A comprehensive risk assessment model based on a fuzzy synthetic evaluation approach for green building projects: the case of Vietnam

Hung Duy Nguyen (Department of Management and Engineering, University of Padova, Vicenza, Italy)
Laura Macchion (Department of Management and Engineering, University of Padova, Vicenza, Italy)

Engineering, Construction and Architectural Management

ISSN: 0969-9988

Article publication date: 14 April 2022

Issue publication date: 15 August 2023

2263

Abstract

Purpose

Risks in implementing green building (GB) projects have emerged as a significant obstacle for GB development, especially in developing countries. In recent years, both academics and construction practitioners have paid considerable attention to the risks associated with GB. In this study, the authors aimed to create a comprehensive risk assessment model that considers three crucial risk features: impact level, probability of occurrence and risk manageability.

Design/methodology/approach

In the research, authors adopted the mean scoring and fuzzy synthetic evaluation method to assess GB risks. Based on expert assessments, this model can determine the significance of risk factors, risk groups and overall risk. Notably, this research applied the proposed model to assess GB risks in Vietnam by surveying 58 GB experienced professionals.

Findings

The findings revealed that GB risks are relatively high in Vietnam, implying that risk management is essential for GB projects to succeed. The results also showed that “lack of experience of GB designers” is the most critical factor, and “human resources risk in the design phase” is the top crucial risk group.

Originality/value

This study contributes a novel and practical model to help practitioners assess risks in GB projects. In addition, this research offers detailed GB risk evaluations in Vietnam and thus could be a valuable reference for construction practitioners and future studies.

Keywords

Citation

Nguyen, H.D. and Macchion, L. (2023), "A comprehensive risk assessment model based on a fuzzy synthetic evaluation approach for green building projects: the case of Vietnam", Engineering, Construction and Architectural Management, Vol. 30 No. 7, pp. 2837-2861. https://doi.org/10.1108/ECAM-09-2021-0824

Publisher

:

Emerald Publishing Limited

Copyright © 2022, Hung Duy Nguyen and Laura Macchion

License

Published by Emerald Publishing Limited. This article is published under the Creative Commons Attribution (CC BY 4.0) licence. Anyone may reproduce, distribute, translate and create derivative works of this article (for both commercial and non-commercial purposes), subject to full attribution to the original publication and authors. The full terms of this licence may be seen at http://creativecommons.org/licences/by/4.0/legalcode


1. Introduction

The construction industry has a crucial role in developing a country. Nevertheless, construction activities also affect the environment seriously, resulting in pollution and global climate change (Kientzel and Kok, 2011). According to previous studies, the construction industry utilizes 40% of raw stone and sand and 25% of natural wood globally (Robichaud and Anantatmula, 2011). In addition, construction activities account for 30–40% of energy and 16% of water use worldwide. Also, environmental pollution is becoming more and more critical due to the large amount of waste generated during traditional buildings’ life cycles (Li et al., 2016).

Green buildings (GBs) have emerged as a solution to reduce the negative influence on the environment of the construction industry (Retzlaff, 2010). Unlike traditional buildings, GBs emphasize environmental and social aspects (Ahmad et al., 2019). Previous research revealed that GBs emit just 1/3 of the greenhouse gases, consume 1/3 of the electricity and water and recycle 96% of the demolition waste compared with traditional buildings (BIC Economics, 2014). Also, some empirical studies have indicated that GBs can help mitigate the threats posed by increasing urbanization, energy consumption and emissions (Dean et al., 2016).

GB has several definitions. Notably, the term “green building” is frequently utilized interchangeably with “sustainable construction” (Woolley and Kimmins, 2003). GB refers to the quality and features of buildings constructed utilizing sustainable construction practices and principles (Kibert, 2016). Likewise, some authors considered that GB is a high-performance building that has a low impact on the environment and effectively improves human health and resource consumption (e.g. raw materials, water and energy) (Darko and Chan, 2016). From these definitions, GBs can be understood as “healthy facilities designed and built in a resource-efficient manner, using ecologically-based principles” (Kibert, 2016). Ahmad et al. (2016) also suggested that energy efficiency, reduced maintenance and operation cost and prolonged life are critical factors that motivate the adoption of GB. Many countries have developed GB standards, such as LEED in the US, BREAM in the UK and Green Star in Australia.

In recent years, GBs have become more popular worldwide (Ahmad et al., 2019). To date, many governments have attempted to improve sustainable development in the construction industry (Hassan et al., 2016). Notably, the development of GBs in several developing countries has experienced impressive growth, and the number of GBs in these countries is anticipated to increase significantly in the following years (Dodge Data and Analytics, 2018). Along with that, construction communities in developing countries have recognized the benefits of GBs (Chua and Oh, 2011). This phenomenon revealed that GBs had received attention not only in developed countries but also in developing countries.

However, GB development faces many hindrances. In which, risks in implementing GB projects have emerged as a substantial problem (Ahmad et al., 2019). Indeed, “No construction project is risk-free” (Latham, 1994). Construction projects confront numerous challenges, such as cost, technical, human resources and quality issues (Taroun, 2014). Moreover, risks in different life cycle stages usually vary due to the complexity and uncertainty of construction projects (Zhao et al., 2010). Notably, risks in GB projects are even higher than those in regular projects (Hwang et al., 2017b). Compared with conventional projects, GB projects are riskier because of the application of novel technology and green materials to achieve green objectives in addition to common objectives (Guan et al., 2020). Thus, GB projects will be more likely to fail if practitioners cannot appropriately identify, assess and respond to risks. This revealed that studying the risks in GB projects is necessary for the development of GBs.

The topic of risks in GB projects has recently received growing interest from academics (Nguyen and Macchion, 2022). However, current solutions still have limitations, such as the identification and classification of GB risks being less consistent. In addition, most previous studies only used traditional methods to evaluate risks (i.e. multiple impact levels with probability) (Nguyen and Macchion, 2022). Moreover, these studies were mainly limited to developed economies such as Singapore, Australia, US and China (Nguyen et al., 2021). There has been a dearth of studies on GB risk in developing economies (Ahmad et al., 2019; Nguyen and Macchion, 2022). This highlights the necessity to investigate risks in GB projects in developing countries.

To contribute to the literature, this research developed a comprehensive risk assessment (RA) model for GB projects. This model was then applied to thoroughly assess the GB risks in Vietnam. Vietnam was selected as a case study because it is a paradigmatic example of a developing country in Southeast Asia. In addition, the development of GBs has recently improved significantly in Vietnam, with an increasing number being built (Dodge Data and Analytics, 2018). Furthermore, according to previous research, risk in the implementation of GB projects is a noteworthy hindrance to developing GBs in Vietnam (Nguyen et al., 2017). Therefore, this research fills the gap by contributing a practical RA model, thereby supporting the development of GBs in Vietnam as well as developing countries in general.

2. Theoretical background

2.1 Risks in GB projects

This section provides an overview of GB risk studies to position this research within the existing literature. The results of the literature review indicated that a growing number of studies had investigated risk in GBs in recent years (Nguyen and Macchion, 2022).

For example, Hwang et al. (2017a) endeavored to identify risks in residential GB projects in Singapore. The study revealed the 5 most essential risk factors and suggested 14 risk mitigation measures to handle these in residential GB projects in Singapore. Similarly, another study examined the risks related to commercial GB projects in Singapore (Hwang et al., 2017b). The results revealed the top-five risk factors and proposed seven widely used risk mitigation measures in commercial GB projects. Notably, compared with conventional projects, these two studies concluded that risks in GB projects are more critical than in traditional projects. This finding is not surprising as adopting green solutions (e.g. green materials and technologies) introduces further risk factors into GB projects.

In the same vein, El-Sayegh et al. (2021) investigated risks in GB projects in the United Arab Emirates (UAE). A survey was conducted to assess 30 risk factors which were grouped into 5 categories. The results revealed the top-five critical risk factors that may help practitioners respond appropriately. Similarly, Ismael and Shealy (2018) explored the risks associated with sustainable buildings in Kuwait. A survey was conducted with 131 practitioners to assess 52 risk elements. According to the results, the lack of experience of designers and contractors with GBs is the most severe risk. In addition, a high initial cost for materials and overall project costs are also worth considering.

Tao and Xiang-Yuan (2018) investigated risk factors in GB projects based on the sustainability perspective in China. The results showed that the two most significant risks were “Lack of experienced management in the operational phase” and “The satisfaction of the public is meager”. Likewise, Qin et al. (2016) assessed risk factors in the life cycle of GB projects by multiplying the probability of occurrence and impact level. In addition, the outcomes revealed that project stakeholders have different risk preferences. This finding could help practitioners develop risk management (RM) strategies according to the stakeholders’ perceptions. Especially, Rafindadi et al. (2014) attempted to explore GB risks based on stakeholder opinions in 56 countries. The results showed no significant discrepancy among stakeholders’ attitudes toward sustainable project risks. The contradiction between these findings may suggest that GB risk assessments in various countries could also be different.

In another point of view, Guan et al. (2020) examined the interdependencies of GB risks factor by using interpretive structural modeling. This research identified 22 risks, 16 constraints and 11 objectives through a literature review. Also, this study created a hierarchical network structure to depict the cause-effect relationships between constraints, risk factors and objectives. Furthermore, the dependence/drive powers of risk interdependency were analyzed. The findings indicated the significance level of constraints/risk factors with the objectives and revealed critical risk factors/constraints in implementing GB projects.

In summary, a number of studies have attempted to investigate the risk factors in implementing GB projects in recent years (Nguyen and Macchion, 2022). However, the identification and classification of GB risks remain inconsistent in previous studies (Nguyen et al., 2021). Several studies have attempted to create models for assessing risk levels in GB projects. Nevertheless, most of the previously proposed risk assessment (RA) models for GB projects only considered the two traditional risk features, including the impact level and probability of occurrence. Notably, very few studies have examined the GB risks in developing countries. The findings reveal gaps that this research can exploit.

2.2 Fuzzy synthesis evaluation in RA

RA is widely recognized as complicated and vague; thus, qualitative linguistic terms are inevitable when evaluating risk factors (Wang et al., 2004). Fortunately, fuzzy set theory can solve ambiguous and subjective problems (Pedrycz et al., 2011). Furthermore, mathematical operators can be used in the fuzzy domain using the fuzzy set theory (Ma and Kremer, 2015). The fuzzy set theory can also quantify linguistic aspects and the decision-making of individuals or groups (Zhao et al., 2014). Therefore, it is suitable to adopt the fuzzy set theory in the RA process.

Fuzzy synthetic evaluation (FSE) applies fuzzy set theory and is a suitable method for evaluating decision-making with regard to various criteria. According to previous research, FSE can provide a synthetic assessment of an object associated with many factors/criteria in a fuzzy decision environment (Hsu and Yang, 1997). Notably, FSE is adopted in many fields, such as environmental analysis, human resource management and RA. For example, one study in China used FSE to evaluate contractors’ RM competency in subway projects (Mu et al., 2014). FSE has also been applied to analyze risks in sustainable projects in Singapore (Zhao et al., 2016). According to previous studies, FSE has advantages in handling complicated evaluations with numerous characteristics and levels (Mu et al., 2014; Xu et al., 2010). Therefore, the authors selected FSE to develop the RA model in this study.

2.3 Identify the most significant risk factors in GB projects

In the first step, GB risk factors were identified through a comprehensive literature review. The outcome of this step was a list of 90 risk factors. This list was then reviewed and refined through interviews and brainstorming with ten professionals. The final list consisted of 53 risk factors. In the second step, the authors conducted a questionnaire survey to assess the importance of the 53 risk factors. Based on the collected data from 207 GB practitioners, exploratory factor analysis was adopted to reveal the 30 most crucial risk factors loaded under the six risk components/groups: (1) human resources and technical risks in the construction phase; (2) performance risk in the operation phase; (3) human resource risk in the design phase; (4) financial risk; (5) regulation risk and (6) green material risk (Table 1). The authors used the 30 identified factors to create the RA model in this research.

3. Research methodology

Figure 1 illustrates the overall research framework. The first block illustrates the steps to identify GB risks, which are presented in Section 2.3, whereas the second block shows the approaches to developing the RA model. The research methodology in the second block comprised the following steps: (1) developing an RA model; (2) collecting input from knowledgeable professionals; (3) calculating risk parameters and (4) discussing the findings.

3.1 Measures of the questionnaires

The questionnaire, consisting of three parts, was developed to collect ideas from GB professionals. Part 1 identifies participants’ experiences with GBs, such as the frequency of participation in GB projects and GB knowledge. Part 2 involves assessing risk factors based on three criteria: impact level, probability of occurrence and manageability. The scales are presented in Table 2. Finally, Part 3 investigates the participants’ backgrounds, such as project roles, experience, GB knowledge and position.

The impact level (I) of risk factors was assessed using an ordinal scale: 1 denotes “very low impact” and 5 means “very high impact”. Similarly, this study evaluated the occurrence probability (P) from 1 (likelihood of occurrence is very high) to 5 (likelihood of occurrence is very high). On the same scale, risk manageability (M) was assessed as follow: 1 = extremely easy to control (the probability of occurrence and the impact can be decreased/eliminated); 2 = easy to control; 3 = medium to control (the probability of occurrence or impact can be reduced at some level); 4 = difficult to control; 5 = considerably difficult to control (neither probability of occurrence nor impact can be decreased).

Risk manageability indicates the feasibility of mitigating the risk magnitude by reducing the risk impact and probability of occurrence. This feature is determined not only based on risk factors but also on practitioners’ capacity. In other words, risk manageability is related to the attributes of both risk factors and practitioners. Thus, when assessing risk manageability, participants should consider two aspects: the first aspect is the capacity to control specific risks based on experience in dealing with them (Dikmen et al., 2018); the second aspect is risk attributes (i.e. the natural controllability of risk factors). This implies that some risk factors are more controllable than others by their nature (Aven et al., 2007).

3.2 Questionnaire survey

First, seven professionals were invited to participate in the pilot survey to validate the questionnaire. Professionals were required to (1) answer all questions and (2) write feedback to clarify the survey questions. The pilot test was completed once the professionals had reached a general consensus regarding the questionnaire content. As a result, the questionnaire had minor adjustments. The final questionnaire was distributed to the potential respondents.

A total of 250 survey questionnaires were sent to professionals. Potential respondents with rich GB risk experience were identified from the Vietnam Green Building Council, GB consultants and GB contractors. Finally, 195 respondents received questionnaires via email and 55 respondents took hard copies.

After three months, 69 complete questionnaires were obtained. The response rate was 27.6%, which is consistent with the average rate (20–30%) in most surveys in the construction industry (Akintoye, 2000). Among these responses, 11 incomplete responses were eliminated. Finally, 58 valid responses were used as the inputs for the RA model. The reliability test revealed a Cronbach’s alpha coefficient of internal consistency value of 0.90 (>0.80), indicating that the data are reliable (Nunnally, 1994).

Table 3 summarizes the profiles of respondents. The majority of participants (93.10%) worked nationally or internationally (mainly in Southeast Asia). Thus, they should have a good understanding of the construction industry in Vietnam and developing countries. Furthermore, this survey covered numerous construction companies and stakeholders, such as owners, consultants and contractors. Regarding their positions, 24.14% were senior managers, 31.03% were managers and 41.38% were engineers. In addition, 28 (48.28%) respondents had worked for more than 10 years in the construction industry. Regarding GB knowledge, 39.66% of the participants were GB experts and 60.34% were familiar with GBs. In summary, the results indicate the trustworthiness of the collected data.

3.3 Calculate risk parameters

The most common way to evaluate the significance of risk factors is to multiply the impact level and probability of occurrence. This is also the most popular method for evaluating risk factors in the construction literature (Taroun, 2014). The formula is as follows:

(1)RA=P×I
where RA = risk assessment, P = probability of occurrence, and I = impact level.

In this research, the authors complemented the traditional formula above by adding risk manageability (M), which was recommended by previous research (Dikmen et al., 2018; Taroun, 2014). According to previous studies, risk manageability reflects risk attributes and is related to practitioners’ abilities and specific situations (Dikmen et al., 2018; Xia et al., 2017). Indeed, the higher the probability of occurrence and impact, the greater the risk significance. In contrast, risk significance decreases if the ability to manage risk increases.

To facilitate respondents’ assessment, the scale of risk manageability was set similar to the scales of risk impact and probability: the higher the M value, the more difficult it is to manage risk. In addition, this helps the value of risk significance (RS) be presented on the same scale as other criteria (from 1 to 5), thereby facilitating the interpretation of results. This is also suitable for the fuzzy technique because we can switch between linguistics and number values and vice versa. The formula for risk significance is

(2)RS=P×I×M3

3.4 Mean scoring ranking technique

The mean scoring (MS) method is a popular technique that can be applied to many fields. For example, the MS method has been applied to calculate the relative importance of various indices/criteria (Mu et al., 2014; Xu et al., 2010). In this study, MS was used as a statistical technique to determine the relative importance of GB risk factors (Mu et al., 2014; Zhao et al., 2016). The collected data were used to compute the MS according to each risk factor attribute, which determines the relative ranking of each feature of the risk factors. The formula of MS to calculate for each attribute of risk factors is illustrated by

(3)MS=i=15sifii=15fi
where:
  1. i denotes the response category index, from 1 = very low/rarely/extremely easy to control to 5 = very high/almost definite/greatly difficult to control;

  2. si denotes the weight assigned to the ith response; si = 1, 2, 3, 4 and 5 for i = 1, 2, 3, 4 and 5, respectively;

  3. fi denotes the frequency of the ith response.

3.5 Fuzzy synthetic evaluation

The purpose of FSE is to assess an object associated with various criteria in a fuzzy decision environment (Mu et al., 2014). According to previous studies, FSE has advantages in handling complicated assessments with multiple criteria and multiple levels (Akter et al., 2019; Xu et al., 2010). Therefore, utilizing FSE to assess GB risks in this study is appropriate because risks also comprise multiple criteria and levels.

As is well known, risks in construction projects frequently comprise numerous risk factors and risk groups. Thus, risk factors and risk groups must be scrutinized during an RA process to ensure accuracy. This research applied FSE to create an RA model to evaluate risk factors in GB projects via three attributes: risk impact, probability of occurrence and risk manageability.

There are three essential components in the RA model as a multi-criteria assessment model (Mu et al., 2014; Xu et al., 2010):

  1. A family of criteria/risk factors f = {f1, f2, …, fm}. In this study, m was the number of risk factors.

  2. A set of alternatives E = {e1, e2, …, en}, where n is the number of alternatives.

  3. For every object, there is an evaluation matrix R = (rij)m×n, where rij denotes the degree to which alternative ej satisfies the criterion/risk factor fi.

The evaluation results of the objects can be calculated based on these three elements. In addition, three hierarchical GB risks were investigated in this model: risk factors, risk groups and overall risk. The process of assessing risks includes three steps: first, the model calculates parameters to assess risk factors; the evaluation of risk groups is then determined based on risk factors; and, finally, the overall risk is determined.

3.5.1 Evaluate GB risk factors

First, the features (P, I and M) of all risk factors were identified based on the inputs from the questionnaire survey. According to Table 2, all of the features have the same value (from 1 to 5) in the set of alternatives E. Hence, set of E for probability is e1 = rarely, e2 = somewhat likely, e3 = likely, e4 = very likely and e5 = almost definite; the set of E for impact contains e1 = very low, e2 = low, e3 = moderate, e4 = high and e5 = very high; and the set of E for manageability is e1 = extremely easy to control, e2 = easy to control, e3 = medium to control, e4 = difficult to control and e5 = considerably difficult to control.

Regarding the evaluation matrix, rij represents the degree to which alternative ej satisfies the ith risk factor. For each GB risk factor, the membership function of each feature can be identified based on the collected data. For example, the P of factor HC2 (lack of experienced and qualified professionals about GB) shows that 3% of the responses evaluated the probability as very low, 19% as low, 31% as medium, 36% as high and 10% as very high. Thus, the membership function of P was calculated using

(4)0.03verylow+0.19low+0.31medium+0.36high+0.10veryhigh=0.031+0.192+0.313+0.364+0.105

The result could also be denoted in matrix form as

(5)(RiP)1×5=(R2P)1×5=(r21P,r22P,r23P,r24P,r25P)=(0.03,0.19,0.31,0.36,0.10)

Similarly, the membership functions of all GB risk factors were identified using the same procedure. Subsequently, the parameter values of the ith risk factor were calculated using

(6)Pi=(RiP)1×5×E5×1=j=15(rijP×ej)
(7)Ii=(RiI)1×5×E5×1=j=15(rijI×ej)
(8)Mi=(RiM)1×5×E5×1=j=15(rijM×ej)
where ej is the rating given to the ith risk factor, and represents the linguistic variable. In this research, e1 = rarely/very low/extremely easy to control; e2 = somewhat likely/low/easy to control; e3 = likely/moderate/medium to control; e4 = very likely/high/difficult to control and e5 = almost definite/very high/considerably difficult to control.

Risk significance (RS) was used to measure the significant levels of risk factors. The risk significance of the ith risk factor was calculated using

(9)RSi=Pi×Ii×Mi3

In addition, the authors calculated RA based on the traditional approach (Taroun, 2014). It might be interesting to compare the conventional approach with the proposed formula in this study. Also, this comparison provides a comprehensive view of the current GB risks in Vietnam. The RA of the ith risk factor was calculated using

(10)RAi=Pi×Ii

3.5.2 Evaluate GB risk groups

First, the weight of risk factors in each risk group must be identified using the MS ranking technique (Equation (3)). The weight vector of the tth risk group has the following form: Wt = {w1, w2, …, wk}, where k is the number of risk factors in the risk group. In addition, this model identified three weight vectors separately for P, I and M in the risk groups. The weight of risk factors within a risk group can be computed using

(11)wiP=Pii=1kPi
(12)wiI=Iii=1kIi
(13)wiM=Mii=1kMi

In the next step, the parameters of risk groups were calculated using the FSE model based on their membership functions, which were determined by their weight vector and the membership function of risk factors. The FSE commonly uses four methods to integrate the results. This model applies the fuzzy composition of the weight vector W and evaluation matrix R (D = W × R) to determine the membership function of the risk groups. As recommended by previous studies (Mu et al., 2014; Xu et al., 2010), this method is appropriate when considering numerous factors, and the variation in the weights is not significant. Therefore, this approach is suitable for this RA model because (1) the number of risk factors in risk groups is different and (2) the difference in the weight of risk factors is not significant. The membership functions of the tth risk group were computed using

(14)(DtP)1×5=(WtP)1×k×(RtP)k×5=(dt1P, dt2P,dt3P,dt4P,dt5P)
(15)dtjP=j=15i=1k(wiP×rijP)
(16)(DtI)1×5=(WtI)1×k×(RtI)k×5=(dt1I, dt2I,dt3I,dt4I,dt5I)
(17)dtjI=j=15i=1k(wiI×rijI)
(18)(DtM)1×5=(WtM)1×k×(RtM)k×5=(dt1M,dt2M,dt3M,dt4M,dt5M)
(19)dtjM=j=15i=1k(wiM×rijM)

After identifying the membership functions of the tth risk group, we then calculated the values of the corresponding parameters using

(20)PGt=(DtP)1×5×E5×1=j=15(dtjP×ej)
(21)IGt=(DtI)1×5×E5×1=j=15(dtjI×ej)
(22)MGt=(DtM)1×5×E5×1=j=15(dtjM×ej)
(23)RAGt=PGt×IGt
(24)RSGt=PGt×IGt×MGt3
where ej = 1, 2, 3, 4, 5.

3.5.3 Evaluate the overall risk

Similarly, we needed to calculate the weights of risk groups using the MS ranking technique to determine the overall risk parameters. The weight vector has the form WG = {wG1, wG2, …, wGq}. In this formula, q denotes the number of risk groups; thus, in this study, q = 6. The weight of the tth risk group was determined by

(25)wGtP=(i=1kPi)tt=1q(i=1kPi)t
(26)wGtI=(i=1kIi)tt=1q(i=1kIi)t
(27)wGtM=(i=1kMi)tt=1q(i=1kMi)t
where (i=1kPi)t indicates the total of P of k risk factors in group t; similarly, (i=1kIi)t denotes the sum of I of k risk factors in group t; and (i=1kMi)t indicates the total of M of k risk factors in group t.

Subsequently, the membership functions of the overall risk were identified using

(28)(DAllP)1×5=(WGP)1×q×(DGP)q×5=(dAll1P,dAll2P,dAll3P,dAll4P,dAll5P)
(29)dAlljP=j=15t=1q(wGtP×dtjP)
(30)(DAllI)1×5=(WGI)1×q×(DGI)q×5=(dAll1I,dAll2I,dAll3I,dAll4I,dAll5I)
(31)dAlljI=j=15t=1q(wGtI×dtjI)
(32)(DAllM)1×5=(WGM)1×q×(DGM)q×5=(dAll1M,dAll2M,dAll3M,dAll4M,dAll5M)
(33)dAlljM=j=15t=1q(wGtM×dtjM)
where (DGP)q×5, (DGI)q×5, and (DGM)q×5 are matrices that comprise q membership functions of risk groups (i.e. (DtP)1×5, (DtI)1×5, and (DtM)1×5) which are calculated in Section 3.5.2.

Finally, the parameters of the overall risk were determined:

(34)PAll=(DAllP)1×5×E5×1=j=15(dAlljP×ej)
(35)IAll=(DAllI)1×5×E5×1=j=15(dAlljI×ej)
(36)MAll=(DAllM)1×5×E5×1=j=15(dAlljM×ej)
(37)RAAll=PAll×IAll
(38)RSAll=PAll×IAll×MAll3
where sj = 1, 2, 3, 4, 5.

4. Results and findings

4.1 The assessment of each risk factor

First, the membership functions of the risk factors were determined (Table 4). For instance, the P of risk factor RR1 (“Complex planning approval and permit procedures”) shows that 5% of the responses evaluated the probability very low, 19% low, 29% medium, 31% high and 16% very high. Thus, the P membership function of RR1 was identified by Equations (4–5):

0.05verylow+0.19low+0.29medium+0.31high+0.16veryhigh=0.051+0.192+0.293+0.314+0.165
(R24P)1×5=(r241P,r242P,r243P,r244P,r245P)=(0.05,0.19,0.29,0.31,0.16)

Subsequently, the values of all parameters were calculated using Equations (6–10) (Table 5). Table 5 also presents the rank of the risk factors according to each parameter value. The following example illustrates the calculation of the parameters of factor RR1:

PRR1=j=15(sj×r24jP)=1×0.05+2×0.19+3×0.29+4×0.31+5×0.16=3.34
IRR1=j=15(sj×r24jI)=1×0.03+2×0.12+3×0.21+4×0.40+5×0.24=3.70
MRR1=j=15(sj×r24jM)=1×0.03+2×0.14+3×0.22+4×0.31+5×0.29=3.66
RARR1=PRR1×IRR1=3.52
RSRR1=PRR1×IRR1×MRR13=3.56

4.2 The assessment of risk groups

The first step identified the weight of the risk factors within each risk group (Table 6). For example, the weight of P for risk factor RR1 was calculated using Equation (11). Assuming that group RR (“Regulations risk”) has four risk factors, the denominator is the sum of the four elements:

WRR1P=PRR1/i=14PRRi=3.34(3.34+2.87+2.79+3.35)=0.270

Subsequently, the membership functions of the risk groups were determined using formulas (14–19). Table 7 presents the membership functions for all risk groups and the overall risk. For example, the membership function of P for the risk group MR (“Green material risk”) was calculated as follows:

(DMRP)1×5=(WMRP)1×3×(RMRP)3×5=[0.3080.3620.331]=[0.070.170.500.020.120.380.030.220.38    0.240.020.310.170.220.14]=(0.0390.1690.4170.2590.114)
where (WMRP)1×3 is a weight matrix of P for the group MR that contained the P weights of the 3 factors, and matrix (RMRP)3×5 is a membership function matrix composed of the P membership functions of the 3 factors in the MR.

The probability of risk group MR was calculated according to Equation (20):

PGMR=j=15(ej×dMRjP)=1×0.039+2×0.169+3×0.417+4×0.259+5×0.114=3.23

Similarly, the I and M membership functions of group MR were identified by applying Equations (16–19). Subsequently, Equations (21) and (22) were used to calculate I and M of this group:

IGMR=j=15(ej×dMRjI)=1×0.017+2×0.086+3×0.385+4×0.399+5×0.110=3.49
MGMR=j=15(ej×dMRjM)=1×0.013+2×0.186+3×0.432+4×0.311+5×0.065=3.25

Finally, the RA and RS values of the risk group MR were determined:

RAGMR=PGMR×IGMR=3.36
RSGMR=PGMR×IGMR×MGMR3=3.32

Table 8 lists parameter values of risk groups. To facilitate the comparison among risk groups, Table 8 also shows the rank of risk groups according to each parameter.

4.3 The assessment of the overall risk

To identify the overall risk, we first needed to calculate the weights for the risk groups. In this model, the number of risk groups was six. The results are listed in Table 6. For example, the weights of the group FR (“Financial risk”) were determined using Equations (25–27):

wGFRP=(i=15Pi)4t=16(i=1kPi)t=17.1898.19=0.175
wGFRI=(i=15Ii)4t=16(i=1kIi)t=18.61108.9=0.171
wGFRM=(i=15Mi)4t=16(i=1kMi)t=16.3297.99=0.167

These weights were then utilized to determine the membership functions of the overall risk. For instance, to determine the membership function of P for the overall risk, we calculated the fuzzy composition by multiplying the weight vector and evaluation matrix (Equation (28)):

(DAllP)1×5=(WGP)1×6×(DGP)6×5=[0.2320.1930.1750.1750.1260.098]×[0.0200.1770.3920.0330.1980.4040.0080.1280.386     0.3190.0880.2800.0830.3630.116 0.0160.1350.3870.0740.2250.3370.0390.1690.417    0.3380.1290.2550.1100.2590.114]=(0.0280.1700.3880.3080.104) 

Subsequently, the P of the overall risk can be calculated using Equation (34):

PAll=j=15(sj×dAlljP)=1×0.028+2×0.170+3×0.388+4×0.308+5×0.104=3.28

Similarly, the overall I value was identified using Equations (30), (31) and (35):

(DAllI)1×5=(WGI)1×6×(DGI)6×5=(0.0150.0870.3190.4130.168)
IAll=j=15(ej×dAlljI)=1×0.015+2×0.087+3×0.319+4×0.413+5×0.168=3.64

Using the same process, the value of M of the overall risk was determined by using Equations (32), (33) and (36):

(DAllM)1×5=(WGM)1×6×(DGM)6×5=(0.0140.1730.4420.2670.105)
MAll=j=15(ej×dAlljM)=1×0.014+2×0.173+3×0.442+4×0.267+5×0.105=3.28

Finally, RA and RS of the overall risk were obtained using Equations (37) and (38):

RAAll=PAll×IAll=3.38×4.21=3.46
RSAll=PAll×IAll×MAll3=3.40

This result indicated that risks in GB projects in Vietnam are relatively high.

5. Discussion

This study proposed a practical RA model for GB projects and then adopted it to assess the current GB risks in Vietnam. The result implied that risk in GB projects is relatively high, with the significance of the overall risk being 3.40. This result is generally lower than expected because previous studies have claimed that GB risks are very high (Hwang et al., 2017b; Zhao et al., 2016). However, this does not mean that GB risks in Vietnam are less critical because respondents’ evaluations are somewhat relative and depend on subjective factors. Therefore, this section concentrates on analyzing risk groups and top risk factors based on their RS rankings.

5.1 Risk group assessment

This section discusses the assessment results of risk groups. This provides an overview of the current GB risks in Vietnam.

  1. Human resource risk in the design phase (HD): RS = 3.55

Human resource risk during the design phase was the most critical risk group. This is also the risk group with the highest possibility and the most significant impact (Table 8). This result indicates that qualified professionals play a crucial role in GB projects, especially during the design phase (Hwang et al., 2017a). This is understandable because GBs are complex buildings and require various techniques and innovations in design. This finding reflects a common problem in Vietnam: the lack of GB professionals. This result is also aligned with the literature because the shortage of GB professionals has been recognized as a significant barrier for GB development in previous studies (Hwang et al., 2017a; Qin et al., 2016). In the current situation in Vietnam, providing training courses on GBs for construction practitioners is considered a suitable solution for the construction industry.

  1. Financial risk (FR): RS = 3.47

Financial risk is also a critical risk group in GB projects and is ranked second. Finance is a fundamental problem and plays an essential role in construction projects, particularly in large and complex construction projects. Thus, for GB projects, which are considered complicated, the finance problem is even more crucial compared with traditional projects. This is understandable because GBs adopt novel materials and the latest construction technologies; therefore, cost estimation is challenging and regularly faces uncertainty (Hwang et al., 2017b). Moreover, the values of GBs include various intangible benefits (e.g. improving the indoor environment and business advantages) that are not straightforward to evaluate monetarily (Guan et al., 2020).

  1. Regulation risk (RR): RS = 3.40

In the third position, the regulation risk is a significant problem in the implementation process of GB projects. Indeed, implementing GB projects is much more complicated and involves more procedures than traditional projects. For example, GB projects usually apply green solutions (e.g. solar photovoltaic and rain harvesting systems), resulting in lengthy and complicated approval-permit procedures (Qin et al., 2016; Zhao et al., 2016). Furthermore, approval frequently requires the participation of various stakeholders. Thus, this problem can cause significant delays in the implementation process, leading to the failure of GB projects.

  1. Human resources and technical risks in the construction phase (HC): RS = 3.33

The risk group ranked fourth is human resources and technical risks in the construction phase. Similar to the design phase, the construction phase of GB projects also requires experienced professionals to handle problems at construction sites (Hwang et al., 2017a). Therefore, the lack of qualified managers, engineers and workers can significantly affect the costs, schedules and quality of GB projects, even in developed countries such as Singapore (Hwang et al., 2017b; Zhao et al., 2016). In the current situation of Vietnam, the most reasonable solution to develop the GB workforce is to provide training courses for construction practitioners.

  1. Green material risk (MR): RS = 3.32

The fifth position was a common problem that recently received much attention from construction practitioners in GB projects: green material risks. GB frequently uses novel and innovative materials that aim to be more environmentally friendly (Nguyen et al., 2017). In general, green materials (e.g. unburnt bricks or organic paints) are produced using different methods compared with traditional materials. Nevertheless, this is also why many construction practitioners doubt the quality of green materials. There are still many issues related to the quality, certification and supply of green materials in practice. Indeed, such problems can significantly affect GB projects and investors’ trust, thereby somewhat restraining GB development. Similarly, several previous studies also claimed that green material risk is a substantial hindrance to GB development (Nguyen et al., 2017; Shi et al., 2013).

  1. Performance risk in the operation phase (PO): RS = 3.30

Finally, the risk in the operation phase is also worth considering. Indeed, by investing in GB projects, owners hope there could be benefits for their business (e.g. saving energy and water and improving the indoor environment). However, many practitioners claim that the performance of GBs frequently does not meet initial expectations (Hwang et al., 2017a; Qin et al., 2016). Simulation tools are usually used to quantify GB performance at the beginning of projects. Based on the analysis results, investors decide whether to invest in GBs. Thus, performance problems in the operation phase could temper investors’ beliefs and consequently restrict the development of GBs. This is also a common problem in GB projects, as mentioned in previous studies (Ismael and Shealy, 2018; El-Sayegh et al., 2021).

5.2 The most critical risk factors

This section discusses the top-10 risk factors based on RS values. This finding may provide insight into the risks in GB projects and benefit construction practitioners in the RM process.

  1. HD4 (“Lack experience of GB designers”): RS = 3.64

The most critical risk factor is HD4, which relates to GB designers’ lack of experience. This indicates that the incapacity of GB designers is a major problem in the design phase of GB projects in Vietnam (Nguyen et al., 2021). This research also revealed that this risk factor has the greatest impact (impact level ranked first) and is a common problem in Vietnam (probability of occurrence ranked third). This result is understandable because GB projects frequently require qualified designers to handle sustainable designs. This outcome is in line with the GB literature because this risk factor has also been evaluated in previous studies (Ismael and Shealy, 2018). Notably, Qin et al. (2016) rated this factor as the third critical risk in China. Fortunately, the risk manageability of this factor was ranked 8th, indicating that we can still mitigate this risk (e.g. by training GB designers).

  1. HD5 (“Owners lack determination when implementing GB projects”): RS = 3.61

The second position belonged to HD5, which reflected an issue in GB projects in Vietnam: if owners face considerable obstacles in implementing GB projects, they may give up. Interestingly, this factor does not have a high probability of occurrence (probability of occurrence rated 15th), but its impact is relatively substantial (impact level ranked sixth). Notably, managing this factor is very difficult (risk manageability ranked second), which makes this risk factor critical. If we used the traditional approach to assess (only considering I and p) this factor would be ranked 12th. However, this factor became more severe as we examined risk manageability. This finding provides insight and could help practitioners develop a suitable strategy to deal with this factor in implementing GB projects. This result aligns with the research of Nguyen et al. (2021), who rated this risk factor as the most critical risk factor. Indeed, this problem could restrain the development of GBs; thus, enhancing owners’ awareness and knowledge could mitigate this risk (Nguyen et al., 2021).

  1. HD3 (“Project teams lack design management experience”): RS = 3.57

The third position is the factor HD3, which refers to the crucial coordinating role of the project team in the design phase of GB projects. This finding is aligned with results in the literature, as this factor was also significant in previous studies (El-Sayegh et al., 2021; Yang et al., 2016). Notably, this risk factor was the most common risk in Vietnam (probability of occurrence ranked first), whereas its impact was ranked 17th. In addition, mitigating this risk factor is somewhat challenging in developing countries such as Vietnam, as demonstrated by its sixth rated RM. The most feasible solution is to train construction practitioners about GB projects, especially project manager positions.

  1. FR5 (“Price inflation of construction materials and labor”): RS = 3.57

In the fourth position, the risk factor FR5 refers to the uncertainty of green materials and labor price in implementing GB projects, which has received significant attention in previous studies (Hwang et al., 2017b). Indeed, this problem could lead to cost overruns in practice and the consequent failure of GB projects. The results showed that the probability and impact of this factor were rated 10th and 11th, respectively. Notably, managing this risk factor is challenging (risk manageability is ranked fourth), making this risk highly critical. This revealed that GB projects still face inflation risks, even though Vietnam’s inflation rate has been somewhat stable in the past few years. This is understandable because the proportion of the cost for green materials and skilled labor in GB projects is much higher than in traditional projects.

  1. RR1 (“Complex planning approval and permit procedures”): RS = 3.56

Complex planning approval and permit procedures is also a critical risk factor that is difficult to control. This factor reflects the inherent issue that procedures in GB projects are more complex than conventional projects. This is reasonable because GB applies green solutions; thus, approval permit procedures are frequently prolonged and complicated (Zhao et al., 2016). Consequently, this issue could lead to delays in the implementation of GB projects. Moreover, project teams tend to handle this problem by speeding up the schedule, which could lead to failure or low-quality projects (Zou and Couani, 2012). Notably, although this risk factor is neither highly common nor significantly influential for GB projects (p and I were ranked 14th and 12th, respectively), the difficulty in controlling this factor makes it more severe (RM rated third). This is the most critical risk factor in China (Qin et al., 2016). This revealed that the severity of this risk might depend on the current laws in each country’s construction industry.

  1. FR4 (“Underestimation of initial investment cost”): RS = 3.54

One of the most impactful factors in GB projects is the “Underestimation of the initial investment cost” (impact level ranked third). Moreover, this risk is still a common problem in Vietnam, as shown by its probability of occurrence rated seventh. This revealed that project teams frequently underrated the initial cost of GB projects, such as green materials, technology and GB consultant costs (Hwang et al., 2017a). This result is in line with the literature, as this risk factor had a high evaluation in developed countries such as Singapore (Hwang et al., 2017a). Notably, the initial investment cost is considered a significant obstacle for the development of GBs in Vietnam (Nguyen et al., 2017). Fortunately, we could still mitigate this risk by increasing the practitioners’ awareness. This may be why the RM of this factor was rated 10th.

  1. HC3 (“Project management consultant and/or project team lacks experience in construction management of GB projects”): RS = 3.53

Another common risk in Vietnam is HC3, with the probability of occurrence and impact level ranked fourth. Therefore, considering only the probability of occurrence and impact level, this risk factor would be ranked second. This result is aligned with previous studies that evaluated this risk factor as high (El-Sayegh et al., 2021; Yang et al., 2016). This reflects a critical problem in Vietnam: a lack of qualified project managers who have experience in GB projects. Fortunately, the RM of this risk factor was ranked 13th; consequently, this factor became less severe. Indeed, this risk can be mitigated by training practitioners and by choosing capable project managers for GB projects.

  1. RR4 (“Delay in decision-making”): RS = 3.52

In the eighth position is the risk factor RR4, which signifies the issues in decision-making in GB projects. This problem is related to the complexity of GB projects and the complicated procedures involved in the approval process. The results also showed that this risk factor is relatively common (probability of occurrence rated 12th) and has a significant impact (impact level ranked seventh) in GB projects. Moreover, managing this risk factor is also a challenge reflected by its RM, which is ranked fifth. This finding is aligned with results in the literature, as this factor was evaluated as the second most critical factor in Singapore (Zhao et al., 2016).

  1. MR2 (“Limited availability and reliability of green materials and suppliers”): RS = 3.52

Another critical risk factor is MR2, which is related to the limited availability and reliability of green materials and suppliers. Although the impact level of this factor is ranked 14th, this is a prevalent problem (probability of occurrence rated fifth). This is unsurprising as conventional materials still dominate and outnumber green materials in the construction industry, especially in developing countries such as Vietnam. Moreover, there are still some problems and uncertainty about the quality and certification of green materials that can reduce user confidence. In addition, this problem is not easy to mitigate (RM ranked ninth) because it depends on the development of technologies and objective factors. According to previous studies, the shortage of green material supplies is a critical barrier to the development of GBs (Nguyen et al., 2017).

  1. HD2 (“Inefficient communication and coordination between parties”): RS = 3.49

Finally, in 10th position is the risk factor HD2, with a relatively high impact (impact level ranked fifth). This risk reflects a significant problem: communication and coordination among stakeholders are still ineffective, particularly between GB consultants and other consultants. According to previous studies, collaboration among parties could improve the quality of work and speed up the progress; thereby, stakeholder collaborations are vital in GB projects (Hwang et al., 2017a; Zhao et al., 2016). Indeed, collaboration is essential for any construction project, specifically in complex construction projects. Thus, for distinctive projects such as GB projects, the coordinator role of GB consultants is even more crucial (Zhao et al., 2016). Fortunately, this factor’s probability of occurrence and RM were ranked 13th and 11th, respectively. This implies that practitioners can still mitigate this risk using a suitable RM strategy. Project management consultants play an essential role in addressing this risk. Thus, investors should choose capable project management consultants experienced in GB projects.

6. Conclusion

GB is an inevitable trend in sustainable construction to mitigate adverse impacts on the environment. However, GB projects frequently face many risks during implementation. In this study, we developed an RA model for GB projects based on mean scores and the FSE method to ease this problem. Notably, this model evaluates risk factors based on three features: impact level, probability of occurrence and RM. Furthermore, this research applied the proposed model to evaluate the risks in GB projects in Vietnam by surveying practitioners.

First, this study has provided a novel and reliable model to evaluate GB risks in the GB literature. Thus, this research could be a useful reference for future research to examine GB risks in more depth. In addition, the model could be a helpful tool for construction professionals in the RM process of GB projects. As a second contribution, this research applied the proposed model to thoroughly assess GB risks in Vietnam. The results revealed that risks in implementing GB projects in Vietnam could be regarded as “relatively high”, which implied RM is necessary. Also, this study indicated the top-five critical risk factors are “lack experience of GB designers”, “owners lack determination as implementing GB projects”, “project teams lack design management experience”, “price inflation of green materials and labor” and “complex planning approval and permit procedures”. Regarding risk groups, the most critical risk group is “Human resource risk in the design phase”. Furthermore, we have discussed the assessment results of risk groups and the top risk factors to provide insight into the current risks in GB projects in Vietnam. This could facilitate practitioners in the RM process, thereby, helping to enhance the development of GBs in Vietnam.

Despite the authors’ efforts, this study has some limitations. First, the data used in this research were collected from a developing country, Vietnam. Therefore, caution should be exercised when generalizing the results to other developing countries and should not be generalized to developed countries. Nevertheless, the proposed model can be replicated to assess risk in conventional construction projects, other countries and other sectors. Second, the respondents evaluated risk factors based on their knowledge and individual judgment; thus, the subjectivity of the collected data is inevitable. However, this problem is common in research involving questionnaire surveys or participants’ subjective assessments. Moreover, the RA process regularly depends on specific project teams and GB projects, especially as this model considers the RM aspect. Thus, practitioners should apply the proposed model to assess risks in specific GB projects based on their team and use this research result as a reference.

Future studies should compare risks in GB projects in different countries, especially between developing and developed countries. In addition, exploring the relationship between RM and project performance (e.g. cost, schedule and customer satisfaction) is a promising research direction. Also, it may be helpful for practitioners to investigate how to reduce GB risks through practical measures.

Figures

The overall research framework

Figure 1

The overall research framework

Risk factors in GB projects

NCodeRisk factors
HCComponent 1: Human resource and technical risk in the construction phase
1HC1Lack of experience of contractors/subcontractors in GB construction[1], [2], [4–7], [9]
2HC2Lack of professionals who are experienced and qualified about GB[1–3], [5], [6], [9]
3HC3Project management consultant and/or project team lacks experience in construction management of GB projects[6], [7], [9]
4HC4Unfamiliarity with green materials and construction process[2]
5HC5Difficulty in the selection of contractors providing GB construction services[4], [5], [9]
6HC6Improper quality control process for GB projects[3], [5], [8], [9]
7HC7Detail design/green specifications are unclear or possible errors[1–3], [9]
POComponent 2: Performance risk in the operation phase
8PO1The performance of green solutions is not achieved as the original goal[2], [4–6]
9PO2Lack of adequate GB maintenance[5], [6]
10PO3Lack of experienced management agency in the operation phase[5–7]
11PO4Project evaluation results did not reach the expected GB standard[4–6], [9]
12PO5The lack of cooperation among the parties involved in the GB trial operation stage[6]
13PO6Difficulties in operating green solutions[10]
HDComponent 3: Human resource risk in the design phase
14HD1Late involvement of GB consultants in the design phase[10]
15HD2Inefficient communication and coordination between parties[1], [2], [5]
16HD3Project teams lack design management experience in GB projects[1], [4], [9]
17HD4Lack of experience of designers about GB[4–7], [9]
18HD5Owners lack determination as implementing GB projects[10]
FRComponent 4: Financial risk
19FR1The payback period of GB projects may be longer than conventional projects[5]
20FR2High costs of sustainable materials and equipment[3], [6], [9]
21FR3Lack of accurate estimation of investment and long-term return[5], [6], [8], [10]
22FR4Underestimation of initial investment cost[2], [5]
23FR5Price inflation of construction materials and labor[1–3], [5–9]
RRComponent 5: Regulations risk
24RR1Complex planning approval and permit procedures[1], [5]
25RR2Change in local regulations/governmental policies that affect the implementation of GB projects[3], [4], [5], [7], [9]
26RR3The regulations on duties, powers, and dispute resolution in the GB design contract are unclear[1], [2], [7], [8]
27RR4Delay in decision-making[1]
MRComponent 6: Green material risk
28MR1Green material quality problems[1], [7]
29MR2Limited availability and reliability of green materials and products suppliers[1–3], [5–9]
30MR3No general standards for testing the quality and origin of green materials[10]

Likert scales for risk assessment

ScalesImpact levelOccurrence probabilityRisk manageability
1Very lowRarely (<20%)Extremely easy to control
2LowSomewhat likely (20–40%)Easy to control
3ModerateLikely (40–60%)Medium to control
4HighVery likely (60–80%)Difficult to control
5Very highAlmost definite (>80%)Considerably difficult to control

The demographic background of respondents

Demographic characteristics FrequencyPercent (%)
Company scalesInternational3458.62
National2034.48
Multi-cities/provinces35.17
Within a city/province11.72
Project rolesOwners1220.69
Architects712.07
Engineering designers23.45
GB consultant1932.76
PM consultant813.79
Contractors58.62
Other58.62
Position in organizationDirectorial level1424.14
Managerial level1831.03
Expert level2441.38
Other23.45
Year of experience3–5 years2237.93
6–10 years813.79
11–15 years1118.97
More than 15 years1729.31
GB knowledgeExpert2339.66
Familiar3560.34
(n = 58)

The membership functions of risk factors

NCodeMembership function of PMembership function of IMembership function of M
HCGroup 1: Human resource and technical risk in the construction phase
1HC1(0.03, 0.19, 0.31, 0.36, 0.10)(0.03, 0.10, 0.33, 0.40, 0.14)(0.02, 0.17, 0.53, 0.17, 0.10)
2HC2(0.03, 0.19, 0.36, 0.31, 0.10)(0.00, 0.05, 0.24, 0.47, 0.24)(0.00, 0.17, 0.47, 0.26, 0.10)
3HC3(0.00, 0.09, 0.43, 0.36, 0.12)(0.00, 0.07, 0.28, 0.45, 0.21)(0.00, 0.12, 0.55, 0.22, 0.10)
4HC4(0.00, 0.10, 0.43, 0.36, 0.10)(0.00, 0.09, 0.45, 0.40, 0.07)(0.00, 0.21, 0.53, 0.22, 0.00)
5HC5(0.02, 0.26, 0.45, 0.24, 0.03)(0.02, 0.17, 0.50, 0.24, 0.07)(0.02, 0.26, 0.43, 0.28, 0.02)
6HC6(0.03, 0.24, 0.38, 0.26, 0.09)(0.02, 0.21, 0.29, 0.38, 0.10)(0.00, 0.24, 0.50, 0.21, 0.05)
7HC7(0.03, 0.19, 0.38, 0.33, 0.07)(0.02, 0.02, 0.34, 0.43, 0.19)(0.00, 0.17, 0.50, 0.26, 0.07)
POGroup 2: Performance risk in the operation phase
8PO1(0.00, 0.22, 0.38, 0.36, 0.03)(0.00, 0.16, 0.26, 0.52, 0.07)(0.00, 0.17, 0.47, 0.31, 0.05)
9PO2(0.00, 0.17, 0.34, 0.38, 0.10)(0.00, 0.02, 0.40, 0.43, 0.16)(0.02, 0.24, 0.43, 0.22, 0.09)
10PO3(0.02, 0.14, 0.40, 0.33, 0.12)(0.00, 0.05, 0.43, 0.36, 0.16)(0.00, 0.19, 0.50, 0.21, 0.10)
11PO4(0.07, 0.24, 0.43, 0.19, 0.07)(0.02, 0.09, 0.36, 0.36, 0.17)(0.00, 0.21, 0.59, 0.16, 0.05)
12PO5(0.03, 0.19, 0.52, 0.16, 0.10)(0.02, 0.02, 0.40, 0.43, 0.14)(0.02, 0.21, 0.52, 0.17, 0.09)
13PO6(0.09, 0.24, 0.36, 0.24, 0.07)(0.03, 0.12, 0.36, 0.40, 0.09)(0.07, 0.28, 0.34, 0.22, 0.09)
HDGroup 3: Human resource risk in the design phase
14HD1(0.00, 0.09, 0.60, 0.24, 0.07)(0.00, 0.09, 0.29, 0.52, 0.10)(0.02, 0.14, 0.36, 0.38, 0.10)
15HD2(0.00, 0.14, 0.45, 0.34, 0.07)(0.00, 0.07, 0.24, 0.48, 0.21)(0.02, 0.09, 0.50, 0.34, 0.05)
16HD3(0.00, 0.07, 0.34, 0.45, 0.14)(0.05, 0.07, 0.24, 0.47, 0.17)(0.02, 0.07, 0.48, 0.34, 0.09)
17HD4(0.02, 0.09, 0.31, 0.41, 0.17)(0.00, 0.07, 0.26, 0.40, 0.28)(0.00, 0.16, 0.45, 0.28, 0.12)
18HD5(0.02, 0.26, 0.24, 0.36, 0.12)(0.05, 0.10, 0.16, 0.36, 0.33)(0.00, 0.16, 0.21, 0.43, 0.21)
FRGroup 4: Financial risk
19FR1(0.02, 0.07, 0.36, 0.40, 0.16)(0.02, 0.05, 0.33, 0.47, 0.14)(0.02, 0.21, 0.52, 0.19, 0.07)
20FR2(0.00, 0.14, 0.36, 0.38, 0.12)(0.00, 0.09, 0.36, 0.41, 0.14)(0.02, 0.22, 0.45, 0.21, 0.10)
21FR3(0.02, 0.19, 0.45, 0.24, 0.10)(0.02, 0.09, 0.28, 0.40, 0.22)(0.03, 0.17, 0.48, 0.22, 0.09)
22FR4(0.02, 0.14, 0.34, 0.38, 0.12)(0.02, 0.03, 0.28, 0.41, 0.26)(0.00, 0.12, 0.48, 0.29, 0.10)
23FR5(0.02, 0.14, 0.43, 0.28, 0.14)(0.02, 0.07, 0.33, 0.38, 0.21)(0.03, 0.07, 0.34, 0.36, 0.19)
RRGroup 5: Regulations risk
24RR1(0.05, 0.19, 0.29, 0.31, 0.16)(0.03, 0.12, 0.21, 0.40, 0.24)(0.03, 0.14, 0.22, 0.31, 0.29)
25RR2(0.07, 0.38, 0.26, 0.19, 0.10)(0.00, 0.22, 0.14, 0.40, 0.24)(0.00, 0.17, 0.24, 0.26, 0.33)
26RR3(0.16, 0.21, 0.40, 0.19, 0.05)(0.05, 0.10, 0.43, 0.33, 0.09)(0.03, 0.26, 0.47, 0.14, 0.10)
27RR4(0.03, 0.14, 0.40, 0.31, 0.12)(0.00, 0.05, 0.31, 0.45, 0.19)(0.00, 0.09, 0.52, 0.31, 0.09)
MRGroup 6: Green material risk
28MR1(0.07, 0.17, 0.50, 0.24, 0.02)(0.00, 0.09, 0.45, 0.43, 0.03)(0.02, 0.21, 0.50, 0.26, 0.02)
29MR2(0.02, 0.12, 0.38, 0.31, 0.17)(0.02, 0.07, 0.33, 0.36, 0.22)(0.00, 0.16, 0.40, 0.34, 0.10)
30MR3(0.03, 0.22, 0.38, 0.22, 0.14)(0.03, 0.10, 0.38, 0.41, 0.07)(0.02, 0.19, 0.40, 0.33, 0.07)

The parameters of risk factors

NCodePossibility (P)Impact (I)Manageability (M)Risk assessment (RA)Risk significant (RS)
ValueRankValueRankValueRankValueRankValueRank
HCGroup 1: Human resource and technical risk in the construction phase
1HC13.28173.52233.13203.4203.3121
2HC23.23183.9023.29123.55113.4612
3HC33.5143.8343.27133.6723.537
4HC43.4383.48243.04283.45193.3121
5HC53.00253.17303.05273.08293.0729
6HC63.14233.33283.07263.23263.1826
7HC73.22193.7593.23163.47163.3918
POGroup 2: Performance risk in the operation phase
8PO13.17223.53223.24153.35223.3121
9PO23.38113.7683.12223.5693.4115
10PO33.4293.63183.22173.52143.4214
11PO42.95283.57213.08243.25243.1925
12PO53.11243.68153.13213.38213.323
13PO62.96273.4252.98303.17283.1128
HDGroup 3: Human resource risk in the design phase
14HD13.29163.63193.4073.46173.4413
15HD23.34133.8353.31113.5873.4910
16HD33.6613.64173.4163.6543.573
17HD43.6233.9213.3983.7713.641
18HD53.3153.8263.7223.55123.612
FRGroup 4: Financial risk
19FR13.6423.69133.11233.6633.4711
20FR23.4863.6203.15183.54133.416
21FR33.21203.74103.14193.46183.3519
22FR43.4473.8633.34103.6453.546
23FR53.41103.72113.5843.5693.574
RRGroup 5: Regulations risk
24RR13.34143.7123.6633.52153.565
25RR22.87293.66163.7513.24253.4017
26RR32.79303.31293.02293.04303.0330
27RR43.35123.7873.4353.5693.528
MRGroup 6: Green material risk
28MR12.97263.4263.08253.18273.1427
29MR23.4953.69143.3893.5963.529
30MR33.19213.36273.27143.27233.2724

Weights of risk factors and risk groups

NCodeWeightsNCodeWeights
PIMPIM
HC0.2320.2290.225 FR0.1750.1710.167
1HC10.1440.1410.14219FR10.2120.1980.191
2HC20.1420.1560.14920FR20.2030.1930.193
3HC30.1540.1530.14821FR30.1870.2010.192
4HC40.1500.1390.13822FR40.2000.2070.205
5HC50.1320.1270.13823FR50.1980.2000.219
6HC60.1380.1330.139
7HC70.1410.1500.146
PO0.1930.1980.192 PR0.1260.1330.141
8PO10.1670.1640.17324PR10.2700.2560.264
9PO20.1780.1740.16625PR20.2320.2530.271
10PO30.1800.1680.17226PR30.2260.2290.218
11PO40.1550.1660.16427PR40.2710.2620.247
12PO50.1640.1710.167
13PO60.1560.1580.159
HD0.1750.1730.176 MR0.0980.0960.099
14HD10.1910.1930.19728MR10.3080.3250.317
15HD20.1940.2030.19229MR20.3620.3530.347
16HD30.2130.1930.19830MR30.3310.3220.336
17HD40.2100.2080.197
18HD50.1920.2030.216

The membership functions of risk groups and the overall risk

CodeMembership function of PMembership function of IMembership function of M
HC(0.020, 0.177, 0.392, 0.319, 0.088)(0.012, 0.098, 0.342, 0.400, 0.150)(0.006, 0.190, 0.502, 0.232, 0.068)
PO(0.033, 0.198, 0.404, 0.280, 0.083)(0.011, 0.075, 0.370, 0.417, 0.133)(0.018, 0.216, 0.476, 0.216, 0.078)
HD(0.008, 0.128, 0.386, 0.363, 0.116)(0.020, 0.080, 0.238, 0.445, 0.22)(0.012, 0.125, 0.396, 0.356, 0.116)
FR(0.016, 0.135, 0.387, 0.338, 0.129)(0.016, 0.066, 0.315, 0.413, 0.195)(0.020, 0.155, 0.451, 0.257, 0.112)
RR(0.074, 0.225, 0.337, 0.255, 0.110)(0.019, 0.122, 0.269, 0.397, 0.193)(0.014, 0.162, 0.354, 0.259, 0.21)
MR(0.039, 0.169, 0.417, 0.259, 0.114)(0.017, 0.086, 0.385, 0.399, 0.110)(0.013, 0.186, 0.432, 0.311, 0.065)
All(0.028, 0.17, 0.388, 0.308, 0.104)(0.015, 0.087, 0.319, 0.413, 0.168)(0.014, 0.173, 0.442, 0.267, 0.105)

The parameters of risk groups and the overall risk

CodePIMRARS
ValueRankValueRankValueRankValueRankValueRank
HC3.2733.5853.1653.4233.334
PO3.1853.643.1363.3843.36
HD3.4513.7713.4523.6113.551
FR3.4423.7223.2733.5823.472
RR3.1163.6233.4913.3653.43
MR3.2343.4963.2543.3663.325
All3.28 3.64 3.28 3.46 3.40

References

Ahmad, T., Thaheem, M.J. and Anwar, A. (2016), “Developing a green-building design approach by selective use of systems and techniques”, Architectural Engineering and Design Management, Vol. 12 No. 1, pp. 29-50.

Ahmad, T., Aibinu, A.A. and Stephan, A. (2019), “Managing green building development – a review of current state of research and future directions”, Building and Environment, Vol. 155, pp. 83-104, Elsevier.

Akintoye, A. (2000), “Analysis of factors influencing project cost estimating practice”, Construction Management and Economics, Taylor & Francis, Vol. 18 No. 1, pp. 77-89.

Akter, M., Jahan, M., Kabir, R., Karim, D.S., Haque, A., Rahman, M. and Salehin, M. (2019), “Risk assessment based on fuzzy synthetic evaluation method”, Science of The Total Environment, Elsevier, Vol. 658, pp. 818-829.

Aven, T., Vinnem, J.E. and Wiencke, H.S. (2007), “A decision framework for risk management, with application to the offshore oil and gas industry”, Reliability Engineering and System Safety, Elsevier, Vol. 92 No. 4, pp. 433-448.

BCI Economics (2014), Green Building Market Report Australia/New Zealand 2014, BCI Economics, Sydney.

Chua, S.C. and Oh, T.H. (2011), “Green progress and prospect in Malaysia”, Renewable and Sustainable Energy Reviews, Elsevier, Vol. 15 No. 6, pp. 2850-2861.

Darko, A. and Chan, A.P.C. (2016), “Critical analysis of green building research trend in construction journals”, Habitat International, Vol. 57, pp. 53-63.

Dean, B., Dulac, J., Petrichenko, K. and Graham, P. (2016), Towards Zero-Emission Efficient and Resilient buildings.: Global Status Report, Global Alliance for Buildings and Construction (GABC), Paris.

Dikmen, I., Budayan, C., Talat Birgonul, M. and Hayat, E. (2018), “Effects of risk attitude and controllability assumption on risk ratings: observational study on international construction project risk assessment”, Journal of Management in Engineering, American Society of Civil Engineers, Vol. 34 No. 6, pp. 1-12.

Dodge Data and Analytics (2018), World Green Building Trends 2018 - Smart Market Report, Smart Market Report, U.S. Green Building Council, Washington DC, available at: www.construction.com.

El-Sayegh, S.M., Manjikian, S., Ibrahim, A., Abouelyousr, A. and Jabbour, R. (2021), “Risk identification and assessment in sustainable construction projects in the UAE”, International Journal of Construction Management, Vol. 21 No. 4, pp. 327-336, doi: 10.1080/15623599.2018.1536963.

Guan, L., Abbasi, A. and Ryan, M.J. (2020), “Analyzing green building project risk interdependencies using Interpretive Structural Modeling”, Journal of Cleaner Production, Vol. 256, p. 120372, Elsevier.

Hassan, M.E., Kandil, A., Senouci, A. and Al-Derham, H. (2016), “Organizational behavior attributes and sustainable construction adoption: an econometric analysis using data from Qatar”, Journal of Construction Engineering and Management, Vol. 142 No. 12, 05016016, American Society of Civil Engineers.

Hsu, T.H. and Yang, T.S. (1997), “The application of fuzzy synthetic decision to the human resource management”, Fu Jen Management Review, Vol. 4 No. 2, pp. 85-100.

Hwang, B.-G., Shan, M., Phua, H. and Chi, S. (2017a), “An exploratory analysis of risks in green residential building construction projects: the case of Singapore”, Sustainability, Multidisciplinary Digital Publishing Institute, Vol. 9 No. 7, p. 1116.

Hwang, B.-G., Shan, M. and Supa’at, N.N.B. (2017b), “Green commercial building projects in Singapore: critical risk factors and mitigation measures”, Sustainable Cities and Society, Elsevier, Vol. 30, pp. 237-247.

Ismael, D. and Shealy, T. (2018), “Sustainable construction risk perceptions in the Kuwaiti construction industry”, Sustainability, Multidisciplinary Digital Publishing Institute, Vol. 10 No. 6, p. 1854.

Kibert, C.J. (2016), Sustainable Construction: Green Building Design and Delivery, John Wiley & Sons, Hoboken, New Jersey.

Kientzel, J. and Kok, G. (2011), “Environmental assessment methodologies for commercial buildings: an elicitation study of U.S. Building professionals’ beliefs on leadership in energy and environmental design (LEED)”, Sustainability, Molecular Diversity Preservation International, Vol. 3 No. 12, pp. 2392-2412.

Latham, M. (1994), Constructing the Team: Final Report of the Government/industry Review of Procurement and Contractual Arrangements in the UK Construction Industry, Hmso, London.

Li, Y., Zhang, X., Ding, G. and Feng, Z. (2016), “Developing a quantitative construction waste estimation model for building construction projects”, Resources, Conservation and Recycling, Elsevier, Vol. 106, pp. 9-20.

Ma, J. and Kremer, G.E.O. (2015), “A fuzzy logic-based approach to determine product component end-of-life option from the views of sustainability and designer’s perception”, Journal of Cleaner Production, Elsevier, Vol. 108, pp. 289-300.

Mu, S., Cheng, H., Chohr, M. and Peng, W. (2014), “Assessing risk management capability of contractors in subway projects in mainland China”, International Journal of Project Management, Elsevier, Vol. 32 No. 3, pp. 452-460.

Nguyen, H.D. and Macchion, L. (2022), “Risk management in green building: a review of the current state of research and future directions”, Environment, Development and Sustainability. doi: 10.1007/s10668-022-02168-y.

Nguyen, H.-T.T., Skitmore, M., Gray, M., Zhang, X. and Olanipekun, A.O. (2017), “Will green building development take off? An exploratory study of barriers to green building in Vietnam”, Resources, Conservation and Recycling, Elsevier, Vol. 127 No. August, pp. 8-20.

Nguyen, H.D., Do, Q.N.H. and Macchion, L. (2021), Influence of Practitioners’ Characteristics on Risk Assessment in Green Building Projects in Emerging Economies: A Case of Vietnam", Engineering, Construction and Architectural Management, Vols ahead-of-print, doi: 10.1108/ECAM-05-2021-0436.

Nunnally, J.C. (1994), Psychometric Theory 3E, Tata McGraw-Hill Education, New York.

Pedrycz, W., Ekel, P. and Parreiras, R. (2011), Fuzzy Multicriteria Decision-Making: Models, Methods and Applications, John Wiley & Sons, Hoboken, New Jersey.

Qin, X., Mo, Y. and Jing, L. (2016), “Risk perceptions of the life-cycle of green buildings in China”, Journal of Cleaner Production, Vol. 126, Elsevier, pp. 148-158.

Rafindadi, A.D., Mikić, M., Kovačić, I. and Cekić, Z. (2014), “Global perception of sustainable construction project risks”, Procedia-Social and Behavioral Sciences, Elsevier, Vol. 119 No. Williams 1995, pp. 456-465.

Retzlaff, R. (2010), “Developing policies for green buildings: what can the United States learn from The Netherlands?”, Sustainability: Science, Practice and Policy, Taylor & Francis, Vol. 6 No. 1, pp. 28-38.

Robichaud, L.B. and Anantatmula, V.S. (2011), “Greening project management practices for sustainable construction”, Journal of Management in Engineering, American Society of Civil Engineers, Vol. 27 No. 1, pp. 48-57.

Shi, Q., Zuo, J., Huang, R., Huang, J. and Pullen, S. (2013), “Identifying the critical factors for green construction – an empirical study in China”, Habitat International, Vol. 40, pp. 1-8, doi: 10.1016/j.habitatint.2013.01.003.

Tao, X. and Xiang-Yuan, S. (2018), “Identification of risk in green building projects based on the perspective of sustainability”, IOP Conference Series: Materials Science and Engineering, Vol. 439, p. 32053.

Taroun, A. (2014), “Towards a better modelling and assessment of construction risk: insights from a literature review”, International Journal of Project Management, Elsevier, Vol. 32 No. 1, pp. 101-115.

Wang, S.Q., Dulaimi, M.F. and Aguria, M.Y. (2004), “Risk management framework for construction projects in developing countries”, Construction Management and Economics, Taylor & Francis, Vol. 22 No. 3, pp. 237-252.

Woolley, T. and Kimmins, S. (2003), Green Building Handbook: Volume 2: A Guide to Building Products and Their Impact on the Environment, Routledge, Abingdon-on-Thames, Oxfordshire.

Xia, N., Zhong, R., Wu, C., Wang, X. and Wang, S. (2017), “Assessment of stakeholder-related risks in construction projects: integrated analyses of risk attributes and stakeholder influences”, Journal of Construction Engineering and Management, American Society of Civil Engineers, Vol. 143 No. 8, pp. 1-11.

Xu, Y., Chan, A.P.C. and Yeung, J.F.Y. (2010), “Developing a fuzzy risk allocation model for PPP projects in China”, Journal of Construction Engineering and Management, American Society of Civil Engineers, Vol. 136 No. 8, pp. 894-903.

Yang, R.J., Zou, P.X.W.W. and Wang, J. (2016), “Modelling stakeholder-associated risk networks in green building projects”, International Journal of Project Management, Elsevier and Association for Project Management and the International Project Management Association, Vol. 34 No. 1, pp. 66-81.

Zhao, Z.Y., Lv, Q.L., Zuo, J. and Zillante, G. (2010), “Prediction system for change management in construction project”, Journal of Construction Engineering and Management, American Society of Civil Engineers, Vol. 136 No. 6, pp. 659-669.

Zhao, X., Hwang, B.-G. and Low, S.P. (2014), “Investigating enterprise risk management maturity in construction firms”, Journal of Construction Engineering and Management, American Society of Civil Engineers, Vol. 140 No. 8, p. 5014006.

Zhao, X., Hwang, B.-G.G. and Gao, Y. (2016), “A fuzzy synthetic evaluation approach for risk assessment: a case of Singapore’s green projects”, Journal of Cleaner Production, Elsevier, Vol. 115, pp. 203-213.

Zou, P.X.W. and Couani, P. (2012), “Managing risks in green building supply chain”, Architectural Engineering and Design Management, Taylor & Francis, Vol. 8 No. 2, pp. 143-158.

Acknowledgements

The research is funded by the Fondazione Cassa di Risparmio di Padova e Rovigo.

Corresponding author

Hung Duy Nguyen can be contacted at: duyhung.nguyen@studenti.unipd.it

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