Next Article in Journal
Effect of Seasonal Characteristics of Temperature and Relative Humidity on Chloride Diffusion Process in Concrete: A Preliminary Theoretical Study
Next Article in Special Issue
A Principal-Agent Theory Perspective on PPP Risk Allocation
Previous Article in Journal
Packaging as an Offline Method to Share Information: Evidence from the Food and Beverage Industry in the Republic of Korea
Previous Article in Special Issue
Stability Analyses and Cable Bolt Support Design for A Deep Large-Span Stope at the Hongtoushan Mine, China
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

An Evidential Model for Environmental Risk Assessment in Projects Using Dempster–Shafer Theory of Evidence

by
Seyed Morteza Hatefi
1,
Mohammad Ehsan Basiri
2 and
Jolanta Tamošaitienė
3,*
1
Department of Civil Engineering, Faculty of Engineering, Shahrekord University, Rahbar Boulevard, P.O. Box 115 Shahrekord, Iran
2
Department of Computer Engineering, Faculty of Engineering, Shahrekord University, Rahbar Boulevard, P.O. Box 115 Shahrekord, Iran
3
Institute of Sustainable Construction, Faculty of Civil Engineering, Vilnius Gediminas Technical University, Saulėtekio al. 11, LT-10223 Vilnius, Lithuania
*
Author to whom correspondence should be addressed.
Sustainability 2019, 11(22), 6329; https://doi.org/10.3390/su11226329
Submission received: 6 April 2019 / Revised: 28 April 2019 / Accepted: 8 November 2019 / Published: 11 November 2019
(This article belongs to the Special Issue Sustainability and Risks in Construction Management)

Abstract

:
One of the goals of sustainable development is to achieve economic and social growth according to environmental criteria. Nowadays, impact assessment is an efficient decision making method in planning and management with environmental perspectives. Environmental risk assessment is a tool to reduce the impacts and consequences of various activities on the environment in order to achieve sustainable development. One of the commonly used environmental risk assessment methods is the probability–impact matrix method, which is known as a quantitative method for risk assessment of projects. In this method, numerical estimates of probability and impact of risk occurrence are very difficult, and these factors are associated with uncertainty. When uncertainty exists, data integration is of great importance, for which the fuzzy inference system and evidence theory are known as effective methods. Unavailability of experts’ opinion and the exponential growth of the number of required fuzzy rules associated with the risk factors are two drawbacks of fuzzy inference. Dempster–Shafer’s theory of evidence is one of the popular theories used in intelligent systems for modeling and reasoning under uncertainty and inaccuracy. In this paper, an evidential model for project environmental risk assessment is proposed based on the Dempster–Shafer theory, which is capable of taking into account the uncertainties. The proposed model is used to assess the environmental risks of Maroon oil pipelines in Isfahan. In addition, the proposed model is used in the case of tunneling risk assessment taken from the subject literature. To evaluate the validity of the proposed evidential model, the results are compared in two case studies, with the results of the conventional risk assessment method and the fuzzy inference system method. The comparative results show that the proposed model has a high potential for project risk assessment under an uncertain environment.

1. Introduction

1.1. Project Risk Assessment under Uncertainty

Risk is an uncertain event or state that, if it occurs, may influence at least one of the objectives of the project. Objectives may include timing, cost, quality, or performance. Each risk may have one or more causes that will result in one or more of the effects. Any cause can be a need, limitation, or condition that can produce negative or positive outcomes. For example, causes may include the need for an environmental permission to carry out work, personnel constraints, etc. In this case, the risk may include issues such as prolonged licensing by the licensing authority over the scheduled status, or the limitation of the allocation and provision of personnel for the work to be done on-time. If any of such uncertainty events occur, they may affect the cost, scheduling, quality, or performance of the project [1].
The source of the project risk is the uncertainties in these projects. Known risks are those that are identified and analyzed, and there is the potential for planning in response to them, while it is not possible to perform preventive management regarding the unknown risks, and the project team provides a feasible plan. Organizations have found that risk is a threat to project success or an opportunity for effective and efficient project success. Risks that present a threat to the project may be accepted if they are balanced by the results of risk-taking.
The nature of the construction projects is one of the most complex and hazardous industries in the field of safety due to the large number of variables in it, and with the simultaneous shift of the two factors of the labor force and work environment in such projects. Therefore, there exists high uncertainty in construction projects. Consequently, the lack of attention to the assessment of risks in the construction industry will cause irreparable problems and impose heavy costs on the project. Different methods have been employed to evaluate the risk of projects. The probability–impact matrix is one of the traditional methods for risk assessment. Winch [2] believes that for efficient applications, quantitative risk management is difficult and complex, and requires accurate data. Therefore, selecting an effective risk assessment method plays an important role in the economic evaluation phase of projects [3]. Unfortunately, obtaining such data is either difficult or not available in many projects. In addition, using these data is difficult to illustrate with uncertainties. The nature of construction projects has uncertainties in which the risk analysis process relates to individual thinking. This prevents the use of many risk assessment methods. The aim of this paper is to propose an evidential model based on the Dempster–Shafer (DS) theory of evidence for project risk assessment. The proposed DS method helps us to assess the risks of projects in the cases where there exist uncertainties in the data. For instance, the data for the probability of occurrence and the impacts of risk events in the probability–impact method are associated with uncertainty. Therefore, this paper reflects this uncertainty in the process of risk assessment by the concept of theory of evidence.

1.2. Background

Fuzzy multi-criteria decision making methods and the fuzzy inference system are widely used tools for managing and handling complex issues in projects. Application of fuzzy multi-criteria decision making methods for project risk assessment can be seen in several researches. In a study, fuzzy logic was used to assess the risk of construction projects [4]. Nieto and Ruz-Vila [5] used fuzzy theory to assess the risk of construction projects. In this research, the fuzzy hierarchy process analysis method was used to evaluate the risk in construction projects. In one recent paper, Tylan et al. [6] used the five risk criteria to evaluate construction projects. They evaluated 30 projects using the fuzzy analytic hierarchy process (AHP) and the fuzzy technique for order of preference by similarity to ideal solution (TOPSIS). In this study, time risk, cost risk, safety risk, quality risk, and environmental sustainability risk are used as effective risk factors for construction projects.
Valipour et al. [7] proposed a novel framework based on the step-wise weight assessment ratio analysis (SWARA) and complex proportional assessment (COPRAS) methods to assess the existing risks in the excavation projects. Their proposed model enables decision makers to consider uncertainties in the risk assessment process. Seker and Zavadskas [8] extracted the employed fuzzy decision making trial and evaluation laboratory (DEMATEL) to assess occupational risks in the construction industry by considering the interrelationship among risk factors. EI-Shayegh and Mansour [9] assessed the risk of freeway construction projects in the United Arab Emirates. The authors used the likelihood and effect matrix to evaluate projects based on internal and external risk factors. Wang et al. [10] introduced a risk assessment framework for assessing the risk of submarine routes in China. Time risk was considered to evaluate the risks arising from external factors. In addition, the risks associated with decision-makers’ behavior are also considered within the proposed evaluation framework. Samantra et al. [11] introduced an integrated risk assessment methodology based on fuzzy theory to assess the risk of urban construction projects. The authors used a hierarchical structure to identify and classify risks. Then, they defined the risk rate as a function of the possibility of the occurrence of the risk and severity of the occurrence of the risk and, accordingly, assessed the risk of subway stations.
Islam et al. [12] used Bayesian fuzzy networks to assess the risk of construction projects. In their research, the authors first investigated risk assessment methods in construction projects. The authors concluded that the use of Bayesian fuzzy networks could be considered as an effective tool for risk assessment. In another study, Chau et al. [13] identified risk patterns in bridge building and road construction projects in Vietnam. In this research, using the questionnaire and collecting the views of the contractors, the existing risks of bridge building and road construction projects were identified and classified into four categories of contractor risks, project risks, owner-risk, and external risk. Then, the authors identified the probability and impact of each identified risk for a variety of small, medium, and large bridge building and road construction projects. Ghasemi et al. [14] proposed Bayesian network methodology for modeling and analyzing portfolio risks a construction company. Chatterjee et al. [15] introduced the analytic network process in the D number and an extended multi-attributive border approximation area comparison (MABAC) method in D number to prioritize and select the best alternative risk response strategy. Hatefi and Tamošaitienė [16] introduced an integrated fuzzy DEMATEL–fuzzy analytic network process (ANP) model for evaluating construction projects by considering interrelationships among risk factors. The authors utilized the proposed model to evaluate five construction projects based on 22 risk factors.
Fuzzy inference system is a useful method for risk assessment in different domains. In a recent study, the risks were first identified in tunneling projects, and then a fuzzy inference system was designed to evaluate and prioritize the risks involved in tunneling projects. In this research, using the experts’ opinion, 25 fuzzy if-then rules are considered in the fuzzy inference system [17]. Jamshidi et al. [18] designed a fuzzy inference system to assess the risk of pipelines. In the proposed fuzzy inference system, 14 fuzzy if-then rules are considered using experts’ opinions. In another study conducted in this area, a fuzzy inference system containing 25 fuzzy if-then rules designed to assess the safety of oil and gas pipelines. Jaderi et al. [19] designed a fuzzy inference system for risk assessment in the petrochemical industry. Using the Mamdani inference System and the 20 fuzzy if-then rules, the authors perform the risk assessment.
As pointed out in the above-mentioned articles, the fuzzy if-then rules are used for the inference mechanism in the fuzzy inference system, that is a state-of-the-art method for risk assessment, and these rules are determined by the opinions of the experts. Therefore, the correct writing of the fuzzy if-then rules and determining their number can play an important role in the results of risk assessment. Unavailability of experts’ opinion and the exponential growth of the number of needed fuzzy rules with the risk factors are two drawbacks of fuzzy inference systems used for risk assessment, while their ability to model the uncertainty of experts and values is their main advantage. In order to address these problems, a new model based on the Dempster–Shafer (DS) theory of evidence [20] is proposed in this article. This proposed method, similar to fuzzy inference systems, can model the uncertainty involved in the projects and, contrary to fuzzy inference systems, does not need any predefined experts’ rules. This makes the proposed model scalable and efficient.
The DS theory of evidence was applied in different problems and showed promising results. For example, Basir and Yuan [21] utilized the DS theory for engine fault diagnosis and Wahab et al. [22] proposed a DS-based model for detecting misbehaving vehicles. Basiri et al. [23] exploited the DS theory for predicting the sentiment of users from their comments and Nemati and Naghsh-Nilchi [24,25] used DS theory in multimodal affective video retrieval. More recently, Basiri and Kabiri [26] used the DS theory for aggregating sentiment labels and combining supervised and unsupervised machine learning classifier results for sentiment analysis [27].
The remainder of the article is organized as follows. Risk assessment with the fuzzy inference system for is described in Section 2 where the architecture of this system is first introduced and then, their main components are reviewed. A brief overview of the DS theory of evidence and the proposed DS-based model is represented in Section 3. Experimental results and discussions are presented in Section 4 and finally Section 5 sets out the conclusion and identifies some research directions for the future work.

2. Fuzzy Inference System

The fuzzy logic was first introduced by Professor Lotfizadeh in 1965 and became operational in the 1970s. Fuzzy logic is a successful application in the context of fuzzy sets in which variables are linguistic rather than numerical. The fuzzy logic is in contrast to binary or Aristotelian logic that sees everything in two or more ways; yes or no, black or white, zero or one. The values in this logic change between zero and one. In Figure 1, the architecture of the fuzzy inference system is shown.
As it is clear, the fuzzy inference system is generally made up of the following components:
  • Fuzzifier
  • Knowledge-based and fuzzy rules
  • Fuzzy inference engine
  • Defuzzifier
In the following, components of a fuzzy inference system are described for risk assessment based on Yazdani et al. [28]. The process of transforming explicit variables into linguistic variables is called fuzzifying. In a fuzzy inference system, the inputs and outputs of the fuzzy inference system must first be fuzzy. The probability of occurrence and the severity of the risk effect are considered as the two inputs and the risk level is considered as the output of the fuzzy inference system. Linguistic expressions and fuzzy sets used to fuzzify inputs and outputs of the fuzzy inference system are presented in Table 1 and Figure 1, Figure 2 and Figure 3, in the risk assessment. Further details are presented in Yazdani-Chamzini [28].
The second component of the designed fuzzy inference system for risk assessment is a knowledge base and fuzzy rules, which includes 25 fuzzy if-then rules, which are presented in the Table 2.
The third component of the designed fuzzy inference system for risk assessment is the fuzzy inference engine. The inference engine evaluates and inferences the rules using inference algorithms, and, after aggregating the output rules by a defuzzifier unit, it is converted into an explicit or numerical value. Often, the Mamdani and Sugno methods are used for inference. The fuzzy inference engine used by Yazdani-Chamzini [28] is the Mamdani algorithm. The maximum method is used to aggregate the outputs and the center of gravity method is used for defuzzification.

3. The Proposed DS-Based Model

In this section, a brief overview of DS theory is first given, and then its similarities and differences with the fuzzy systems are discussed. Finally, the process of applying the DS theory in risk assessment is described in detail.

3.1. Dempster–Shafer Theory of Evidence

The Dempster–Shafer theory is a theory of uncertainty that is presented to determine the degree of support for an information source from a proposition [19]. In fact, this theory is a substitute for the classical probability theory that lets combining and neglecting evidence, too Basiri et al. [23]. This theory was originally presented by Dempster [29], and then Shafer completed it in his book “A mathematical theory of evidence” [30]. In this theory, the scope of the problem is determined by using a non-empty set of bounded and mutually exclusive sets of hypotheses called the frame of discernment, which is represented by θ, and is defined as:
θ = { θ 1 , θ 2 , , θ n } ,
where 2θ is the power set of θ, which contains all possible subsets of θ. If θ has n members, then there are 2n elements in 2θ.
The amount of evidence support from each member, such as A ⊆ θ, of this set is characterized by a function called the mass function, which is represented by m(A). In other words, each mass function is a basic probability assignment (BPA) to each member of the set θ. This numeric function returns a number in the interval [0, 1] and has the following properties:
m : P ( X ) [ 0 , 1 ] ;
m(∅)=0;
A 2 θ m ( A ) = 1 .
where m(A) can be interpreted as the amount of belief in A based on existing evidence.
The Dempster’s fundamental operator that uses various sources to integrate evidence, is the Dempster’s rule of combination [30]. It can be used to combine two evidences provided that both are defined on the same frame of discernment. This operator, sometimes represented by the symbol ⊕, and also called the orthogonal sum, can be used for the combination of two BPAs, such as m 1 and m 2 , as follows:
m ( A ) = m 1 , 2 ( A ) = ( m 1 m 2 ) ( A ) =   { X Y = A m 1 ( X ) m 2 ( Y ) 1 K 12 A 0 A = ,
K 12 =   X Y = m 1 ( X ) m 2 ( Y ) .
In this relationship, K 12 is a balancing factor that ensures that the composition of m 1 m 2 remains BPA. This factor is also called the contradiction factor, and indicates the degree of contradiction between the two sources of evidence. If K 12 = 0 , then there is no contradiction between evidence, and K 12 = 1 denotes the complete conflict. Further evidence is combined as follows:
( m 1 m 2 m n ) ( A ) = i = 1 n X i = A ( j = 1 n m j ( X i ) ) 1 i = 1 n X i = ( j = 1 n m j ( X i ) ) .

3.2. Applying DS Theory of Evidence in Risk Assessment

Before describing the steps for applying the DS theory in risk assessment, the reason for choosing this theory is presented. First, the DS method is a more general form of the Bayesian approach which has all its benefits. For instance, in the DS method, like the Bayesian method, the available prior information can be incorporated in the inexact inference of the uncertain indicators and inferential results. However, the use of prior information in the DS method is not mandatory. This matter is one of the merits of the DS method. Furthermore, DS theory similar to Bayesian decision theory can provide a framework in which the initial inferential results of the uncertain indicators are related to the final decision analysis. Second, compared to other probabilistic methods such as Bayesian method, in the DS method calculation of the prior probability is not required. Third, it has a flexible and understandable mass function. Forth, creating the mass function is easy and convenient. Fifth, the computational complexity of this method is much less than that of the Bayesian method. Sixth, such as the fuzzy inference system, it is usable in cases where uncertainty exists.
The first step in using Dempster’s theory in each problem is to define the propositions [23,24]. In the proposed model, each proposition indicates the amount of belief in the evidence for the relevant risk factor, which is a real number in the range [ 1 , 5 ] as:
A = f i [ 1 , 5 ]   and   i = { 1 ,   2 } .
In Equation (8), i has only two possible values because we intend to aggregate just two evidences. The second step in using Dempster’s theory is to define the evidence [23]. In the current study, following the natural way in which experts make a decision, we consider the impact and probability as evidence for the final risk value.
After defining the evidence, the third step in using Dempster’s theory is to define the mass function [31]. For this purpose, we use the normalized values of impact and probability as follows:
m ( A ) = f i m a x F m a x F m i n F ,
where max F = m a x { f j | j [ 1 , n ] } , minF = m i n   { f j | j [ 1 , n ] } , and n is the number of risks in the problem.
In order to see a working example of applying the proposed method for obtaining the risk value, suppose the impact and probability scores has the values 4.535 and 1.350, respectively. Based on these two values and according to Equation (9), m 1 ( A ) and m 2 ( A ) are 0.0875 and 0.88375, respectively. Now these two BPAs may be aggregated using Equations (5) and (6) as follows:
K 12 =   X Y = m 1 ( X ) m 2 ( Y ) = 0.0875 × ( 1 0.88375 ) + 0.88375 × ( 1 0.0875 ) = 0.8166 , m ( A ) = m 1 , 2 ( A ) = ( m 1 m 2 ) ( A ) = X Y = A m 1 ( X ) m 2 ( Y ) 1 K 12 = 0.0875 × 0.88375 1 0.8166 = 2.686
As could be seen in the above example, the amount of belief in evidence is considered as propositions. Thus, in the nominator of Equation (5), the values for m 1 ( A ) and m 2 ( A ) are multiplied, while in the denominator, K 12 is calculated using the multiplication of each evidence in the complement of that evidence.

4. Experiments and Results

4.1. Environmental Risk Assessment of Maroon–Isfahan Pipeline

Pipelines seem to be one of the most effective and economical means for the transportation of hazardous and flammable materials such as natural gas, crude oil, and its derivatives that cannot be transported through a railway or rail transport line. In most countries, the system of pipelines is expanding and increasing gas and oil consumption, and they constantly need these materials and safe operation facilities. Additionally, due to combustible materials, explosion and diffusion are normal. In transmission pipelines, due to the dispersal of gas or natural gas through failure or leakage, it creates a risk of explosion or fire as a precursor position.
Isfahan region is located 10 km north of the city of Isfahan and near the refinery in the city at an altitude of 1697 m above sea level. The region is responsible for the transfer of crude oil from the Maroon oil field in Omidieh, Khuzestan province, to the Isfahan oil refinery. The characteristics of the Isfahan area are exploitation and maintenance of the strategic Maroon oil pipeline, 430 km from Omidieh, in Khuzestan to the Isfahan refinery, which is known as the Maroon–Isfahan pipeline. The minimum height of the pipeline is 74 m and the highest elevation is 2700 m above sea level. Due to the Maroon-Isfahan pipeline is located in impassable mountainous areas, it is considered as one of the most damaging pipelines in the world. Despite frequent problems, such as intermittent falls and landslides and seasonal floods, maintenance of this pipeline is in good demand and all pipelines in this area are monitored day-to-day with advanced electronic systems and manpower.
The first and second columns of Table 3 show the notations and the environmental risk events identified in the Maroon–Isfahan pipeline.
The third and fourth columns of Table 3 show the probability of occurrence and the impact of risk events. In order to obtain the probability and impact of risk events, 22 employees of Isfahan oil pipelines and Telecommunication Company identified the environmental risks of the Maroon–Isfahan pipeline and then the probability of the occurrence and severity of the effect of each of the risks was evaluated. To determine the probability of the occurrence and severity of the effect of each identified risk, each expert person first presented his/her views on the likelihood of occurrence and the severity of the effect using Table 1. Then the collected comments were converted to crisp numbers according to the last column of Table 1. At the end, the average scores of the 22 expert opinions were calculated for the probability of the occurrence and severity of the effect of each of the risks and were reported in the third and fourth columns of Table 3.
Columns 5 to 10 of Table 3 show the risk score and rank of risk events, which were obtained by the conventional risk assessment method, the fuzzy inference method, and the proposed method, respectively. In the conventional risk assessment method, the risk score reported in column 5 of Table 3 is derived from the multiplication of the probability of occurrence of risk in the severity of the risk effect. The sixth column of Table 3 shows the rank of risk events obtained using the conventional risk assessment methodology.
The seventh and eighth columns, respectively, represent the risk score and the rank of risk events calculated by implementing the fuzzy inference system. To do this end, according to Yazdani-Chamzini [16], for each type of risk event presented in Table 3, the level of probability and its impact based on the values given in Table 1 are determined by an expert team, including seven assessors with a high degree of knowledge in the area of risk management. Therefore, risk levels are extracted from these numerical values, as represented in Table 3. For each risk event, its probability and impact values are considered as the inputs of the fuzzy inference system. The fuzzy inference engine is applied on both of these inputs and the fuzzy rules represented in Table 2 are evaluated based on the Mamdani algorithm. After evaluating each fuzzy rule, the output of each fuzzy rule is obtained. In the next stage, the outputs of fuzzy rules are aggregated by maximum method and then they are defuzzified by the center of gravity method and converted into the numerical values, which are reported in the seventh column of Table 3.
The last two columns of Table 3 also show the risk score and the rank of risk events obtained by using the proposed Dempster–Shafer method. For obtaining the results of the proposed Dempster–Shafer method, several steps must be performed. In the first step, the propositions and the amount of belief are obtained based on formulation (8). In the second step, the probability and the impact are considered as two evidences for each risk event and their mass functions are provided according to formulation (9). After that, formulations (5) and (6) are applied to combine their respected mass functions, which show the risk score reported in the ninth column of Table 3. Figure 3 graphically depicted the ranks of risk events extracted by the proposed method and fuzzy inference system method.
As Table 3 and Figure 3 show, the risk of "rupture and failure of the pipeline due to burnout", or R4, has been ranked first by the proposed method. This risk factor gained the first and second rank, respectively, by implementing conventional risk assessment methods and the method of the fuzzy inference system. R8 with the title “Making a difference in line pressure at the point of decay due to closure of the valve” was ranked second, third, and tenth, respectively, by using the proposed method, conventional risk assessment method, and fuzzy inference system. The risk of R6, entitled “Rupture of the line or rubbing the reservoir due to landslide”, assigned the third, second, and sixth rank, respectively, using the proposed method, conventional risk assessment method, and fuzzy inference system method. The risk of R10, entitled “Inability to Supply Components Due to Boosts”, was ranked fourth among the top 50 risks by using the proposed method. The risk rating of R10 was four and five using conventional risk assessment methods and the fuzzy inference system, respectively.

4.2. Tunneling Risk Assessment

In this section, the proposed method is used to evaluate tunneling risks and the results are compared with those obtained by the fuzzy inference system method and the conventional risk assessment method. Yazdani-Chamzini [28] proposed a fuzzy inference system to evaluate 47 tunneling risks and compared the results with the conventional risk assessment method. Data on the probability of occurrence and the severity of the effect of each of the tunnel risks are presented. The results of conventional risk assessment and the method of fuzzy inference system and the proposed DS method are reported in Table 4.
The second column of Table 4 shows the risk factors for tunneling. The third and fourth columns show the risk score and the risk rating of the tunnel using the conventional risk assessment method. Fifth and sixth columns show the results of the implementing the fuzzy inference system. In addition, the risk scores and their ranks are shown in columns 7 and 8 in Table 4, which are obtained by the proposed Dempster–Shafer method. Furthermore, the ranking results of the proposed method and fuzzy inference system are depicted in Figure 4.
The results reported in Table 4 and Figure 4 show that the R20 entitled “Toxic gas leakage” had the first rank among the tunneling risks using the proposed method, conventional risk assessment method and fuzzy inference system method. The R19 risk, “Collisions”, ranked second with the proposed method, while this risk factor was ranked fourth in the conventional risk assessment method and fuzzy inference system. The risk of R47, entitled “Financing difficulties,” was ranked third by the proposed method. This risk factor was ranked fourth and second, using the conventional risk assessment method and fuzzy inference system, respectively.

5. Discussion

As mentioned earlier, the DS theory of evidence and the fuzzy inference system were two efficient and applicable methods for modeling uncertainty in project risk assessment. Unavailability of experts’ opinion and the exponential growth of the number of needed fuzzy rules with respect to the risk factors are two drawbacks of fuzzy inference systems used for risk assessment. Fortunately, the DS theory of evidence overcomes to these drawbacks. When the DS method is compared with the probabilistic methods such as the Bayesian method, it has the several merits. Unlike the Bayesian method, the DS method does not require the prior probability. The computational complexity of the DS method is less than that of the Bayesian method. Furthermore, it has a flexible and easy-to-use mass function.
In order to validate the proposed DS method for risk assessment, two cases including the environmental risk assessment of the Maroon–Isfahan pipeline and tunneling risk assessment were considered and the respected results were compared with those obtained by the fuzzy inference system. For doing so, we used the Spearman correlation coefficient. The Spearman correlation coefficient shows the correlation between two ordinal variables. In the first case, which is the environmental risk assessment of the Maroon–Isfahan pipeline, the correlation coefficient between the risk rating in the proposed method and the conventional risk assessment method is 0.946. This correlation coefficient indicates that there is a high correlation between the results of the proposed method and the conventional risk assessment method. Furthermore, the Spearman’s correlation coefficient between the proposed risk rating and the fuzzy inference system method is 0.823. This coefficient shows that there is a high correlation between the results of the proposed method and the method of the fuzzy inference system.
In the case of tunneling risk assessment, the correlation coefficient between the risk rating in the proposed method and the conventional risk assessment method is 0.922. This correlation coefficient indicates that there is a high correlation between the results of the proposed method and the conventional risk assessment method. In addition, the Spearman’s correlation coefficient between the proposed risk rating and the method of the fuzzy inference system is 0.911. This coefficient shows that there is a high correlation between the results of the proposed method and the two methods of fuzzy inference system and conventional risk assessment for the evaluation of tunnel risks. According to the aforementioned results, the proposed method has a high potential for risk assessment in the aforementioned projects. The proposed DS method can be considered as the extension of the probability–impact method for risk assessment in the cases where uncertainty exists. Therefore, the proposed DS method can be utilized for risk assessment in an uncertain environment instead of the conventional probability–impact method.

6. Conclusions

Due to the uncertain nature of experts’ opinions about the probability of occurrence and impact level of risks, this paper proposed an evidential model for environmental risk assessment using the Dempster–Shafer theory of evidence. The proposed evidential model enables us to consider uncertainty in the environmental risk assessment process and, contrary to the fuzzy inference system, does not require any predefined experts’ rules. The proposed evidential model is used to assess the existing risks in two cases. The first case refers to the environmental risk assessment of the Maroon–Isfahan pipeline, where 50 environmental risks are considered to be evaluated. The second case is taken from the literature review in which 47 tunneling risks are assessed [28]. The proposed evidential model is employed to assess the existing risks in the two mentioned cases and the obtained results are compared with those obtained by the conventional risk assessment method and the fuzzy inference system method. The validity of the proposed model is investigated by the Spearman correlation coefficient in two cases. The Spearman correlation coefficient between the results of our proposed method and those obtained by the fuzzy inference system are 0.823 and 0.911, in the pipeline and tunneling risk assessment cases, respectively. Furthermore, these coefficients are 0.946 and 0.922 when comparing our proposed method with the conventional risk assessment method in two studied cases, respectively. According to the results, it can be concluded that the results of proposed evidential model have high consistency with those obtained by the conventional risk assessment method and the fuzzy inference system method.
The DS theory of evidence is an efficient and applicable tool to solve decision making problems under uncertainty. Evaluating construction projects based on the risk factors under uncertainty is an important topic in the field of construction risk management [16]. Therefore, applying DS theory of evidence to solve the construction project evaluation problem under uncertainty is an interesting topic for future research. The existence of conflicts among evidences is one of the limitations of applying the DS method, which may lead to unreliable results. Therefore, proposing a modified DS method for project risk assessment in the case where there exist conflicts among evidences is an important topic for future research.

Author Contributions

Conceptualization, S.M.H. and M.E.B.; methodology, S.M.H. and M.E.B.; software, M.E.B.; validation, S.M.H. and M.E.B.; formal analysis, S.M.H. and M.E.B.; investigation, S.M.H. and M.E.B.; data curation, S.M.H.; writing—original draft preparation, S.M.H. and M.E.B.; writing—review and editing, J.T.; visualization, J.T.; supervision, J.T.; project administration, J.T.

Funding

This research received no external funding.

Acknowledgments

The authors are grateful to the respected reviewers for their constructive and valuable comments in preparation of the revised manuscript.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Iqbal, S.; Choudhry, R.M.; Holschemacher, K.; Ali, A.; Tamošaitienė, J. Risk management in construction projects. Technol. Econ. Dev. Econ. 2015, 21, 65–78. [Google Scholar] [CrossRef]
  2. Winch, G. Managing Construction Projects: An Information Processing Approach; Wiley: Hoboken, NJ, USA, 2002. [Google Scholar]
  3. Nesticò, A.; He, S.; De Mare, G.; Benintendi, R.; Maselli, G. The ALARP Principle in the Cost-Benefit Analysis for the Acceptability of Investment Risk. Sustainability 2018, 10, 4668. [Google Scholar] [CrossRef]
  4. Tah, J.H.M.; Carr, V. A proposal for construction project risk assessment using fuzzy logic. Constr. Manag. Econ. 2000, 18, 491–500. [Google Scholar] [CrossRef]
  5. Nieto-Morote, A.; Ruz-Vila, F. A fuzzy approach to construction project risk assessment. Int. J. Proj. Manag. 2011, 29, 220–231. [Google Scholar] [CrossRef]
  6. Taylan, O.; Bafail, A.O.; Abdulaal, R.M.S.; Kabli, M.R. Construction projects selection and risk assessment by fuzzy AHP and fuzzy TOPSIS methodologies. Appl. Soft Comput. 2014, 17, 105–116. [Google Scholar] [CrossRef]
  7. Valipour, A.; Yahaya, N.; Md Noor, N.; Antuchevičienė, J.; Tamošaitienė, J. Hybrid SWARA-COPRAS method for risk assessment in deep foundation excavation project: An Iranian case study. J. Civil Eng. Manag. 2017, 23, 524–532. [Google Scholar] [CrossRef]
  8. Seker, S.; Zavadskas, E.K. Application of Fuzzy DEMATEL Method for Analyzing Occupational Risks on Construction Sites. Sustainability 2017, 9, 2083. [Google Scholar] [CrossRef]
  9. El-Sayegh, S.M.; Mansour, M.H. Risk Assessment and Allocation in Highway Construction Projects in the UAE. J. Manag. Eng. 2015, 31, 15–22. [Google Scholar] [CrossRef]
  10. Wang, T.; Wang, S.; Zhang, L.; Huang, Z.; Li, Y. A major infrastructure risk-assessment framework: Application to a cross-sea route project in China. Int. J. Proj. Manag. 2016, 34, 1403–1415. [Google Scholar] [CrossRef]
  11. Samantra, C.; Datta, S.; Mahapatra, S.S. Fuzzy based risk assessment module for metropolitan construction project: An empirical study. Eng. Appl. Artif. Intell. 2017, 65, 449–464. [Google Scholar] [CrossRef]
  12. Islam, M.S.; Nepal, M.P.; Skitmore, M.; Attarzadeh, M. Current research trends and application areas of fuzzy and hybrid methods to the risk assessment of construction projects. Adv. Eng. Inform. 2017, 33, 112–131. [Google Scholar] [CrossRef]
  13. Chau Ngoc, D.; Long, L.H.; Soo-Yong, K.; Chau Van, N.; Young-Dai, L.; Sun-Ho, L. Identification of risk patterns in Vietnamese road and bridge construction: Contractor’s perspective. Built Environ. Proj. Asset Manag. 2017, 7, 59–72. [Google Scholar]
  14. Ghasemi, F.; Sari, M.H.M.; Yousefi, V.; Falsafi, R.; Tamošaitienė, J. Project Portfolio Risk Identification and Analysis, Considering Project Risk Interactions and Using Bayesian Networks. Sustainability 2018, 10, 1609. [Google Scholar] [CrossRef]
  15. Chatterjee, K.; Zavadskas, E.K.; Tamošaitienė, J.; Adhikary, K.; Kar, S. A Hybrid MCDM Technique for Risk Management in Construction Projects. Symmetry 2018, 10, 46. [Google Scholar] [CrossRef]
  16. Hatefi, S.M.; Tamošaitienė, J. An Integrated Fuzzy DEMATEL-Fuzzy ANP Model for Evaluating Construction Projects by Considering Interrelationships among Risk Factors. J. Civil Eng. Manag. 2019, 25, 1–18. [Google Scholar] [CrossRef]
  17. Guzman Urbina, A.; Aoyama, A. Measuring the benefit of investing in pipeline safety using fuzzy risk assessment. J. Loss Prev. Process Ind. 2017, 45, 116–132. [Google Scholar] [CrossRef]
  18. Jamshidi, A.; Yazdani Chamzini, A.; Yakhchali, S.H.; Khaleghi, S. Developing a new fuzzy inference system for pipeline risk assessment. J. Loss Prev. Process Ind. 2013, 26, 197–208. [Google Scholar] [CrossRef]
  19. Jaderi, F.; Ibrahim, Z.Z.; Zahiri, M.R. Criticality analysis of petrochemical assets using risk based maintenance and the fuzzy inference system. Process Saf. Environ. Prot. 2019, 121, 312–325. [Google Scholar] [CrossRef]
  20. Shafer, G. Dempster–Shafer theory. Encycl. Artif. Intell. 1992, 1, 330–331. [Google Scholar]
  21. Basir, O.; Yuan, X. Engine fault diagnosis based on multi-sensor information fusion using Dempster–Shafer evidence theory. Inf. Fusion 2007, 8, 379–386. [Google Scholar] [CrossRef]
  22. Wahab, O.A.; Otrok, H.; Mourad, A. A cooperative watchdog model based on Dempster–Shafer for detecting misbehaving vehicles. Comput. Commun. 2014, 41, 43–54. [Google Scholar] [CrossRef]
  23. Basiri, M.E.; Ghasem-Aghaee, N.; Naghsh-Nilchi, A.R. Exploiting reviewers’ comment histories for sentiment analysis. J. Inf. Sci. 2014, 40, 313–328. [Google Scholar] [CrossRef]
  24. Nemati, S.; Naghsh-Nilchi, A.R. An evidential data fusion method for affective music video retrieval. Intell. Data Anal. 2017, 21, 427–441. [Google Scholar] [CrossRef]
  25. Nemati, S.; Naghsh-Nilchi, A.R. Exploiting evidential theory in the fusion of textual, audio, and visual modalities for affective music video retrieval. In Proceedings of the 2017 3rd International Conference on Pattern Recognition and Image Analysis (IPRIA), Shahrekord, Iran, 19–20 April 2017; pp. 222–228. [Google Scholar]
  26. Basiri, M.E.; Kabiri, A. Words are important: Improving sentiment analysis in the Persian language by lexicon refining. ACM Trans. Asian Low-Resour. Lang. Inf. Process. (TALLIP) 2018, 17, 26. [Google Scholar] [CrossRef]
  27. Basiri, M.E.; Kabiri, A. HOMPer: A new hybrid system for opinion mining in the Persian language. J. Inf. Sci. 2019. [Google Scholar] [CrossRef]
  28. Yazdani-Chamzini, A. Proposing a new methodology based on fuzzy logic for tunnelling risk assessment. J. Civil Eng. Manag. 2014, 20, 82–94. [Google Scholar] [CrossRef]
  29. Dempster, A.P. A generalization of Bayesian inference. J. R. Stat. Soc. Ser. B (Methodol.) 1968, 30, 205–232. [Google Scholar] [CrossRef]
  30. Shafer, G. A Mathematical Theory of Evidence; Princeton University Press: Princeton, NJ, USA, 1976; Volume 42. [Google Scholar]
  31. Basiri, M.E.; Naghsh-Nilchi, A.R.; Ghasem-Aghaee, N. Sentiment prediction based on Dempster–Shafer theory of evidence. Math. Probl. Eng. 2014, 2014, 361201. [Google Scholar] [CrossRef] [Green Version]
Figure 1. The structure of a fuzzy inference system, adapted from Urbina and Aoyama [17].
Figure 1. The structure of a fuzzy inference system, adapted from Urbina and Aoyama [17].
Sustainability 11 06329 g001
Figure 2. Membership functions for probability of occurrence, impact level, and risk level [28].
Figure 2. Membership functions for probability of occurrence, impact level, and risk level [28].
Sustainability 11 06329 g002
Figure 3. Ranking results of environmental risks obtained by the proposed method and the fuzzy inference system.
Figure 3. Ranking results of environmental risks obtained by the proposed method and the fuzzy inference system.
Sustainability 11 06329 g003
Figure 4. Ranking results of tunneling risks obtained by the proposed method and the fuzzy inference system [28].
Figure 4. Ranking results of tunneling risks obtained by the proposed method and the fuzzy inference system [28].
Sustainability 11 06329 g004
Table 1. Linguistic terms and definitions of risk factors.
Table 1. Linguistic terms and definitions of risk factors.
Inputs and OutputLinguistic TermsDefinitionsCrisp Rating
Probability levels (Input 1)Improbable (IM)So unlikely event, it may not be experienced1
Remote (R)Unlikely to occur during the lifetime2
Occasional (O)Likely to occur during the lifetime3
Probable (P)May occur several times4
Frequent (F)Will occur frequently5
Impact levels (Input 2)Negligible (N)Highly have no impact on the process1
Minor (M)Have no critical impact on the process2
Major (MA)Have no substantial impact on the process3
Critical (C)Have a certain impact on the performance4
Catastrophic (CA)Have a highly impact on the performance5
Risk levels (Output)Insignificant (IN)Risk is tolerable without any mitigation(1–4)
Tolerable (T)Some partial mitigation may be needed(5–8)
Substantial (SU)Mitigation may be needed(9–12)
Significant (S)Mitigation should be implemented to reduce risk(13–16)
Intolerable (INT)Mitigation that reduces risk must be implemented(17–25)
Table 2. Fuzzy if-then rules [28].
Table 2. Fuzzy if-then rules [28].
Probability
IMROPF
ImpactNININTTT
MINTTSUSU
MATSUSUSS
CTSUSSIN
CASUSSININ
Table 3. Comparison of the priority of risks between the proposed model and the fuzzy inference system.
Table 3. Comparison of the priority of risks between the proposed model and the fuzzy inference system.
NoRisk EventProbabilityImpactConventional MethodFuzzy Inference System MethodProposed Method
RiskRankRiskRankRiskRank
12345678910
R1Water and environment pollution due to leakage of crude oil from the pipeline through the lake2.0504.7059.6593.2974.2695
R2Water-taking and tearing of the pathway of the Dooplan River1.9004.6808.89103.1584.0787
R3The penetration of welding at the site of the half pipe, patched to the pipeline and piercing it4.0003.18012.7253.4814.1296
R4Rupture and breaking of the pipeline due to burnout4.0004.05016.2013.4524.6241
R5Breaking the tube due to underwater flows3.7503.25012.1963.4143.9559
R6Rupture of the line or cracking of the reservoir due to the drift of the ground3.7504.12015.4523.3864.5453
R7Line tearing due to falling mountain3.8003.15011.9773.4333.92210
R8Difference in pressure and line tearing at the point of decay due to the closure of the valve3.5504.26815.1533.07104.5482
R9Reservoir corrosion due to dewatering delay1.9004.3388.24112.73123.37612
R10Failure to procure parts due to sanctions3.0504.42113.4843.3954.4454
R11Fire due to material release to turbine exhaust through hole line1.5504.8007.44122.89114.0078
R12Abrupt stopping of turbines and reverse pressure on the transmission line2.7002.6007.02172.04332.3225
R13Inability to check and visit the transit line3.0002.4007.20151.87362.421
R14Defective cable and failure to send and receive electricity2.2002.1804.80441.51451.60840
R15Material leakage from the reservoir due to corrosion1.3504.5356.12302.37232.68616
R16Line break due to inappropriate design2.7002.0705.59341.45471.8532
R17Environmental pollution due to human wastewater transfer2.5004.25010.6383.1193.88911
12345678910
R18Abrupt stopping of turbines and reverse pressure on the transmission line2.5002.0405.10371.46461.69634
R19Damage to lines due to the impact of machinery3.4002.0206.87221.88352.35723
R20The collision with the tube and its deterioration due to the redundancy1.7503.9806.97182.29252.61118
R21Disrupting the measurement of technical quantities due to the presence of water2.5002.0005.00391.43481.66736
R22Corrosion of the pipeline due to the release of corrosive materials1.2004.8285.79322.52173.15513
R23Valve fracture, due to existence of water inside it2.2003.1106.84232.62142.29427
R24Drop of personnel due to freezing stairs2.0503.2006.56282.56162.21329
R25The creation of an anode cathode flow due to the lack of tank cover2.2003.2507.15162.72132.42120
R26Breakdown of tubes or lines by cold weather1.0504.3754.59451.87361.25643
R27Crash of passing cars2.1003.2956.92202.62142.35224
R28The collision of agricultural equipment with the pipeline1.6504.2206.96192.37232.77915
R29The creation of decay and corrosion in the facility due to the presence of water1.2504.1785.22361.87361.8233
R30Disruption of the cathodic system1.7504.1707.30142.43192.87414
R31Cable tear and collision with residential building1.9003.8557.32132.39222.6817
R32Machine failure and equipment collapse during repair1.8003.7136.68262.27272.3822
R33The destruction of the coating on the pipe due to inappropriate area around (water, growing plants, and etc.)1.9353.4706.71252.41212.3225
R34Decrease in the life of the devices considering their standard1.8003.5656.42292.24292.23528
R35Oil spill due to lack of repair of tank floor plates1.9353.0605.92312.43191.97930
R36Line damage due to earthquake1.8003.1405.65332.28261.89431
R37The collapse of local people while crossing the pipeline4.0001.6606.64272.11312.48919
R38Lack of timely implement of relief valves1.0003.6603.66491.4150146
R39Drop of personnel due to freezing stairs1.6503.0004.95402.1321.6537
R40Misdiagnosis regarding the required repair site1.8002.6904.84432.13301.61839
R41Delay in the expropriation of land from residents1.3503.1004.19471.69411.38342
R42Tensions and pressures caused by building materials1.0503.2803.44501.42491.06645
R43Local threats1.8002.4504.41461.8401.49841
12345678910
R44Bursting the stopper during welding4.0001.2605.04381.58431.6935
R45The emission of toxic gases SO2 and CO2 in the operation of tank repair due to environmental factors1.2503.0003.75481.57441.2544
R46Fire during welding due to the presence of petroleum products1.0004.9504.95402.4718146
R47Failure to transfer petroleum products due to equipment inefficiency3.8001.3004.94421.63421.63638
R48Failure of the pipeline due to the impact on it3.8001.4605.55351.84391.93133
R49Damage to personnel’s hearing system at the place of material pumping3.8001.7806.76242.26282.44420
R50Environmental pollution due to its correlation3.5501.9406.89212.03342.40322
Table 4. Comparison results of tunneling risk assessment methods.
Table 4. Comparison results of tunneling risk assessment methods.
No.Risk EventsConventional MethodFuzzy Inference System MethodProposed Method
RiskRankRiskRankRiskRank
12345678
R1Land acquisition problem6301.56452.0340
R2Difficulty in cooperation with related government6302.56322.3835
R3Public opposition8232.89173.5620
R4Unscientific planning of tunnel construction4441.57441.3345
R5Inadequate design specification and documentation8232.50332.7330
R6Over break6302.75212.5431
R7Inaccurate survey data6302.69232.4533
R8Design mistakes5422.31382.0538
R9Lack of experienced designers3461.53461.1946
R10Conflict designs on interface between adjacent a1273.53103.9615
R11Water inflow8232.65243.6519
R12Tunnel walls instability9192.61263.1622
R13Tunnel face instability6302.38362.0340
R14Fault zone6301.99402.5332
R15Squeezing6302.24391.9642
R16Collapse1273.6744.1811
R17Rock burst5422.59273.2721
R18Roof fall1273.6744.2510
R19Collisions1543.6744.72
R20Toxic gas leakage2014.3414.971
R21Poor ventilation6301.91412.4434
R22Fire in tunnel8232.59273.1523
R23Disturbance to the residents near the construction1273.694.0513
R24Physical damage to workers10162.88194.308
R25Ecological constraints6301.68431.9642
12345678
R26Surface subsidence1273.44133.8616
R27Noise8232.41352.8827
R28Air pollution9192.57303.0824
R29Interference of different operations8232.89173.0125
R30Inconsistent schedule in intersections6302.32372.0439
R31Damage to the foundation of adjacent buildings1273.46123.9814
R32Inappropriate machine and equipment selection1273.16163.7518
R33Rough and incomplete construction program4441.82421.6944
R34Inappropriate material selection6302.65242.3636
R35Machinery breakdown10162.88194.397
R36Poor workmanship6302.57302.2437
R37Poor construction programming9192.47342.9526
R38Delay of materials supply1623.7134.594
R39Managerial inability10163.25154.289
R40Lack of experienced professional consultants3461.41471.0547
R41Change of key personnel8232.75212.8628
R42Workers’ strike1273.6744.1712
R43High tender price1543.35144.446
R44Material price escalation1273.49113.8217
R45Labor cost escalation9192.58292.7529
R46Delay in contractual progress payment1623.6684.485
R47Financing difficulties1543.7724.663

Share and Cite

MDPI and ACS Style

Hatefi, S.M.; Basiri, M.E.; Tamošaitienė, J. An Evidential Model for Environmental Risk Assessment in Projects Using Dempster–Shafer Theory of Evidence. Sustainability 2019, 11, 6329. https://doi.org/10.3390/su11226329

AMA Style

Hatefi SM, Basiri ME, Tamošaitienė J. An Evidential Model for Environmental Risk Assessment in Projects Using Dempster–Shafer Theory of Evidence. Sustainability. 2019; 11(22):6329. https://doi.org/10.3390/su11226329

Chicago/Turabian Style

Hatefi, Seyed Morteza, Mohammad Ehsan Basiri, and Jolanta Tamošaitienė. 2019. "An Evidential Model for Environmental Risk Assessment in Projects Using Dempster–Shafer Theory of Evidence" Sustainability 11, no. 22: 6329. https://doi.org/10.3390/su11226329

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop