of sustainability metrics, we provide the foundations for the selection of appropriate sustainability-related indicators. We also present the data collection process for the empirical research to operationalise and validate our proposed approach. In the 4th section, we present the findings of the study, and in the final 5th section we conclude our paper with a discussion of the main contributions of the study, its limitations and an agenda for future research.
2. Literature Review Sustainable supply chain management can be defined as “the management of material, information and capital flows as well as cooperation among companies along the supply chain while taking goals from all three dimensions of sustainable development, i.e., economic, environmental and social, into account which are derived from customer and stakeholder requirements” (Seuring and Müller, 2008). It involves managerial decisions across several areas towards achieving sustainability, such as changing the organisational culture, improving transparency and effective supply chain risk management (Carter and Rogers, 2008). We use these definitions as a precursor An indispensable part of sustainable supply chain management is the selection of sustainable suppliers and the evaluation of their performance (Luthra et al., 2017). There is a growing literature on the selection of sustainable suppliers that incorporate factors related to the triple bottom line effect of sustainability (Govindan et al., 2013; Govindan et al., 2015). Although economic and environmental performance have long existed as parameters in the sustainable supplier selection process, the systematic consideration of social and ethical outlook of companies has been developed recently, including issues such as child labor, human right abuses, and corruption indexes (Awasthi et al., 2018). The sustainable supplier selection problem can be considered as a multiple-criteria decision-making (MCDM) process. The MCDM discipline is very useful for disentangling the decision-making processes of complex issues but also enables decision-makers to take into account and balance the trade-offs amongst a wide range of criteria that can affect a decision (Saaty, 1996; Chai et al., 2013). This is particularly evident in the selection of sustainable suppliers where the tradeoffs between economic and either social or environmental issues are prevalent. Several MCDM evaluation methods have been applied, with Analytic Hierarchy Process, Analytic Network Process and fuzzy-based approaches dominating the literature (Zimmer et al., 2016). Among the
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first researchers that incorporated sustainability into the supplier selection problem are Lu et al. (2007) who explored environmental principles applicable to green supplier evaluation by using a multiobjective decision analysis, Bai and Sarkis (2010) who used a grey system and rough set theory to develop a sustainability framework for their supplier selection process and Buyukozkan and Çifçi (2011) who used a fuzzy multi-criteria decision framework for sustainable supplier selection with incomplete information. In Table 1 we provide a short list of well-cited studies over the past 10 years related to sustainable supplier selection that use MDCM methods to illustrate the growing interest in the topic. As sustainability is becoming a central strategic objective for many companies, the proposed MCDM models are becoming more elaborate and focused on specific sustainability and operational related issues. For example, the ANP/AHP methods have been combined with rough set and fuzzy set theories or with several MCDM methods. Chen et al. (2019) use a rough-fuzzy DEMATEL-ANP method for evaluating sustainable requirements. Notable recent studies in this domain are also the work the work of Parkouhi et al. (2019) who use Grey DEMATEL technique to examine the importance of the criteria used for supplier selection, and the work Bai et al. (2019) who use a group decision support approach to select suppliers using social sustainable criteria. Table 1: Summary of literature on the use of MDCM for sustainable supplier evaluation and selection Authors Method Topic / relevance to this study A green supplier selection model that considers the vagueness Lee et al. (2009) Fuzzy extended AHP of experts’ opinions in evaluating criteria. Fuzzy entropy and fuzzy A sustainability performance model that utilizes an alert Erol et al. (2011) multi-attribute utility management system. Amindoust et al. A mathematical sustainable supplier ranking model that Fuzzy Inference System (2012) considers the subjectivity of decision-makers’ perceptions A sustainability performance measurement tool that uses Govindan et al. Fuzzy TOPSIS triangular fuzzy numbers to express linguistic values of experts' (2013) subjective preferences. A model that rates green suppliers and allocates optimum order Kannan et al. (2013) Fuzzy AHP / MOLP quantities based on various constraints. Fuzzy AHP / multi-objective A mathematical model that allocates the optimal quantities of Azadina et al. (2015) mathematical programming orders to suppliers considering lot-sizing problems. Govindan et al. A systematic literature review to identify the most prevalent Literature review (2015) techniques and topics for green supplier evaluation. ANP / Grey Relational A green supplier selection model that enables decision-makers Hashemi et al. (2015) Analysis to use linguistic evaluation. A model to rank and select suppliers using specific selection Bayesian framework / Monte Sarkis et al. (2015) Carlo Markov chain simulation objectives, appropriate for small or missing data sets. A framework for evaluating sustainable supplier selection using Luthra. et al. (2017) AHP / VIKOR 22 evaluation criteria. Haeri & Rezaei “Best-worst” / fuzzy grey A weight assignment model for green supplier selection. (2019) cognitive maps
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Kellner & Utz (2019) Markowitz portfolio theory Li et al. (2019)
Rough cloud TOPSIS
A method for supplier selection that takes into account the trade-offs between the supplier sustainability, the purchasing costs, and the overall supply risk. A method to weigh sustainable supply chain management practices under conditions of decision method uncertainty.
2.1 The ANP method In our pursuit for a sustainability evaluation framework for supplier selection, we utilize the ANP method to identify the relative importance and prioritization of specific sustainability metrics, which can assist the decision of sustainable suppliers. The ANP is a generalization of the AHP method and is useful in solving complex decision-making problems (Saaty and Vargas, 2004). Our choice is primarily grounded in the fact that the ANP method can deal with complex multi-criteria issues and can generate evidence of interrelationships and dependencies among several performance metrics and therefore, determine a more accurate ranking of each metric (Saaty, 1996). The ANP method has been combined with fuzzy or rough sets models and/or with other MCDM methods such as TOPSIS. However, the main limitation of TOPSIS is that it assumes that all the criteria are independent (Aguaron-Joven et al., 2015), which is not always the case in sustainability. Saaty and Tran (2007) posit that good judgement produces valid answers in AHP, and fuzzy AHP simply produces perturbation without producing any better outcomes. If the pairwise comparison is consistent, then fuzzy AHP would yield similar priority vectors as the classical AHP (Csutora and Buckley, 2011). Similarly, fuzzy set theory and its application in combination with MCDM methods is appropriate when dealing with the uncertainty of measurement of qualitative evaluation metrics (Ferrero and Salicone, 2004; Lun and Leng, 2007; Rahmanita et al., 2018). The majority of existing studies that deal with the sustainable supplier selection problem utilise metrics that cover the triple bottom line of sustainability. However, a critical limitation is that they use evaluation criteria that are either generic, difficult to quantify and entail a certain level of ambiguity. For example, despite the usefulness of such criteria such as the presence of “environmental management systems” (Govindan et al., 2015), “environmental costs” (Luthra et al., 2019), or “fight for fair-trading” (Li et al., 2019), their evaluation is not easy and requires subjective measures. In our study, we select metrics that can be obtained accurately and are easily quantifiable, as most of them are in the form of ratios. Therefore,
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the use of a method that combines the ANP method with fuzzy or rough set theories would not add substantial benefits to our model. Saaty and Vargas (2006) outline four steps for the utilization of the ANP method. Step 1 - Define the problem and construct the network model in a logical way including appropriate and parsimonious criteria: Unlike the AHP method where the problem is structured as a hierarchy, in ANP, the problem is structured in the form of a network, that consists of decision clusters and elements which are connected through network links. The links represent the inter-dependencies amongst the clusters and the elements (Saaty, 2004). The network is built by considering all potential inter-dependencies amongst the elements of the system. The inter-dependencies among elements can be in the form of outer dependencies (when an element or elements in a cluster have a dependency with an element or elements in other clusters), or inner dependencies (when an element or elements in the same cluster have an influence on each other) (Saaty, 2004). The objective of the decision (in our case the selection of sustainable suppliers) is defined as the goal of the hierarchy of the selected criteria (the sustainability metrics). Step 2 - Conduct pairwise comparisons of the clusters and elements and obtain priority vectors: For a given set of sustainability metrics, the ANP method conducts pairwise comparisons for each combination of pairs of these metrics and attempts to identify how much more does a metric (of a single pair of metrics) influence the decision for selecting a supplier than the other metric of the pair, to finally rank the alternatives in the selection of the supplier (Saaty and Vargas, 2006). During this step, the potential decision-makers are asked to evaluate the relative importance clusters and elements. For every pairwise comparison matrix, the consistency index and ratio should be calculated to check for the consistency of the matrix. The concept of consistency is that if metric a is more important than is metric b, and metric b is more important than is metric c, then metric a must be more important than metric c. The consistency ratio (C.R.) can be calculated by the formula
Consistenc y Ratio =
λ
Consistenc y Index Random Consistenc y Index
−n
max and the consistency index (C.I) as follows C.I. = n − 1 , with n representing the number of criteria. The
random consistency index (R.I) as proposed by Saaty and Vargas (2007). For n=12 elements the RI=1.48. If C.R≤0.1, the pairwise comparison matrix is consistent. The pairwise comparisons are conducted using the following ranking scale (Saaty, 1996).
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Metric
9
8
7
6
5
4
3
2
1
2
3
4
5
6
7
8
ai
9 Metric aj
(1)
Where 1= equally important; 3 = moderately more important; 5= strongly more important; 7= very strongly more important; 9= extremely more important; 2-4-6-8 = mean intermediate values (Saaty, 1996).
Step 3 – Form the supermatrix: The ANP problem is represented by a supermatrix, which is a partitioned matrix in which each block matrix represents a relationship between two clusters (Peykarjou & Safavi, 2015). The structure of the supermatrix at the element level is shown below. If and
denotes the nth element in the Nth cluster,
denotes the Nth cluster
is a block matrix that denotes the priority vectors,
which represent the relative importance of the elements in the ith cluster with regard to the jth cluster (Bottero & Mondini, 2008), i.e. the inter-dependencies between the elements (metrics). All relations are assessed through pairwise comparisons and the priority vectors are used to construct the supermatrix. If there is no relationship between clusters and within elements in the same cluster,
will be zero. This
analytical process yields an unweighted supermatrix of the following form (Saaty, 2008). C1
e
11
e
C2
12
.. e
1n1
e
21
e
22
.. e
CN
2n2
e
m1
e m2
.. e
mnm
e 11
C1
e 12
W 11
W 12
W 1m
. e 1n1
. W= C2
e 21 e 22
W 21 :
W 22 :
W 2m :
.
(2)
e 2n2
. Cm
e m1 e m2 . e mnm
W m1
W m2
W mm
The supermatrix needs to be stochastic so that we can derive meaningful limiting priorities. Hence, there is a need to form a weighted supermatrix. In our approach, we do this by using the priority vector from the cluster matrix obtained in the previous step, weighted by each block matrix that falls into the column under the given cluster (Peykarjou & Safavi, 2015). For instance, the first entry of the priority vector derived from the cluster matrix is multiplied by all elements in the first block matrix of the unweighted supermatrix, and so on. Based on the priority vectors obtained from the pairwise comparison matrices, the unweighted and weighted supermatrices are constructed.
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Step 4 - Identify the weighting attributes of the elements towards the goal and select the best alternatives: The final step of the ANP is to obtain a priority ranking for each element in the network structure. In the weighted supermatrix, there is only the direct influence of an element on any other element. However, an element that directly influences a second element can indirectly influence a third element that is directly influenced by a second element. Therefore, the weighted supermatrix obtained from the previous step is transformed into a limiting supermatrix by raising itself to a limiting power to converge and to obtain a long-term, stable set of weights, which is the global priority vector for each element (Abastante et al., 2011). The reason for this calculation is to capture the transmission of all influence paths within the network (Peykarjou & Safavi, 2015).
3. Research Method 3.1 Our ANP approach Following the steps for the application of the ANP method (Saaty and Vargas, 2006), our proposed approach consists of the following steps.
Selection of Sustainability performance metrics
Identify dependencies between the selected metrics and construct the network model
Conduct a survey amongst professionals for pairwise comparisons of the criteria
Calculate the weights of the criteria and rank them using a decision supermatrix
Selection of sustainability metrics: The selection of the sustainability-related metrics was done through a thorough review of the literature. To triangulate our choice of the selected metrics, we also consulted a panel of 5 senior academic experts what work in the field of sustainable supply chain management through structured interviews. During the interviews, the experts were asked to provide their opinion on whether selected metrics from the literature were relevant or not and to provide alternatives and conditions whereby metrics should be selected. Based on the literature review and the experts’ consensus on the process and selected criteria, a final list of metrics was established. A large number of sustainability metrics have been proposed in studies from bodies of literature spanning economics, management, agriculture, and politics. Typical metrics cover environment factors (e.g., energy consumption, greenhouse gas emissions, waste generation), social issues, (e.g., total number of employees,
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gender equality) and economic factors (e.g., economic value added, net income and revenue) (Szekely and Knirsch, 2005). For the design of our proposed sustainability performance framework, initially, we selected sustainability metrics based on the review of existing literature related to sustainability performance indicators. Based on the literature review and the experts’ interview, we formulated and applied the following four main qualifying conditions (Table 2). Table 2: Qualifying conditions for the selection sustainability performance indicators Criteria Relevance to corporate and public policy
Comparability
Measurability
Cost Effective
Definition Promote sustainability (Guy & Kibert, 1998); Critically activity-related (Keeble et al., 2003); Relevant to key internal and external concerns (Keeble et al., 2003); Complement existing regulatory programs (Tanzil & Beloff, 2006); Have social appeal, measure what is important to stakeholders (Reed et al., 2006); Involve several community stakeholders, Useful for decisionmaking (Tanzil & Beloff, 2006); Relevant to the local system (Nordheim & Barrasso, 2007 Capable of comparison with other values reported elsewhere (Holland, 1997); Potentially benchmarkable (Keeble et al., 2003); Have a target level and baseline with regard to which to measure (Reed et al., 2006). Measureable and verifiable (Keeble et al., 2003); Be easily measured, make use of available data (Reed et al., 2006); Quantitatively measurable and/or qualitatively descriptive, Data available or possible to generate (Nordheim & Barrasso, 2007);. Cost-effective in term of data collection (Tanzil & Beloff, 2006); Be cost effective to measure (Reed et al., 2006).
We then applied the following additional set of conditions to filter the abundance of metrics that are available in the literature. Based on the definitions of Seuring and Muller (2008) and of Carter and Rogers (2008), we included metrics that cover all the three commonly used dimensions of sustainability, that are simple to develop, relevant to business and useful to decision-makers, cost-effective to collect and measure, easy to understand to a wide variety of people, assure the results can be reproducible, consistent and comparable, and prevent the calculation of confidential or private information (Schwarz et al., 2002). Finally, we selected metrics based on their ability to be constructed as a ratio that meets the needs of industries and their numerators and denominators can be related to one product unit. This final qualifying condition was deemed critical for the practical application of our proposed method, as the use of quantitative metrics is easier to measure and obtain more objectively. Based on these conditions, we selected the following sustainability-related performance metrics (Table 3).
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Table 3: Selected Sustainability metrics based on those commonly used in the literature Metrics
Authors
En1 - Greenhouse gas emissions Veleva & Ellenbecker (2001), Székely & Knirsch (2005), Singh (tons/unit of production) et al. (2007), Santos et al. (2013), Erol et al. (2009) En2 - Water consumption (m3/unit of production)
Veleva & Ellenbecker (2001), Singh et al. (2007), Erol et al. (2009), Hubbard (2009), Weber et al. (2010), Santos et al. (2013) Environmental Veleva & Ellenbecker (2001), Székely & Knirsch (2005), Singh En3 - Energy consumption (kWh/unit of production) et al. (2007), Hubbard (2009), Santos et al. (2013) En4 - Amount of waste generated Veleva & Ellenbecker (2001), Erol et al. (2009), Weber et al. (tons/unit of production) (2010) So1 – (Social) Investment in Epstein & Roy (2001), Linton et al. (2007), Székely & Knirsch community (2005), Searcy et al. (2007), Erol et al. (2009), Hubbard (2009), (% proportion of revenues) Bai and Sarkis (2010) So2 - Customer/Community Veleva & Ellenbecker (2001), Linton et al. (2007), Erol et al. complaints (rate) (2009) Social So3 - Health and safety incident Veleva & Ellenbecker (2001), Singh et al. (2007), Santos et al. rate (rate e.g. number/hour) (2013) So4 - Average hour of employee Veleva & Ellenbecker (2001), Székely & Knirsch (2005) training (hours/ employee) Ec1 - Productivity Székely & Knirsch (2005), Linton et al. (2007), Singh et al. (turnover / employee) (2007) Ec2 - Return on equity Hubbard (2009), Weber et al. (2010), Santos et al. (2013) (percentage) Ec3 - Economic value added Economic Epstein & Roy (2001), Picazo-Tadeo et al. (2011) (in currency used, e.g. USD) Ec4 - Investment in sustainable processes/products (proportion Searcy, et al. (2007), Singh et al. (2007), Erol et al. (2009) from annual revenues)
Their definition and major proponents are provided in the Appendix of the paper. It should be noticed that the objective of our study is not to come up with an exhaustive list of sustainability metrics, but to point out the breadth of different sustainability issues that need to be considered for the development of sustainable supplier performance framework. Further classifications and detailed metrics could be proposed for specific industries. Depending upon the strategy of organizations, the perspectives of their stakeholders, the preferred indicators may be unique for each company. Identify dependencies and design the network structure: To create the network structure of our MCDM problem, first we classified the criteria into clusters (sustainability pillars) that comprise various elements
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(sustainability metrics) (Bottero & Mondini, 2008). Subsequently, we consulted the panel of experts that helped us in the selection of the sustainability metrics for a second round of interviews to define the interdependencies between the clusters and between each element of the network. The experts were asked to provide their opinion on potential dependencies between the selected criteria by inserting in a relationship matrix the number 1 if they considered there was a dependency between a pair of metrics, and 0 if they considered there was not any relationship. We determined that a relationship between two criteria is present if the majority (i.e., more than 3 experts) agreed on it. Based on our analysis and the experts’ opinions, we identified the following key relationships between elements within the network (Figure 1). Inner dependencies
Explanation
So1
So2
It is possible that companies can minimize the community complaints if they can engage the communities in which they operate.
So4
So3
Providing training to employees, might influence the health and safety incident rate.
Ec1 Ec4
Ec2
Investment in new processes and products might influence productivity, return on equity and economic value added.
Ec3
Outer dependencies
Explanation
Ec1 Ec2
So1
Ec3 En1 En2
Ec4
En3
The level of investment in the community might be dependent on economic performance. For instance, if companies can generate higher revenue and profits, they will have adequate budgets to create the initiative to invest in the community in which they operate. If companies can invest in developing better processes for reducing negative impacts on the environment, it is likely that they will achieve better environmental performance in the four metrics.
En4 So2
Greenhouse gas emission and the amount of waste generated might influence community and customer complaints.
Ec1
Productivity might be dependent on the average number of hours of employee training. The productivity of turnover per employee can potentially increase by providing training and education for employees.
En1 En4 So4
Figure 1: Inner and outer dependencies
Goal Selection of sustainable supplier / prioritization of sustainability metrics A
H Social responsibility performance (So)
C
B
I
D G
Economic/Financial performance (Ec) E
F Environmental performance (En)
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Outer Dependency Inner Dependency
Figure 2: The network model at the cluster level Based on the proposed inner and outer dependencies among all the elements, the network model at the cluster level is shown in Figure 2. The nodes of the network show the components of the system and the arcs represent the interactions between them. In Figure 3 we demonstrate the detailed network structure at the element level, showing the inter-relations and dependencies within the network. In our analysis, we considered all the interactions amongst the elements. It can be seen that all the metrics are linked. Goal Selection of sustainable supplier / prioritization of sustainability metrics Social Responsibility Performance Economic/Financial Performance
Investment in community (So1)
Productivity or Turnover per employee (Ec1)
Customer / Community complaints (So2)
Return on Equity (Ec2)
Health and safety incident rate (So3)
Economic Value Added (Ec3)
Average number of hours of employee training (So4)
Investment in Sustainable Processes and Products (Ec4)
Outer Dependency Inner Dependency
Greenhouse gas emissions (En1)
Energy Consumption (En2)
Amount of waste generated (En4)
Water Consumption (En3)
Environmental Performance
Figure 3: The network model at element level and the interaction among clusters and elements Pairwise comparisons: Based on the structure of the network, we built the structure of the unweighted supermatrix. The unweighted supermatrix helped us identify the number of pairwise comparisons at the cluster as well as the element levels that are needed in our model. Table 4 shows the structure of the unweighted supermatrix at the cluster level. It consists of the sub-matrices (A, B, C, D, E, F) that were obtained from the priorities vectors derived from the pairwise comparisons, as defined by our network model. If there is no relationship between clusters, the sub-matrices are zero. Table 4: The unweighted supermatrix Goal
Environmental
Social
Economic
Goal Environmental
0 B
0 0
0 0
0 E
Social Economic
A C
F 0
H G
D I
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Empirical study: We conducted a broad survey to collect data for the pairwise comparisons of the metrics. The survey involved manufacturing companies in the UK and France with more than 100 employees in the following sectors: aerospace, automotive, chemicals, electronics, steel and shipbuilding. We developed an online questionnaire of the selected metrics using the software qualtrics©. We used stratified sampling from the national databases of purchasing professionals: The Chartered Institute of Procurement and Supply (CIPS) in the UK, and the Conseil National des Achats (CNA) in France. We filtered the original list of professionals according to the following criteria: • • •
Professionals with career experience of at least 15 years as supply chain and procurement managers. Using their profiles, evidence of experience in supplier selection and supplier development processes. There was no filter in terms of race, sex, religion, or specific age groups.
The respondents were given the list of the selected sustainability metrics (along with their definition) and a question that asked them to rate the relative importance of each metric in their decision to evaluate the performance of a potential supplier was posed. We sent the questionnaire to 550 senior supply chain professionals and we received 144 complete replies.
4. Data Analysis and Results 4.1 Pairwise Comparison The data analysis involved three main steps: pairwise comparison of the selected metrics, the formulation of a supermatrix and calculation of final priorities (Bottero & Mondini, 2008). Pairwise comparisons are needed when at least one element in the source cluster is connected to at least two elements in the target cluster (Saaty, 2008). We conducted pairwise comparisons at two levels: at the cluster and element levels. We included the value obtained from each pairwise comparison in a pairwise comparison matrix that we then used to calculate a priority vector (weight of the metric). Subsequently, we incorporated the priority vectors in each pairwise comparison matrix into a supermatrix. We constructed the cluster matrices by obtaining the priority vectors that were derived from the pairwise comparison matrices at cluster levels. The analysis of the data collected was done using the Super Decisions® software package (“Introduction to the ANP”, n.d.), using the simple geometric mean to aggregate the data to get a consensus opinion (Adams, 2001; Shao et al., 2016). Based on the ANP network structure, the three required pairwise comparison matrices at the cluster level and the five required pairwise comparison matrices at the element
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level were developed using data collected from the survey. The pairwise comparison matrices with priority vectors and the respective consistency ratios are shown in Table 5. We conducted consistency tests that yielded consistency ratios of less than 0.10; this confirms that our data are consistent. The last columns of each pairwise comparison matrix are the priority vectors for each element in the pairwise comparison matrices. The priority vectors derived from these pairwise comparison matrices form the elements that were included in the supermatrix. Table 5 – Pairwise comparison Matrices Pairwise comparison matrices at the cluster level With respect to Goal Environmental (En) Social (So) Economic (Ec)
En 1.0000 0.7085 0.8821
So 1.4114 1.0000 1.2028
Ec 1.1336 0.8314 1.0000
Priority vector 0.3863 0.2769 0.3369
Consistency Ratio = 0.0001
With respect to Social aspect Social (So) Economic (Ec)
En
So 1.0000 1.2028
Ec 0.8314 1.0000
Priority vector 0.3107 0.1744 Consistency Ratio 0.0000
With respect to Economic aspect Environmental (En) Social (So) Economic (Ec)
En 1.0000 0.7085 0.8821
So 1.4114 1.0000 1.2028
Ec 1.1336 0.8314 1.0000
Priority vector 0.3863 0.2769 0.3369 Consistency Ratio = 0.0001
Pairwise comparison matrices at the element level With respect to Goal En1-Greenhouse gas emissions En2-Energy consumption En3-Water consumption En4-The amount of waste generated
En 1.0000 1.0966 0.9790 1.1369
En2 0.9119 1.0000 0.7543 0.8835
En2 1.0214 1.3258 1.0000 1.0970
En3 0.8796 1.1319 0.9116 1.0000
Priority vector 0.2371 0.2822 0.2256 0.2551 Consistency Ratio = 0.0014
With respect to Goal So1-Social Investment in community So2- Customer/Community complaints So3-Health and safety incident rate So4-Average number of hours of employee training
So1 1.0000 1.3875 2.4067 0.8929
So2 0.7207 1.0000 2.4456 0.5619
So3 0.4155 0.4089 1.0000 0.2988
So4 1.1199 1.7797 3.3466 1.0000
Priority vector 0.1693 0.2231 0.4694 0.1382
Consistency Ratio = 0.0059
With respect to Goal Ec1-Productivity or turnover per employee Ec2-Return on equity Ec3-Economic value added Ec4-Investment in sustainable processes and products
Ec1
Ec2
Ec3
Ec4
1.0000 1.1307 1.3428 0.9580
0.8844 1.0000 0.9087 0.8073
0.7447 1.1005 1.0000 0.7766
1.0438 1.2387 1.2877 1.0000
Priority vector 0.2263 0.2770 0.2783 0.2184
Consistency Ratio = 0.0023
With respect to Ec4 En1-Greenhouse gas emissions En2-Energy consumption En3-Water consumption En4-The amount of waste generated
En1
En2
En3
En4
1.0000 1.0966 0.9790 1.1369
0.9119 1.0000 0.7543 0.8835
1.0214 1.3258 1.0000 1.0970
0.8796 1.1319 0.9116 1.0000
Priority vector 0.2371 0.2822 0.2256 0.2551
Consistency Ratio = 0.0014
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With respect to Ec4 Ec1-Productivity or turnover per employee Ec2-Return on equity Ec3-Economic value added
Ec1 1.0000 1.1307 1.3428
Ec2 0.8844 1.0000 0.9087
Ec3 0.7447 1.1005 1.0000
Priority vector 0.2886 0.3568 0.3545 Consistency Ratio = 0.0077
The priority vectors derived from the pairwise comparison matrices at the cluster level were used to form the cluster matrix in Table 6. The cluster matrix was used to develop the weighted supermatrix. According to Saaty (2008), pairwise comparisons must be conducted if at least one element in the cluster is connected to at least two elements in the target cluster. It can be seen that some priority vectors in the cluster matrix are given the value 1 because the influencing element is only connected to one element. For example, So1 is directly connected only to So2; therefore, its priority vector has a value of 1, while the priority vectors for others are obtained from the pairwise comparison between elements with regard to the controlling criterion that is at the top of the column of each table. Table 6: The cluster matrix for the ANP model Goal Environmental Social Economic
Goal 0.0000 0.3863 0.2769 0.3369
Environmental 0.0000 0.0000 1.0000 0.0000
Social 0.0000 0.0000 0.4540 0.5460
Economic 0.0000 0.3863 0.2769 0.3369
The final step of the ANP method is to obtain a priority ranking for each element in the network structure. In the weighted supermatrix, there is only the direct influence of one element (metric) on any other element. However, if an element a directly influences element b, then it can also indirectly influence a third element c that is directly influenced by element b. Therefore, we transformed the weighted supermatrix obtained from the previous step into a limiting supermatrix by raising itself to a limiting power in order to converge and to obtain a long-term, stable set of weights, which is the global priority vector for each element (Abastante et al., 2011). The reason for this calculation is to capture the transmission of all influence paths within the network (Peykarjou & Safavi, 2015). In Table 7 we show the detailed limited supermatrix and the final priority ranking of the selected metrics. We also provide a column showing the goal for the weighted and unweighted supermatrices. The priority ranking of each metric for the objective of evaluating the most important metric for sustainability
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performance is shown in the “Limiting Supermatrix Goal” column and the column “Priority vector normalized by cluster” shows the local weight within each cluster.
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Table 7. Unweighted, Weighted and Limiting Supermatrices
Goal
En
So
Ec
En1 Greenhouse gas emissions En2 - Energy Consumption En3 - Water consumption En4 - Amount of waste generated So1 - Social Investment in community So2 – Customer / Community Complaints So3 - Health and safety incident rate So4 - Average number of hours of employee training Ec1 Productivity or turnover per employee Ec2 - Return of equity Ec3 Economic value added Ec4 Investment in sust. process / products
Unweighted Supermatrix Goal
Weighted Supermatrix Goal
Limiting Supermatrix Goal
En1
En2
En3
En4
So1
So2
So3
So4
Ec1
Ec2
Ec3
Ec4
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.2371
0.0916
0.0503
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.2822
0.1090
0.0599
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.2256
0.0871
0.0479
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.2551
0.0986
0.0542
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.1693
0.0469
0.1822
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.2231
0.0618
0.3175
1.0000
0.0000
0.0000
1.0000
1.0000
0.0735
0.0000
0.0000
0.0000
0.0000
0.4694
0.1300
En
So
Ec Rank
0.0000
Priority Vector Normalised by cluster
0.0000
0.0577
0.2371
9
0.0000
0.0000
0.0687
0.2822
4
0.0000
0.0000
0.0000
0.0549
0.2256
10
0.0000
0.0000
0.0000
0.0000
0.0621
0.2551
5
0.0000
0.2610
0.5000
0.5000
0.5000
0.2123
0.3077
2
0.0000
0.0000
0.2610
0.5000
0.5000
0.5000
0.3321
0.5361
1
0.0000
0.0000
0.0000
0.2170
0.0000
0.0000
0.0000
0.0000
0.1241
3
0.1382
0.0383
0.0191
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0322
12
0.2263
0.0762
0.0534
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.2610
0.0000
0.0000
0.0000
0.0613
0.2730
6
0.2770
0.0933
0.0526
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0757
0.2692
8
0.2784
0.0938
0.0528
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0753
0.2702
7
0.0367
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.0000
0.1877
11
9
4
10
5
2
1
3
12
6
8
7
11
0.2184
0.0736
Final priority ranking of each metric
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Figure 4 shows the inner and outer dependencies between the metrics in the ANP model. It can be seen that most of the influence paths within the network, directly or indirectly point to customer/community complaints (So2) and social investment in community (So1). In addition, the metric customer/community complaints is the last destination of the influence path.
Figure 4: The outer and inner dependency in the network of ANP
5. Discussion of results The empirical study was conducted in several manufacturing sectors and the results suggest that social sustainability metrics are perceived to have a relatively higher priority in the selection of sustainable suppliers. Similarly, for suppliers, efficiency, economic value-added and greenhouse gas emissions are also critical areas. We should emphasize that we would expect that the results of the prioritization will be dependent on the opinions of the professionals that participate the decision-making process for the selection of sustainable supplier in terms of their pairwise comparisons. Similarly, we would expect the ranking to change, if a different set of criteria is selected. However, the main focus of the study is not to come up with an authoritative ranking of sustainability metrics but to generate a novel approach of selecting sustainable suppliers. Our proposed approach has certain theoretical, managerial, and policymaking implications that we discuss in this section. From a theoretical point of view, our study moves beyond the normative prescription that a company would typically seek excellence on behalf of its suppliers across all the three dimensions of sustainability. Our results show that the cost and resource constraints that many companies face, forces decision-makers to consider dimensions with short term effects, such as assessing and dealing with potential risks of poor
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social responsibility performance of suppliers as well as short term economic dimensions such as turnover per employee or the operational costs associated with waste generation. From a methodological point of view, we consider that the dependencies among the various sustainability metrics are pivotal in determining the choice of sustainable suppliers and propose the utilization of the ANP, a well-established decision-making method of MCDM to take this into account. We posit that the evaluation of sustainable performance should take into account the dependencies amongst several sustainability performance indicators. The literature is rife of studies of sustainable supplier selection and sustainable performance evaluation. However, the majority of the studies either evaluate the criteria separately or use either a limiting, vague and in some cases arbitrary sustainability metrics without a comprehensive objective. Our study attempts to close this gap in the literature by proposing an analytical evaluation method for weighting sustainability metrics that are widely used across several industries and are easily obtainable and quantified. As a result of the proposed method, the weights and prioritization for each sustainability metric are calculated in a systematic and straightforward way. Our study also has several managerial implications. Many companies and policy-makers often perceive sustainability and sustainable supplier selection in defined silos. The environment in one box, child labour, or racial injustice in another, economic growth or health are in different compartments. And there are many stakeholders within and outside companies, each competing with one another for resources, leverage in decision-making and priorities. This compartmentalisation generates a culture of inaction for supply chain sustainability and prevents decision-makers from exploring and identifying dependencies between sustainability issues. For instance, very often, companies that are active in reducing greenhouse gas emissions, are lagging in social investment, even though the effects of climate change will primarily affect communities with low income. As a result, their selection of suppliers neglects these issues. To overcome this division and the lack of a holistic approach to sustainable suppliers’ evaluation, our proposed method can assist decision-makers in appreciating which aspect or sustainability they should focus on in the selection of appropriate suppliers; as it provides clear insight of suppliers’ sustainability performance with quantitative analysis. Its main contribution is that it is based on authoritative experts’ support using a broad spectrum of standardized, easily quantifiable and measurable sustainability-related metrics, thereby proving a clear weighting factor for each metric.
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From an internal auditing point of view, a company can also use the method to compare at which metrics it performs better than others. By calculating the perceived importance of each sustainability-related metric derived from the proposed model, the company’s sustainability performance can be monitored and managers can identify the critical operations or processes related to the performance metrics that need to be improved to achieve the desired level of performance. As the notion of sustainable supply chain management is concerned with ensuring that every stage and activity in the supply chain contributes to a positive impact on society, the environment and the economy, companies can align their strategies and operations, such as evaluating the sustainable performance of suppliers, based on the priority of their sustainability performance metrics. As such, the proposed method can be used to aggregate multiple decisions in cases when group decision-making is required. The results of the study are important for policy-makers for sustainable development that can design legislations and industrial policies based on issues that are important to companies. The comprehensive list of metrics can help companies to improve competitiveness and supply chains to improve their sustainable performance.
6. Conclusion The growing trend for global sourcing and offshoring has increased the complexity of the selection of the most appropriate partners. Parkouhi et al. (2019) argue that the selection of suppliers in turbulent environments is one of the most challenging and complex tasks. Short-term, cost-focused sourcing and development of arm’s length relationships are no longer considered an effective option. There is a growing pressure for vendors in the developed world to focus on social as well as environmental and financial factors in their selection of suppliers and for companies to opt for holistic approaches to suppliers’ evaluation that incorporate several dimensions (operational, financial, organizational) (Kraft et al., 2018). Our study contributes to the existing literature by introducing a novel decision-making evaluation framework for selecting sustainable suppliers using the ANP method. Through a comprehensive literature review and interviews with sustainability experts, we incorporated salient environmental, social and economic performance metrics in a framework that are quantifiable, easy to obtain and can be used across a variety of different industries. Contrary to fuzzy methods that use criteria that are difficult to assess, our
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model presents a clear method of well-established quantitative decision-making process, which can be used to shape an evaluation platform for the sustainability performance of potential suppliers. It can also be used as a diagnostic tool for a firm to evaluate and align its sustainability performance with its supply chain and corporate strategy. The application of this method is bound to some implementation challenges. Firstly, it is difficult to determine with mathematical accuracy the total appropriate number of metrics, as too many measures will result in heavy work, but too few may not fit well. Also, data against these metrics may not be available, in which case projections need to be made. Our selected metrics may cover different areas, which requires a lot of background knowledge to carry out the method accurately. The time to collect data and analyses information may be too long, and thereby it may be too late to realize what should be changed in measures or implementation. Limitations of the study and future research As with any proposed model, our model also has some limitations. The implementation of ANP requires pairwise group comparisons. As the ideal minimum and maximum acceptable values for each metric are challenging to measure or obtain, the utilization of the fuzzy numbers is limited in this model. The selected method also represents a subjective bias of a researcher/decision maker. There is always going to be a bounded rationality bias in this respect. Finally, for some metrics, there is an inherent difficulty in deciding where and how to measure and apply them. Due to value-laden statements, place and time dependency, the results for societal metrics cannot be assured to be as objective. As some metrics are tracked by humans, calculations may not be always correct and provided on time (Lee and Amaril, 2002). These challenges and limitations can be potentially overcome, with the following suggestions for future research. As the data for the empirical study were collected from a variety of manufacturing companies, further research could be conducted by studying specific companies in order to incorporate the influence of certain selected suppliers (model alternatives). Finally, further research could use our proposed method as the starting point of developing a sustainable supply chain performance measurement system by integrating the ANP with an aggregation method such as a TOPSIS, the multi-attribute utility (MAUT), or the ELECTRE methods.
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APPENDIX - The Definition of Selected Sustainability-related Metrics Metrics
Environmental
Greenhouse gas emissions Energy consumption
Energy used by organization’s activities per a unit of production.
Water consumption
Total fresh water consumed by an organization per a unit of production
Amount of waste generated
Amount of waste generated to land, water, and air before recycling per a unit of production per a unit of production.
Social
Social Investment in community
References Veleva & Ellenbecker (2001) Veleva & Ellenbecker (2001) Veleva & Ellenbecker (2001) Veleva & Ellenbecker (2001)
Share of distributed revenues provided to the community such as donations of money and products, and investment in community development.
Lodhia & Martin (2014); Veleva & Ellenbecker (2001)
Customer / Community complaints
Rate of customer or community complaints regarding firm's operation on generated revenue.
Lodhia & Martin (2014)
Health and safety incident rate
Rate of reportable lost workday injuries and illness case per total number of hour worked by all employees.
Veleva & Ellenbecker (2001)
Average number of hours of employees training in every field which provided by an organization per an employee.
Veleva & Ellenbecker (2001)
Productivity (Turnover per employee)
Company's turnover or total sales per employee to assess sales value generated by an employee.
Székely & Knirsch (2005)
Return on equity
Return or net income on shareholders' fund on an annual basis.
Santos et al. (2013)
Economic value added
Net operating profit after taxes less the cost of all capital employed.
Stern Stewart & Co. (2000)
Investment in sustainable processes and products
Percentage of investment in new and sustainable processes and products on the total revenues.
Singh et al. (2007)
Average number of hours of employee training
Economic
Definitions Tons of CO2 equivalent emitted by an organization per a unit of production
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Highlights •
We develop a sustainability performance measurement framework for supplier evaluation.
•
We select and classify salient sustainability performance metrics related to sustainable supplier evaluation across all three dimensions of sustainability.
•
We utilize the Analytic Network Process method to prioritize sustainability metrics and incorporate the inter-relationships between them.
•
We generate insights about aligning the assessment of the sustainability performance of suppliers with a company’s sustainability strategic goals.
The authors declare that there is no conflict of interest.