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. 2022 Aug 18;30(3):5717–5729. doi: 10.1007/s11356-022-22558-z

Understanding barriers and motivations in solid waste management from Malaysian industries: a comparative analysis

Mansoor Ahmed Soomro 1, Mohd Helmi Ali 2,, Suhaiza Zailani 3, Ming-Lang Tseng 4,5,6, Zafir Mohd Makhbul 2
PMCID: PMC9385409  PMID: 35978247

Abstract

The objective of this study is to explore the similarities and differences in the barriers and motivations between the plastic and resins and food and beverages industries as these two industries are the major contributors of solid waste in Malaysia. Prior studies are lacking with regard to explaining the barriers and motivations in solid waste management from the Malaysian context. This study is focused on 10 firms from the plastics and resins industry and 9 from the food and beverages industry in Malaysia. Through Rasch measurement theory, the results indicate that the barriers of lack of skills and qualifications and lack of closed-loop control and the motivations of cost savings and a business model are performed differently. The findings further confirm that the lack of skills and qualifications is a more difficult barrier to overcome than the lack of closed-loop control, while the motivation factor of a business model is more difficult to achieve than cost savings. In terms of practical contribution, this study provides results that can help policy makers in Malaysia to close the gaps present regarding the adoption of solid waste management practices and to devise appropriate incentives. The study also supports managers of companies in regard to working on the most pressing hindering and promoting factors in the field of solid waste management.

Keywords: Barriers and motivations factors, Solid waste management, Rasch measurement theory, Closed-loop control, Rasch rating scale model

Introduction

The management of solid waste is a global problem, but it is an even greater concern in developing and emerging countries. Overall, the topic of solid waste in emerging countries emerges from industrialization and modernization (Moh and Manaf 2020). In terms of emerging countries in Asia, the management of solid waste materials requires immediate attention in Malaysia, South Korea, and China, which have been identified as emerging industrialized countries (Bhakta et al. 2020). Malaysia is an emerging economy and has active participation from both the plastic and resins (P&R) and food and beverages (F&B) industries. The P&R industry is mostly business to business, whereas the F&B industry is largely business to consumer. For the same reason, the competition in the P&R industry is moderate, whereas competition is intense in the F&B industry. The main players in the P&R industry are plastic manufacturers; in F&B, the share is taken primarily by restaurants and cafes. Moreover, small and medium enterprises are more prevalent in the F&B industry in Malaysia than in the P&R industry. Meanwhile, the generation of solid wastes comprises a huge volume.

Industry solid waste management (SWM) challenges such as motivation and barriers to sustainable efforts are largely discussed to capture a holistic and in-depth understanding of phenomena and provide better guidance for the industry (Abdul-Hamid et al. 2020; Ahangar et al. 2021; Mondal and Giri 2021). Following this line of argument, two important industries, P&R and F&B, were studied for the following compelling reasons, which are related to the fact that P&R and F&B are among the major contributors to solid waste (Ncube et al. 2021). These industries are commonly the largest industries in emerging economy countries (Simon et al. 2018). The majority of the solid waste in industrial waste is nonrecyclable, and thus requires more sustainable management (Veleva and Bodkin 2017). Increasing solid waste has been a major challenge, especially in emerging economies (Chen et al. 2021). Critical factors such as growing populations, the inadequate enforcement of waste policies, general public attitudes, and economic burdens have daunted the efforts of SWM (Badgie et al. 2012; Negash et al. 2021). This situation calls for the urgent adoption of adequate and better waste management techniques to avoid adverse consequences on the environment (Bui et al. 2020; Chen et al. 2021; Negash et al. 2021). Managing sustainable SWM requires a strategic approach that focuses on the root cause of and the major contributors to solid waste. This study argues that understanding barriers to and motivations for engaging in SWM can improve such practices in Malaysia.

In particular, the generation of P&R waste, particularly in the consumption of single-use plastics and resins, results in a multitude of challenges for emerging countries’ waste management systems. The mismanagement of P&R wastes causes risks to both public health and the overall ecosystem (Chen et al. 2021). Local issues, such as increasing population and urbanization and waste management problems, are increasing (Horodytska and Cabanes 2019). Emerging economy countries have been known as “dump places” or as major importers of plastic waste from more developed countries. P&R waste further threatens coral reefs and marine ecosystems, which impacts adjacent industries such as agriculture. Therefore, the need for the recycling, recovery, and management of P&R waste is of paramount importance, and the P&R industry has a shared responsibility with other industries (Pham Phu et al. 2018). Similarly, food waste is more concerning for emerging economies due to minimal resources and the absence of strict regulations (Ncube et al. 2021). The adverse impacts from the F&B industry on the environment often attract media attention, but corrective action is often lacking (Aarnio and Anne 2008). This is exemplified by the continuous pressure from the media demanding that the government introduce and regulate sustainable programs and approaches for companies in the F&B industry (Ncube et al. 2021).This study aims to understand the shortcomings of SWM barriers and motivation factors in related practices.

Determining how the P&R and F&B industries perform in SWM in terms of barriers and motivations is a pressing and relevant topic for the following two reasons. First, these two industries contribute the majority of solid waste, and their approach to addressing barriers and reinforcing motivations can provide guidance on dealing with the issue of SWM. Second, there are commonalities between these two industries. For example, during the present COVID-19 pandemic and extended lockdown situation in different areas, food takeaway options have significantly increased. Customers who preferred a dine-in meal at their favorite restaurant had no choice but to place food delivery orders (Bhakta et al. 2020; Carroll and Conboy 2020). These food deliveries were usually contained in single-use food packaging plastics. Consumption therefore leads to an increase in both plastic waste and food waste, which is an overlapping area between the two industries (Duarte et al. 2020). There is a need to study these two industries and clarify the strategic points in SWM.

Even within the specialist literature in this area, empirical evidence comparing the P&R and F&B industries is relatively scarce (Chen et al. 2021; Zorpas et al. 2021). The majority of previous literature focuses on barriers and motivations for SWM, examining either a broad perspective covering multiple industries (Azevedo et al. 2019; Fedotkina et al. 2019; Bhakta et al. 2020) or covering only one specific industry (Chen et al. 2021; Horodytska and Cabanes 2019; Zorpas et al. 2021). In terms of the plastics industry, past studies have focused largely on recycling (Chen et al. 2021), packaging (Ncube et al. 2021), and reuse (Horodytska and Cabanes 2019). In terms of the food industry, the empirical focus of past research has been on using new technologies such as blockchain (Ali et al. 2021) and dealing with household and commercial food waste (Aarnio and Anne 2008).

In comparing the different performances, barriers and motivations for SWM between the P&R and F&B industries, there are two main objectives of the current study. (1) Barriers are important to understand as they need to be overcome in order to achieve the potential of companies with regard to SWM. Likewise, motivations are important as they reinforce and encourage companies to prioritize SWM in their business model and operations. (2) The Rasch measurement theory (RMT) has been used to rigorously compare and contrast the differences between barriers and motivations from these two industries in terms of what works in a certain industry and what does not work equally well in each industry. Achieving these two objectives will contribute to dynamic capabilities theory (Arend and Bromiley 2009) as firms in both the P&R and F&B industries will be encouraged to find and develop new competencies based on overcoming their barriers to the adoption of SWM. Likewise, the results regarding motivating factors in the P&R and F&B industries will signify the importance of competencies that have already been mastered by the firms in the SWM domain. This study will also extend the theory by reinforcing the dimensions or factors that can lead to the expansion of the resource base of firms in the two industries of P&R and F&B, which in turn improve the capability matrix for firms working on SWM practices.

This research studies 19 companies across Malaysia, namely, 10 from the P&R industry and 9 from the F&B industry. To achieve the objectives and to close the research gap, this study is structured as follows. First, based on the literature, a theoretical framework is presented. Second, the research method of Rasch is described. Third, the results are presented in terms of both barriers and motivations. Finally, the study concludes with a discussion of the results with their implications and the study limitations.

Theoretical background

Solid waste management barriers

In the literature, various barriers to the adoption of SWM have been studied and empirically analyzed. The most common ones are high investment cost (Yukalang et al. 2017; Ranta et al. 2018), absence of governmental pressure (Veleva and Bodkin 2017), lack of skills and qualifications (Yukalang et al. 2017; Ranta et al. 2018), and lack of closed-loop control (Veleva and Bodkin 2017). Juxtapose, Ritzén and Sandström (2017) emphasized the importance of a lack of technological infrastructure as a profound barrier, whereas Veleva and Bodkin (2017) found a lack of capabilities to reconfigure production patterns to be the most challenging barrier. The main research gap is that the majority of previous literature focuses on barriers from a wide perspective, comparing all industries together (Azevedo et al. 2019; Fedotkina et al. 2019; Bhakta et al. 2020), whereas the present study aims to take a narrow view of barriers in terms of two industries: P&R and F&B.

The P&R industry consists of companies chiefly engaged in manufacturing various plastics and resins (solid convertible into polymers) for sale to other industries that create plastic sheets, rods, films, and other products. The F&B industry comprises restaurants, cafeterias, food manufacturing operations, catering businesses, and food transportation service providers ranging from packaging to preparing, transporting, and serving food or beverages. Both of these industries have a unique set of barriers to adopting SWM practices. As per dynamic capabilities theory, organizations adopt, implement, and change their internal and external firm-specific competencies into new competencies based on the environment (Arend and Bromiley 2009; Teece and Pisano 1994). In this regard, the barriers faced by firms in terms of SWM can be overcome to develop new competencies for firms.

There are a variety of barriers faced by firms in the P&R industry, beginning with resources that mainly include skilled manpower and the right equipment (Tsai et al. 2020). The lack of these factors is particularly crucial for the P&R industry as a manufacturing industry. Furthermore, the design of an intelligent system for controlling the composition of solid waste is needed (Ali et al. 2021; Negash et al. 2021). There is a need to comprehend the urbanization trend in the country to foresee the inference of urban growth on plastic waste generation. In other words, precise and reliable data about a community’s plastic waste profile are necessary for a successful waste management system. Overall, emerging economies are still not fully capable of administering SWM facilities due to their resourcefulness and technical capabilities in the plastics and resins industry (Ahangar et al. 2021; Li 2018; Mondal and Giri 2021). Therefore, return on investment in SWM is low in this industry and is a major barrier.

Likewise, there are multiple barriers in the F&B industry. SWM for F&B services has a cost, and due to its specific perishability nature, expenditures are usually not recovered. In the best of cases, citizens are considered co-responsible together with companies and the government (Abarca et al. 2013). Communication among stakeholders is also necessary to obtain a performing food waste management system, which is seen as a barrier. Recycling and waste control at the source of food waste are also largely missing (Ali et al. 2021; Negash et al. 2021). Moreover, the attitudes of people towards waste management are a barrier for the F&B industry (Badgie et al. 2012). Another important challenge to address is the influence of education and awareness, which is a prime barrier for SWM (Dinie et al. 2013). In most emerging countries, environmental awareness among the public is not encouraging (Milea 2009). For example, the Malaysian government in 1988 introduced the Action Plan for Beautiful and Clean (ABC) Malaysia followed by a recycling campaign in the following years. However, the campaigns have not resulted in major positive results due to little participation from the public. Similarly, recycling bins mostly had contents that were found to be nonrecyclable (Horodytska and Cabanes 2019; Pham Phu et al. 2018).

SWM barriers are important to study and analyze because they either prevent or make it difficult for firms to adopt SWM practices (Bhakta et al. 2020). It is also important to understand that not all barriers have equal weight (Ali et al. 2021; Negash et al. 2021) or require the same time and effort (Ncube et al. 2021). Furthermore, contradictory viewpoints have been presented in the literature, which has placed even more focus on studying the barriers to SWM and the level of difficulty for these two industries. For example, companies’ attitudes towards SWM is a challenge when environmental issues are not a high priority (Badgie et al. 2012); however, the study by Dinie et al. (2013) found out that concern for environment is well established. Likewise, while the lack of enforcement of solid waste legislation is a barrier to proper documentation in emerging economies like Malaysia (Moh and Manaf 2020), the study by Mondal and Giri (2021) reconfirmed that government policies in Malaysia regarding SWM have been adequately aligned.

Firms studying the various barriers of SWM can better analyze their own strengths and weaknesses and plan a roadmap to overcome the barriers while keeping their business plan and sustainability as the terminal objectives (Joshi and Ahmed 2016). In particular, in the present pandemic (COVID-19), firms are finding it difficult to survive, and overcoming the barriers to SWM is even more challenging (Aarnio and Anne 2008). Hence, it is important to understand the intricacies, difficulties, and implications of various barriers to SWM, which in turn will help firms move towards the adoption of SWM practices.

Solid waste management motivations

Drawing from the literature, relatively few motivational factors have been studied in the area of SWM practices. Aparcana (2016) considered cost savings the main motivation, whereas Masrom et al. (2018) valued motivation from competitors and revenue pressure, respectively, for the adoption of SWM practices. The research gap that remains highlights that existing studies largely focus on motivations from all industries combined (Fedotkina et al. 2019; Bhakta et al. 2020). Therefore, the present study has a sharp focus on motivations in terms of two industries: P&R and F&B. Dynamic capabilities theory states that organizations purposefully create, extend and modify their resource base (Arend and Bromiley 2009; Teece and Pisano 1994). Therefore, the motivations faced by firms to adopt SWM practices can be identified to improve the resource base of the firm.

In the P&R industry, there are multiple opportunities in the area of solid waste that can motivate companies to adopt practices and processes towards SWM. The first motivation is pressure from the public, which can also be categorized as customer demands (Alhumoud and Al-Kandari 2008). In the product area, when consumers are conscious, they impose pressure on product companies to improve their commitment to SWM (Pariatamby and Solutions, 2014; Taylor et al. 2015). Furthermore, in some countries, there exists a concept of extended producer responsibility (EPR) that holds companies responsible for their product even after its useful life (Gu et al. 2018). Benefits of adopting SWM practices can be in the area of cost reduction as well as process optimization (Gaeta et al. 2021). The opportunity overall is to improve the sustainability of companies and their products, which is a win–win for producers, consumers, and governments equally. In terms of economics, opportunities also exist for businesses in terms of tax credits and allowances, which encourage solid waste minimization, cleaner production, and recycling, particularly in the business-to-business (B2B) setting of the P&R industry (Moh and Manaf 2020; Wee and Seow 2014).

In the F&B industry, the same public pressure applies to companies and the government to improve SWM. However, in this industry, the public is both the motivator and the executor as they not only put pressure on companies but also have to demonstrate through their societal actions that they value preventing F&B waste. With the increasing awareness of food waste and its drastic effects, small and medium enterprises in the F&B industry feel empowered to recycle and reuse. Environmental education passed on through government public policy and private associations has also motivated the prioritization of the topic of food waste. Likewise, it is important to note that there are various small and medium companies that are not able to bear the elevated costs of high-quality waste management, which otherwise is an opportunity for national and provincial legislation on this important topic of food and beverage waste (Azevedo et al. 2019).

Moreover, there is a disconnect on certain occasions in terms of motivations for SWM. For instance, environmental stewardship is a great opportunity for companies (Yukalang et al. 2017), whereas the authors of Masrom et al. (2018) are of the view that adherence to international standards is not the main attraction for firms to adopt SWM practices. Similarly, firms with the potential to make footprints with regard to SWM are more profitable in Malaysia (Mondal and Giri 2021), whereas the studies by Fedotkina et al. (2019) and Bhakta et al. (2020) implied that there is business continuity risk assigned with companies putting SWM as their radar with regard to business performance.

Overall, it is important to study the various factors that motivate firms to adopt SWM as a major push is needed on that front, especially because the majority of firms still have not taken the first step towards effective SWM (Boyle 2000; Yukalang et al. 2017). It is also important in terms of positive reinforcement to attract and empower firms to drive initiatives around SWM and to provide them with incentives for doing so. SWM is a multidimensional issue (Abarca et al. 2013) that includes environmental, social, cultural, legal, institutional, economic, and technological factors (Moh and Manaf 2020). Businesses aim at increased efficiency and reduced cost to be sustainable. Therefore, in the drive to adopt SWM practices, it is important to study the motivations for SWM and how it can assist companies in efficiency and cost.

Method

Research setting: Malaysia as an emerging economy

Malaysia, as an emerging country, encounters issues in terms of its technology, workforce, and infrastructure, which are inadequate to cope with the ever-increasing momentum of waste generation (Badgie et al. 2012). Solid waste generation in Malaysia has recently approached a critical point, especially in terms of volume and composition. Statistics from Malaysian Investment Development Authority show that the average quantity of solid waste at the country level exceeds 38,000 tons per day. What is more worrying is the fact that these numbers are expected to increased significantly. In terms of the industry split, Bloomberg reported that the market size of the P&R industry in Malaysia is over US$3,200 million, whereas the market size of F&B is over US$6 billion. These market sizes reaffirm that both the industries studied in this study are of paramount importance to Malaysia and serve as interesting cases for regional countries. Prior management of solid waste demanded less effort as the waste was generated at a manageable level, but now it is alarming, particularly in terms of plastic disposal and food leftovers (Chen et al. 2021). The government of Malaysia implemented a Strategic Plan 2014–2020 including subjects such as mindset, behavior, and culture, which resulted in an approximately 30% recycling rate in 2020 (Moh and Manaf 2020). However, with the heavy reliance on landfilling in Malaysia, it is unavoidable that there are issues of space limitations (Chen et al. 2021). In short, Malaysia, as an emerging country, has experienced economic growth in recent years that has directly resulted in an increase in solid waste pollution, particularly in terms of plastic and food waste (Ncube et al. 2021; Pham Phu et al. 2018).

Two selection criteria were designed to identify and select respondents for the survey: (a) senior managers with organization-wide understanding and (b) at least 1 year of experience working in the company. In line with these criteria, the respondents who became part of this research study (a) were mostly directors and departmental heads and (b) had a minimum of 3 years of working experience in the current company. Data collection was performed across the different states of Malaysia. As a result, 19 companies were studied according to the research aims of this study, of which 10 were from the P&R industry and 9 were from the F&B industry. Of these 19 companies, most were Malaysian-owned (79%). In terms of company age, the majority of the companies were 11–20 years old (37%), followed by more than 30 years old (26%). Second, in terms of the number of employees in the company, 74% of companies had 250 employees or less. Likewise, in terms of annual sales turnover, the majority of the companies (53%) enjoyed an annual sales turnover of more than 50 million Malaysian ringgits. Details of the sample structure are presented in Table 1.

Table 1.

Description of sample

Number of companies
Industry classification

Plastics and resins

F&B

10

9

Ownership

Malaysian-owned

Non-Malaysian-owned

15

4

Company age

 < 5 years

6–10 years

11–20 years

21–30 years

 > 30 years

3

3

7

1

5

Employees in the company

 < 100

101–250

251–500

500–1000

 > 1000

7

7

1

1

3

Annual sales turnover (Malaysian ringgit)

 < 300,000

300,000–15,000,000

15,000,000–50,000,000

 > 50,000,000

1

2

6

10

Total 19

Rasch measurement theory

Rasch measurement theory (RMT) is based on latent-variable probabilistic models (Wolins et al. 1982). It draws an inference from item response theory (IRT), which belongs to the family of mathematical models that attempts to explain the relationship between latent traits (unobservable characteristics) and their manifestations (observed outcomes) (Thissen and Orlando 2021). Rasch modeling offers a range of possibilities by leveraging mathematical features for psychometric testing and measurement (Andrich 1978). In the area of SWM, Rasch has been used in past empirical studies of waste recycler behaviors (Tiew et al. 2015), waste disposal (Kamis et al. 2018), green movement and sustainability (Mona et al. 2016), and waste management cycles (Norizan et al. 2012).

Rasch measurement is based on a theoretical model with statistical properties that accepts the comparability of the measures from the sample data (Wolins et al. 1982). The use of this theory requires the confirmation of unidimensionality and local independence (Andrich 1978). The measures obtained have the characteristics of the ideal model formulated when they globally fit it. Otherwise, individualized analysis of the misfits can clarify the causes of its absence (Marais and Andrich 2008). The uniqueness of the RMT is the use of the same logit measuring scale for the estimation of two parameters—ability and difficulty—to subjects and items. This enables the combined measurement of both entities and the location on the same unidirectional linear continuum.

Andrich (1978) and Wolins et al. (1982) formulated a model for dichotomous items that resulted in the Rasch rating scale model (RRSM). The RRSM allows the definition of the latent variable through polytomous items in ordered categories (Azizan et al. 2020). The Naiperian expression of this model is as follows;

LnPnijPni(j-1)=βn-δi+τj

where.

Pnij

probability of the observed category j.

P(ni(j-1))

probability of the observed category j-1.

βn

measurement of the ability of subject n.

δi

measurement of difficulty of item I.

τj

differential of difficulty of observed category j in relation to the previous j-1.

The invariance feature is inherent to the structure of the Rasch models, which establishes whether some item in the measurement of the construct performs a different function (Andrich 1978). For this, it is vital to analyze the differential item functioning (DIF) and to identify the presence of bias when a group of subjects with some common feature obtains a significantly different calibration from that of another group in an item’s difficulty (Schauberger and Mair 2020). The RRSM is particularly ideal for measuring latent variables such as barriers and motivations as it is the result of the measurements assessed by respondents from both the P&R and F&B industries. Barrier and motivation items are positioned on a linear continuum, allowing them to be measured according to their ability and difficulty, respectively, from left (less) to right (more). Likewise, the DIF analysis allows identification of the presence of different levels of difficulty and statistical significance in the P&R and F&B differentiated industries.

Measurement scale and fit diagnosis

In this study, there are two constructs: barriers and motivations. The items for the construct “barriers” were measured through 24 factors that have been identified in the past literature and empirical studies as elements that slow the progress of SWM (Luiz et al. 2016; Yukalang et al. 2017; Mahpour 2018; Fedotkina et al. 2019). Likewise, the items for the construct “motivations” were measured through 7 factors that have been identified in the past literature and empirical studies as elements that accelerate the progress of SWM (Janmaimool 2017; Fan et al. 2018; Masrom et al. 2018). The scale to measure the ratings was adapted to a 5-point Likert scale with the following levels: 1 (very little extent), 2 (little extent), 3 (some extent), 4 (great extent), and 5 (very great extent). The software Winsteps version 4.4.7 was used for data handling. Table 2 shows the main specifications of this study. The measurement items for both barriers and motivations are listed in Table 3.

Table 2.

Technical specifications

Industries P&R and F&B
Context Malaysia
Type of information Primary
Data collection method Survey
Time scope May 2021—August 2021
Sample size 19 Companies (10 P&R, 9 F&B)
Data handling Rasch Winsteps software, version 4.4.7

Table 3.

Construct items

No Items Reference
Barriers
   B1 Lack of knowledge management systems (Dumlao-Tan and Halog 2017)
   B2 Absence of governmental pressure (Veleva and Bodkin 2017)
   B3 Lack of evidence of profitability (Ritzén and Sandström 2017)
   B4 Poor company SWM operations vision/mission (Dumlao-Tan and Halog 2017; Mahpour 2018)
   B5 Lack of skills and qualifications (Yukalang et al. 2017; Ranta et al. 2018)
   B6 Lack of regulatory framework (Dumlao-Tan and Halog 2017)
   B7 Difficulty accessing suitable financing (Dumlao-Tan and Halog 2017)
   B8 Absence of consumer demand (Veleva and Bodkin 2017)
   B9 Perception of high business risk (Ritzén and Sandström 2017)
   B10 Dominant position of key market players (Mahpour 2018)
   B11 Lack of capabilities to reconfiguring production pattern (Veleva and Bodkin 2017)
   B12 Lack of closed-loop control (Veleva and Bodkin 2017)
   B13 Lack of knowledge base (Ritzén and Sandström 2017)
   B14 Lack of organizational and process changes ( Ranta et al. 2018; Yukalang et al. 2017)
   B15 Lack of process design (Mahpour 2018)
   B16 Unstable connectivity among companies (Mahpour 2018)
   B17 Lack of understanding of SWM implications (Ritzén and Sandström 2017)
   B18 High investment ( Ranta et al. 2018; Yukalang et al. 2017)
   B19 Difficulty recovering materials for recycling (Dumlao-Tan and Halog 2017)
   B20 Low management support and dedication (Veleva and Bodkin 2017)
   B21 Lack of experience leader (Dumlao-Tan and Halog 2017)
   B22 Shareholder pressure promotes linear thinking (Mahpour 2018)
   B23 Lack of technological infrastructure (Ritzén and Sandström 2017)
   B24 Lack of compatibility (Dumlao-Tan and Halog 2017)
Motivations
   M1 Cost savings (Aparcana 2016)
   M2 Green/sustainability credentials (Masrom et al. 2018)
   M3 Competitor’s actions (Milea 2009; Aparcana, 2016)
   M4 Downward pressure on revenue/profits (Masrom et al. 2018)
   M5 Explicit customer demand/preferences (Aparcana 2016)
   M6 Move towards a SWM model (Aparcana 2016)
   M7 Scarcity of natural resources (Milea 2009; Aparcana 2016)

SWM, solid waste management

In the diagnosis of the fit, the need to recategorize the measurement scale is not explicitly observed. Following previous recommendations (Linacre 2009), we chose to establish a structure with 5 categories. The estimates of Andrich threshold parameters (− 2.00, − 0.68, 0.72, 1.95) guarantee the absence of disorders in the levels of difficulty of the items, confirming the effectiveness of the structure of categories. Furthermore, the latent trait barriers and motivations have only one dimension, and the items considered for their definition in the domain of SWM reflect only one reality. This operational requirement of the RRSM was checked with three types of analysis. The first is the principal component analysis of Rasch residuals (PCAR), in which the values of the indicators obtained (variance explained 42.4%, unexplained variance in first contrast 5.53%) allows us to discard the presence of multidimensionality tensions (Linacre 2009).

Second, the positive point-measure (PTM) correlation sign confirms the adequacy of the measurements. As seen in Table 4 and Table 5, the PTM of all items is positive except for motivation item number 2 (green/sustainability credentials), which had − 0.18 PTM, which resulted in the deletion of this item. Finally, the reliability and validity analysis was assessed by using Rasch estimators of measurement separation for subjects and items. As the values were above 0.70, the Rasch standard levels were confirmed, confirming the reliability and validity of the measurement.

Table 4.

Calibration of items: barriers

No Items MEASURE STD ERR INFIT MNSQ INFIT ZSTD OUTFIT MNSQ OUTFIT ZSTD PTM
B1 Lack of knowledge management systems 0.04 0.27 0.60  − 1.45 0.60  − 1.46 0.50
B2 Absence of governmental pressure 1.07 0.27 1.63 1.83 1.62 1.79 0.31
B3 Lack of evidence of profitability 0.26 0.27 1.08 0.37 1.07 0.34 0.58
B4 Poor company SWM operations vision/mission 0.26 0.27 0.84  − 0.45 0.84  − 0.46 0.58
B5 Lack of skills and qualifications  − 0.92 0.30 1.22 0.78 1.52 1.60 0.24
B6 Lack of regulatory framework  − 0.26 0.28 1.05 0.26 1.05 0.26 0.23
B7 Difficulty accessing suitable financing  − 0.26 0.28 1.04 0.23 1.02 0.15 0.27
B8 Absence of consumer demand 1.07 0.27 1.94 2.51 1.93 2.50 0.41
B9 Perception of high business risk  − 0.19 0.28 1.00 0.09 1.00 0.11 0.32
B10 Dominant position of key market players 0.11 0.27 1.23 0.80 1.22 0.78 0.15
B11 Lack of capabilities to reconfiguring production pattern  − 0.03 0.27 0.62  − 1.35 0.62  − 1.36 0.49
B12 Lack of closed-loop control 0.19 0.27 0.97  − 0.01 0.97 0.02 0.08
B13 Lack of knowledge base  − 0.50 0.28 0.56  − 1.68 0.57  − 1.65 0.71
B14 Lack of organizational and process changes  − 0.19 0.28 0.37  − 2.70 0.37  − 2.73 0.24
B15 Lack of process design  − 0.19 0.28 0.91  − 0.21 0.89  − 0.30 0.03
B16 Unstable connectivity among companies 0.19 0.27 1.13 0.50 1.12 0.49 0.25
B17 Lack of understanding of SWM implications 0.34 0.27 0.77  − 0.71 0.77  − 0.70 0.63
B18 High investment  − 1.10 0.31 0.32  − 3.02 0.35  − 2.83 0.48
B19 Difficulty recovering materials for recycling  − 0.66 0.29 0.85  − 0.43 0.81  − 0.57 0.13
B20 Low management support and dedication 1.00 0.27 0.58  − 1.51 0.57  − 1.54 0.22
B21 Lack of experience leader  − 0.03 0.27 1.24 0.85 1.25 0.87 0.49
B22 Shareholder pressure promotes linear thinking 1.00 0.27 0.84  − 0.46 0.83  − 0.47 0.01
B23 Lack of technological infrastructure  − 0.50 0.28 0.76  − 0.79 0.74  − 0.87 0.40
B24 Lack of compatibility 0.19 0.27 1.18 0.67 1.18 0.66 0.64

Table 5.

Calibration of items: motivations

No Items MEASURE STD ERROR INFIT MNSQ INFIT ZSTD OUTFIT MNSQ OUTFIT ZSTD PTM
M1 Cost savings 0.26 0.27 1.00 0.10 1.00 0.11 0.19
M2 Green/sustainability credentials  − 0.83 0.29 1.07 0.33 1.10 0.42  − 0.18
M3 Competitor’s actions  − 0.42 0.28 0.82  − 0.55 0.80  − 0.62 0.34
M4 Downward pressure on revenue/profits 0.63 0.27 0.84  − 0.44 0.84  − 0.44 0.75
M5 Explicit customer demand/preferences  − 1.20 0.31 1.23 0.80 1.23 0.81 0.19
M6 Move towards a SWM model 0.04 0.27 1.48 1.49 1.49 1.50 0.04
M7 Scarcity of natural resources 0.63 0.27 1.47 1.44 1.48 1.45 0.14

Regarding the individual validity analysis, the outfit mean square of residuals (MNSQ) for three items was above the recommended levels (Wright and Linacre 1994): barrier “lack of organizational and process changes,” barrier “high investment,” and barrier “absence of consumer demand”; their Outfit MNSQs were − 2.73, − 2.83, and 2.50, respectively, as shown in Table 4. These three barrier items were checked individually, and no distortions were found; hence, the items were retained. Overall, the diagnosis allows confirmation of the fit of data to Rasch measurement theory. Hence, the measures obtained adopt the properties of the model.

Results

To answer the main research question of this study, the RRSM of the DIF analysis (Linacre 2009) was applied to identify whether there were significant differences in both barriers and motivations among the two industry groups. The statistical Welch’s t test of difference in means was used, and the indicators of differential behavior were interpreted (Bond and Fox 2003). The hypothesis of the existence of differences in the items’ differential behavior was accepted when significance was under 0.05. In addition, the differences were considered based on the DIF contrast value: DIF contrast less than 0.43 was considered small, DIF contrast between 0.43 and 0.64 was considered moderate, and DIF contrast greater than 0.64 was considered large ( Linacre 2002; Wright and Linacre 1994).

The DIF analysis was conducted in two stages. In the first stage, the two industries, P&R and F&B, were compared in terms of barriers to SWM. Table 6 shows each barrier item with its significance value and DIF contrast. It needs to be clearly determined whether there are significant differences in the item responses between the respondents from the P&R industries and those from the F&B industries. The results obtained confirm the existence of differences between these two industry groups for two barrier items, namely, B5, “lack of skills and qualification,” and B12, “lack of closed-loop control.” The first interindustry difference of B5, “lack of skills and qualification,” has a probability of 0.0216 (significant as P < 0.05) and a DIF contrast of 1.74 (categorized as a large difference). Based on the positive direction of comparison from F&B to P&R, the first finding of the study reveals that barrier B5, “lack of skills and qualification,” is a difficult barrier to overcome in the F&B industry compared to the P&R industry with regard to the adoption of SWM practices. The second interindustry difference of B12, “lack of closed-loop control,” has a probability of 0.0322 (significant as P < 0.05) and a DIF contrast of 1.29 (also categorized as a large difference). Based on the positive direction of comparison from P&R to F&B, the second finding of the study reveals that barrier B12, “lack of closed-loop control,” is a difficult barrier to overcome in the P&R industry compared to the F&B industry with regard to the adoption of SWM practices.

Table 6.

DIF of P&R and F&B industry: barriers

No Industry groups DIF contrast t of Welch Probability Items
B1 F&B P&R 1.10 1.97 0.0663 Lack of knowledge management systems
B2 P&R F&B 0.29 0.54 0.5991 Absence of governmental pressure
B3 F&B P&R 0.35 0.65 0.5250 Lack of evidence of profitability
B4 F&B P&R 0.96 1.73 0.1024 Poor company SWM operations vision/mission
B5 F&B P&R 1.74 2.56 0.0216 Lack of skills and qualifications
B6 F&B P&R 0.48 0.85 0.4058 Lack of regulatory framework
B7 F&B P&R 0.48 0.85 0.4058 Difficulty accessing suitable financing
B8 P&R F&B 0.89 1.63 0.1228 Absence of consumer demand
B9 F&B P&R 0.32 0.58 0.5675 Perception of high business risk
B10 P&R F&B 0.25 0.47 0.6469 Dominant position of key market players
B11 P&R F&B 0.27 0.50 0.6256 Lack of capabilities to reconfigure production pattern
B12 P&R F&B 1.29 2.35 0.0322 Lack of closed-loop control
B13 F&B P&R 0.32 0.56 0.5833 Lack of knowledge base
B14 F&B P&R 0.00 0.00 1.000 Lack of organizational and process changes
B15 P&R F&B 0.59 1.07 0.2992 Lack of process design
B16 P&R F&B 0.40 0.73 0.4773 Unstable connectivity among companies
B17 P&R F&B 0.08 0.15 0.8804 Lack of understanding on SWM implications
B18 F&B P&R 0.57 0.90 0.3822 High investment
B19 F&B P&R 0.00 0.00 1.000 Difficulty recovering materials for recycling
B20 P&R F&B 0.45 0.83 0.4194 Low management support and dedication
B21 F&B P&R 0.95 1.69 0.1098 Lack of experience leader
B22 F&B P&R 0.14 0.26 0.7945 Shareholder pressure promotes linear thinking
B23 F&B P&R 0.65 1.13 0.2767 Lack of technological infrastructure
B24 F&B P&R 1.10 1.99 0.0642 Lack of compatibility

The two industries, P&R and F&B, were compared in terms of motivations for SWM. Table 7 shows each motivation item with its significance value and DIF contrast. Subsequently, it needs to be distinctly determined whether there are significant differences in the item responses between the respondents from the P&R and F&B industries. The results obtained confirm the existence of differences between these two industry groups for two motivation items, namely, M1, “achieve cost savings,” and M6, “moving towards SWM model.” The third interindustry difference of M1, “achieve cost savings,” has a probability of 0.0195 (significant as P < 0.05) and a DIF contrast of 1.43 (categorized as a large difference). Based on the positive direction of comparison from P&R to F&B, the third finding of the study reveals that the motivation factor M1, “achieve cost savings,” is a difficult factor to achieve in the P&R industry compared to the F&B industry with regard to the adoption of SWM practices. The fourth interindustry difference of M6, “moving towards SWM model,” has a probability of 0.0034 (significant as P < 0.05) and a DIF contrast of 1.95 (also categorized as large difference). Based on the positive direction of comparison from P&R to F&B, the fourth finding of the study reveals that the motivation factor M6, “moving towards SWM model,” is a difficult factor to achieve in the P&R industry compared to the F&B industry with regard to the adoption of SWM practices.

Table 7.

DIF of P&R and F&B industry: motivations

No Industry groups DIF contrast t of Welch Probability Items
M1 P&R F&B 1.43 2.60 0.0195 Cost savings
M2 P&R F&B 1.07 1.78 0.0949 Green/sustainability credentials
M3 F&B P&R 0.16 0.29 0.7778 Competitors’ actions
M4 F&B P&R 0.54 0.99 0.3363 Downward pressure on revenue/profits
M5 P&R F&B 0.41 0.65 0.5270 Explicit customer demand/preferences
M6 P&R F&B 1.95 3.43 0.0034 Move towards a SWM model
M7 P&R F&B 0.05 0.09 0.9277 Scarcity of natural resources

Discussion

The present study contributes to the literature on the comparison of the SWM performance of the P&R industry with that of the F&B industry using RMT to study their barriers and motivations. This study has resulted in additional empirical evidence regarding the differences in the adoption of SWM practices between these two industries, resulting in a theoretical contribution.

Specifically, this study’s results show four main findings. First, barrier B5, “lack of skills and qualification,” is a difficult barrier to overcome in the F&B industry compared to the P&R industry due to formal and informal training and development structural differences between the two industries (Abarca et al. 2013; Ma et al. 2017). Second, barrier B12, “lack of closed-loop control,” is a difficult barrier to overcome in the P&R industry compared to the F&B industry due to varying complexity between the industries (Manavalan and Jayakrishna 2018). Third, the motivation factor M1, “cost savings,” is a difficult factor to achieve in the P&R industry compared to the F&B industry, taking inference from the scale of organizations in the two industries (Chen et al. 2021; Lingard et al. 2000). Fourth, the motivation factor M6, “moving towards SWM model,” is a difficult factor to achieve in the P&R industry compared to the F&B industry due to the consumption versus the manufacturing nature of organizations in the two industries (Fan et al. 2018; Tsai et al. 2020).

The findings confirm that barrier B5, “lack of skills and qualification,” is significant and performs differently between two industries such that it is a difficult barrier to overcome in the F&B industry compared to the P&R industry. This finding resonates with the studies by Ma et al. (2017) and Abarca et al. (2013). The major reason for this is the structure and organization of training and development. In the P&R industry, firms are mostly medium- to large-sized organizations that have a formal training and development department that ensures that upskilling and reskilling are periodically planned and executed. On the other hand, the F&B industry is mostly driven by small and medium-sized organizations, which mostly have an informal training and development structure. Therefore, the barrier “lack of skills and qualification” is easy to deal with in the P&R industry but relatively difficult to deal with in the F&B industry. However, this result is contrary to the study by Luiz et al. (2016), where technology takes preference over training.

Barrier B12, “lack of closed-loop control,” is significant and performs differently between the two industries such that it is a difficult barrier to overcome in the P&R industry compared to the F&B industry. Closed-loop control is a control system based on monitoring feedback through which feedback identifies deviation and, as a result, controls the action (Manavalan and Jayakrishna 2018). This control system thrives on feedback to determine the outcome and to minimize deviations. In terms of SWM, this finding echoes the studies by Negash et al. (2021) and Manaf et al. (2009). This can be largely explained by the fact that in the P&R industry, processes are complex due to the size of the organization, whereas F&B industry players, mostly have straightforward and simple processes. Therefore, due to the complexity and size of organizations, it is difficult to overcome the lack of closed-loop control in the P&R industry, which is easier to manage in the F&B industry.

This study confirms that the motivation factor M1 “achieve cost savings” is significant and performs differently between the two industries such that it is a difficult motivation factor to achieve in the P&R industry compared to the F&B industry. The P&R industry consists of entities that are involved in manufacturing various plastics and resins (solid convertible into polymers) for sale to other industries that create plastic products. The setup of companies in this industry is comparable to established companies for which cost savings are an everyday exercise. As they work on cost saving initiatives regularly, cost saving as a motivation is not a dominant factor for this industry. However, the motivation of cost savings is a driving force in dealing with F&B industry players, which comprise small setups such as restaurants, cafeterias, and catering businesses. This finding resonates with the studies by Lingard et al. (2000) and Chen et al. (2021). Therefore, due to the scale of organizations, cost savings are an easy motivation factor to achieve in the F&B industry compared to the P&R industry.

The motivation factor M6 “moving towards SWM model” is significant and performs differently between the two industries such that it is a difficult motivation to achieve in the P&R industry compared to the F&B industry. This finding is in concurrence with the studies by Fan et al. (2018) and Tsai et al. (2020). There is a major contrast between the two studied industries. The F&B industry is largely a consumption-based industry, whereas P&R is predominantly a manufacturing-based industry or, recently, has reoriented itself to be an auxiliary industry (a combination of manufacturing and consumption). Additionally, modern manufacturing is advanced and complex, and adapting or customizing the existing advanced manufacturing models to gain the merits of SWM can be challenging initially (Behzad et al. 2011; Fukuda 2020). Therefore, due to the consumption, manufacturing, and auxiliary concerns of organizations, moving towards a SWM model is an easy motivation factor to achieve in the F&B industry but a difficult motivation factor to achieve in the P&R industry.

All four study findings have a large DIF contrast, implying a large significant difference for each of these four items between the two industries. For a comparative analysis, the calibration for barrier B5 “lack of skills and qualification” (DIF Contrast 1.74) is higher than B12 “lack of closed-loop control” (DIF Contrast 1.29), implying that barrier B5 “lack of skills and qualification” is more difficult to overcome than B12 “lack of closed-loop control.” The calibration for motivation factor M6 “moving towards SWM model” (DIF Contrast 1.95) is higher than M1 “achieve cost savings” (DIF Contrast 1.43), implying that the motivation factor M6 “moving towards SWM mode” is more difficult to achieve than M1 “achieve cost savings.”

This study complements and extends research on the P&R and F&B industries and their barriers and motivations in the following four aspects. First, the categorization of plastics and resins with the F&B industry in the SWM sector according to barriers and motivations has made it possible to reconcile the empirical evidence in this regard, which is lacking. Second, the study identifies differences in terms of skills and qualifications (Luiz et al. 2016), closed-loop control (Horodytska and Cabanes 2019), cost savings (Mona et al. 2016), and business models (Tsai et al. 2020) between the two industries. Third, it supports and extends the findings of Chen et al. (2021), Ncube et al. (2021), and Bhakta et al. (2020). Finally, it introduces a measuring instrument, the RMT, that has not been used before in the comparison of the solid waste sector between the P&R and F&B industries.

Conclusions

In Malaysia, the lack of public conscientiousness in modern lifestyles has resulted in an increasing amount of both waste generation and waste disposal, especially in regard to plastic and food waste. Therefore, awareness contributes significantly to the environmental response with regard to how society perceives the issue and how people direct their behavior in managing solid waste. Adding to socioeconomic factors, the perception of infinite resources with no observable environmental consequences to the public is also a factor in overconsumption, which produces unnecessary waste over time. Increased recycling at the household level reduces these problems of increasing solid waste generation. The most pressing challenge in source separation and recycling practice is public attitudes towards making source separation and recycling separation a habit. Consequently, the sense of collective responsibility and concerns about the implications of not separating waste are also somewhat deficient. Therefore, the results lend insight into four implications for the industry.

This study, through Rasch measurement theory, adds to the literature in the area of SWM with a specific focus on comparing barriers and motivations between the P&R and F&B industries in Malaysia as an emerging economy. There are four specific findings of this study, two relating to the barriers (lack of skills and qualifications and lack of closed-loop control) and the other two pertaining to the motivation factors (cost savings and business model), which perform differently for the two studied industries.

There are two limitations of this study. The first is the sample size. Nineteen companies were studied, 10 from the P&R industry and 9 from the F&B industry. The two industries have important differences in terms of perishability, competition, and lifecycle but have commonalities as the largest contributors to solid waste (Dinie et al. 2013; Pham Phu et al. 2018). The 19 studied companies had good heterogeneity in terms of ownership (Malaysian and non-Malaysian), company age, and sales turnover. However, future studies can include more organizations from both the P&R and F&B industries for additional insights and perspectives. The second limitation is the geographical context chosen, Malaysia. This study was based on companies operating in both sectors inside Malaysia only. Malaysia has long struggled to reduce solid waste and accordingly has attracted much legislation and policy-making attention (Ncube et al. 2021). However, it is appropriate to expand the countries, regions, and territories to obtain value from a greater diversity of countries. Therefore, more categorization of items within the P&R and F&B industries is needed.

Author contribution

Mansoor Ahmed Soomro: conceptualizing, original version, data analysis; Mohd Helmi Ali: conceptualizing, original version and finalizing the final version; Suhaiza Zailani: conceptualizing, data collection, editing final version; Ming-Lang Tseng: conceptualizing, finalizing the final version; Zafir Mohd Makhbul: conceptualizing, editing.

Funding

This work was supported in part by the Ministry of Higher Education under FRGS/1/2021/SS01/UKM/02/1.

Declarations

Competing interests

The authors declare no competing interests.

Footnotes

Publisher's note

Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Contributor Information

Mansoor Ahmed Soomro, Email: m.soomro@tees.ac.uk.

Mohd Helmi Ali, Email: mohdhelmiali@ukm.edu.my.

Suhaiza Zailani, Email: shmz@um.edu.my.

Ming-Lang Tseng, Email: tsengminglang@gmail.com.

Zafir Mohd Makhbul, Email: zafir@ukm.edu.my.

References

  1. Aarnio T, Anne H. Challenges in packaging waste management in the fast food industry. Resour Conserv Recycl. 2008;52:612–621. doi: 10.1016/j.resconrec.2007.08.002. [DOI] [Google Scholar]
  2. Abarca L, Maas G, Hogland W. Solid waste management challenges for cities in developing countries. Waste Management. 2013;33(1):220–232. doi: 10.1016/j.wasman.2012.09.008. [DOI] [PubMed] [Google Scholar]
  3. Abdul-Hamid AQ, et al. Impeding challenges on industry 40 in circular economy: Palm oil industry in Malaysia. Comput Oper Res. 2020;123:105052. doi: 10.1016/j.cor.2020.105052. [DOI] [Google Scholar]
  4. Alhumoud JM, Al-Kandari FA. Analysis and overview of industrial solid waste management in Kuwait. Manag Environ Qual Int J. 2008 doi: 10.1108/14777830810894210. [DOI] [Google Scholar]
  5. Ali MH, et al. A sustainable Blockchain framework for the halal food supply chain: Lessons from Malaysia. Technol Forecast Soc Change. 2021;170(May):120870. doi: 10.1016/j.techfore.2021.120870. [DOI] [Google Scholar]
  6. Andrich D (1978) A rating formulation for ordered response categories. Psychometrika 43(4). 10.1007/BF02293814
  7. Ahangar SS, Sadati A, Rabbani M. Sustainable design of a municipal solid waste management system in an integrated closed-loop supply chain network using a fuzzy approach: a case study. J Ind Prod Eng. 2021;38(5):323–340. doi: 10.1080/21681015.2021.1891146. [DOI] [Google Scholar]
  8. Aparcana S. Approaches to formalization of the informal waste sector into municipal solid waste management systems in low- and middle-income countries : review of barriers and success factors. Waste Management. 2016 doi: 10.1016/j.wasman.2016.12.028. [DOI] [PubMed] [Google Scholar]
  9. Arend RJ, Bromiley P. Assessing the dynamic capabilities view: spare change, everyone? Strateg Organ. 2009;7(1):75–90. doi: 10.1177/1476127008100132. [DOI] [Google Scholar]
  10. Azevedo BD, Scavarda LF, Goyannes R. Urban solid waste management in developing countries from the sustainable supply chain management perspective : a case study of Brazil’s largest slum. J Clean Prod. 2019;233:1377–1386. doi: 10.1016/j.jclepro.2019.06.162. [DOI] [Google Scholar]
  11. Azizan NH et al (2020) Rasch rating scale item estimates using maximum likelihood approach: effects of sample size on the accuracy and bias of the estimates. Int J Adv Sci Technol 29(4)
  12. Badgie D, et al. Assessment of municipal solid waste composition in Malaysia : management, practice, and challenges. Pol J Environ Stud. 2012;21(3):539–547. [Google Scholar]
  13. Behzad N, et al (2011) Challenges of solid waste management in Malaysia. Res J Chem Environ (July)
  14. Bhakta H, et al. Challenges, opportunities, and innovations for effective solid waste management during and post COVID-19 pandemic, Resources. Conserv Recycl. 2020;162(May):105052. doi: 10.1016/j.resconrec.2020.105052. [DOI] [PMC free article] [PubMed] [Google Scholar]
  15. Bond TG, Fox CM. Applying the Rasch model: fundamental measurement in the human sciences. J Educ Meas. 2003 doi: 10.1111/j.1745-3984.2003.tb01103.x. [DOI] [Google Scholar]
  16. Boyle CA. Solid waste management in New Zealand. Waste Manage. 2000;20:517–526. doi: 10.1016/S0956-053X(00)00023-4. [DOI] [Google Scholar]
  17. Bui TD, et al. Identifying sustainable solid waste management barriers in practice using the fuzzy Delphi method, Resources. Conserv Recycl. 2020;154(August 2019):104625. doi: 10.1016/j.resconrec.2019.104625. [DOI] [Google Scholar]
  18. Carroll, N. and Conboy, K. (2020) Normalising the “new normal”: changing tech-driven work practices under pandemic time pressure. Int J Inf Manag (June):102186. 10.1016/j.ijinfomgt.2020.102186 (Elsevier) [DOI] [PMC free article] [PubMed]
  19. Chen HL, et al. The plastic waste problem in Malaysia: management, recycling and disposal of local and global plastic waste SN Applied Sciences. Springer Int Publishing. 2021;3(4):1–15. doi: 10.1007/s42452-021-04234-y. [DOI] [Google Scholar]
  20. Dinie M, Samsudin M, Don MM. Municipal solid waste management in Malaysia : current practices, challenges and prospect. Jurnal Teknologi. 2013;1:95–101. [Google Scholar]
  21. Duarte B, et al (2020) Improving urban household solid waste management in developing countries based on the German experience. Waste Manag. 10.1016/j.wasman.2020.11.001 (Elsevier Ltd, (xxxx)). [DOI] [PubMed]
  22. Dumlao-Tan, M. I. and Halog, A. (2017) Moving towards a circular economy in solid waste management: concepts and practices, in Advances in Solid and Hazardous Waste Management. 10.1007/978-3-319-57076-1_2
  23. Fan B, Yang W, Shen X. A comparison study of motivation-intention-behavior model on household solid waste sorting in China and Singapore. J Clean Prod. 2018 doi: 10.1016/j.jclepro.2018.11.168. [DOI] [Google Scholar]
  24. Fedotkina O, et al (2019) Circular economy in Russia : drivers and barriers for waste management development. Sustainability 1–21
  25. Fukuda K. Science, technology and innovation ecosystem transformation toward society 5.0. Int J Prod Econ. 2020;220(April):107460. doi: 10.1016/j.ijpe.2019.07.033. [DOI] [Google Scholar]
  26. Gaeta GL, et al. Innovation in the solid waste management industry : integrating neoclassical and complexity theory perspectives. Waste Manag. 2021;120:50–58. doi: 10.1016/j.wasman.2020.11.009. [DOI] [PubMed] [Google Scholar]
  27. Gu F, et al. An integrated architecture for implementing extended producer responsibility in the context of Industry 4.0. Int J Prod Res. 2018;7543:1–20. doi: 10.1080/00207543.2018.1489161. [DOI] [Google Scholar]
  28. Janmaimool P (2017) Application of protection motivation theory to investigate sustainable waste management behaviors. Sustainability 1–16. 10.3390/su9071079
  29. Joshi R, Ahmed S (2016) Status and challenges of municipal solid waste management in India : a review. Cogent Environ Sci 1–18. 10.1080/23311843.2016.1139434
  30. Kamis A, et al. Items’ validity and reliability using Rasch measurement model for factors that influence clothing disposal behaviour. Indian J Public Health Res Dev. 2018;9(11):1344–1353. doi: 10.5958/0976-5506.2018.01640.6. [DOI] [Google Scholar]
  31. Li L. China’s manufacturing locus in 2025: with a comparison of “Made-in-China 2025” and “Industry 4.0”. Technol Forecast Soc Change. 2018;135(February 2017):66–74. doi: 10.1016/j.techfore.2017.05.028. [DOI] [Google Scholar]
  32. Linacre J (2002) Understanding Rasch measurement: optimizing rating scale category effectiveness. J Appl Meas [PubMed]
  33. Linacre JM (2009) Local independence and residual covariance: a study of olympic figure skating ratings. J Appl Meas 10(2) [PubMed]
  34. Lingard H, Graham P, Smithers G (2000) Employee perceptions of the solid waste management system operating in a large Australian contracting organization : implications for company policy implementation. Constr Manag Econ 37–41. 10.1080/01446190050024806
  35. Luiz A, Basto L, Pinguelli L. The declared barriers of the large developing countries waste management projects : the STAR model. Waste Manage. 2016 doi: 10.1016/j.wasman.2016.03.023. [DOI] [PubMed] [Google Scholar]
  36. Ma AJ, Hipel KW, Hanson ML. An Analysis of influencing factors on municipal solid waste source-separated collection behavior in Guilin, China by using the theory of planned behavior. Sustain Cities Soc. 2017 doi: 10.1016/j.scs.2017.11.037. [DOI] [Google Scholar]
  37. Mahpour A. Prioritizing barriers to adopt circular economy in construction and demolition waste management. Resour Conserv Recycl. 2018;134(November 2017):216–227. doi: 10.1016/j.resconrec.2018.01.026. [DOI] [Google Scholar]
  38. Manaf LA, et al. Municipal solid waste management in Malaysia : practices and challenges. Waste Management. 2009;29(11):2902–2906. doi: 10.1016/j.wasman.2008.07.015. [DOI] [PubMed] [Google Scholar]
  39. Manavalan E, Jayakrishna K. A review of Internet of Things (IoT) embedded sustainable supply chain for industry 40 requirements. Comput Ind Eng. 2018 doi: 10.1016/j.cie.2018.11.030. [DOI] [Google Scholar]
  40. Marais I, Andrich D (2008) Effects of varying magnitude and patterns of response dependence in the unidimensional Rasch model. J Appl Meas 9(2) [PubMed]
  41. Masrom NR, Rahman NAA, Daut BAT. Industrial solid waste management for better green supply chain : barriers and motivation. Int J Human Technol Interact Companies. 2018;2(1):97–106. [Google Scholar]
  42. Milea A (2009) Waste as a social dilemma: issues of social and environmental justice and the role of residents in municipal solid waste management, Delhi, India, Lund University, (May)
  43. Mondal C, Giri BC. Investigating strategies of a green closed-loop supply chain for substitutable products under government subsidy. J Ind Prod Eng. 2021 doi: 10.1080/21681015.2021.1974962. [DOI] [Google Scholar]
  44. Moh Y, Manaf LA. Solid waste management transformation and future challenges of source separation and recycling practice in Malaysia. Resour Conserv Recycl. 2020;116(2017):1–14. doi: 10.1016/j.resconrec.2016.09.012. [DOI] [Google Scholar]
  45. Mona I, Bakar MA, Hasim MS, Anuar MK, Sipan I, Nor MZM (2016) Data quality control for survey instrument of office investors in rationalising green office building investment in Kuala Lumpur by the application of Rasch analysis. Emerald insight
  46. Ncube LK, et al. An overview of plasticwaste generation and management in food packaging industries. Recycling. 2021;6(1):1–25. doi: 10.3390/recycling6010012. [DOI] [Google Scholar]
  47. Negash YT, et al. Sustainable construction and demolition waste management in Somaliland: regulatory barriers lead to technical and environmental barriers. J Clean Prod. 2021;297:126717. doi: 10.1016/j.jclepro.2021.126717. [DOI] [Google Scholar]
  48. Norizan E, et al. Measuring awareness of waste management among school children using Rasch Model analysis. Int J Soc Human Sci. 2012;6(8):555–558. [Google Scholar]
  49. Horodytska O, Cabanes A (2019) Plastic waste management: current status and weaknesses, The Handbook of Environmental Chemistry. Springer, Berlin, Heidelberg. 10.1007/698
  50. Pariatamby A, Solutions S. Municipal solid waste management in Asia and the Pacific Islands. Environmental Science: Springer; 2014. [Google Scholar]
  51. Pham Phu ST, Hoang MG, Fujiwara T. Analyzing solid waste management practices for the hotel industry. Global J Environ Sci Manag. 2018;4(1):19–30. doi: 10.22034/gjesm.2018.04.01.003. [DOI] [Google Scholar]
  52. Ranta V, et al (2018) Exploring institutional drivers and barriers of the circular economy: a cross-regional comparison of China, the US, and Europe. Resour Conserv Recycl 135.10.1016/j.resconrec.2017.08.017
  53. Ritzén S, Sandström GÖ (2017) Barriers to the Circular economy - integration of perspectives and domains, in Procedia CIRP. 10.1016/j.procir.2017.03.005
  54. Schauberger G, Mair P (2020) A regularization approach for the detection of differential item functioning in generalized partial credit models. Behav Res Methods 52(1). 10.3758/s13428-019-01224-2 [DOI] [PubMed]
  55. Simon J, et al. Mass customization model in food industry using industry 4.0 standard with fuzzy-based multi-criteria decision making methodology. Adv Mech Eng. 2018;10(3):1–10. doi: 10.1177/1687814018766776. [DOI] [Google Scholar]
  56. Taylor P, et al (2015) Characterization of NORM solid waste produced from the petroleum industry. Environ Technol (March 2015) 37–41. 10.1080/09593330.2014.982713 [DOI] [PubMed]
  57. Teece D, Pisano G. The dynamic capabilities of firms: an introduction. Ind Corp Chang. 1994;3(3):537–556. doi: 10.1093/icc/3.3.537-a. [DOI] [Google Scholar]
  58. Thissen D, Orlando M (2021) Item response theory for items scored in more than two categories. 10.4324/9781410604729-9
  59. Tiew K-G, Basri NEA, Zain SM, Kohei Watanabe WNAWM. Assessment of factors attracting waste recycler behaviors by Rasch model. Jurnal Teknologi. 2015;1(2015):63–70. [Google Scholar]
  60. Tsai FM, et al. A causal municipal solid waste management model for sustainable cities in Vietnam under uncertainty: a comparison. Resources, Conservation and Recycling. 2020;154(November 2019):104599. doi: 10.1016/j.resconrec.2019.104599. [DOI] [Google Scholar]
  61. Veleva V, Bodkin G (2017) New business model innovations and collaborations to support, Innovation management, entrepreneurship and sustainability
  62. Wee MAA, Seow T. Municipal solid waste management in Malaysia. ICHHE. 2014;1957:192–206. [Google Scholar]
  63. Wolins L, Wright BD, Rasch G (1982) Probabilistic models for some intelligence and attainment tests. J Am Stat Assoc 77(377). 10.2307/2287805.
  64. Wright BD, Linacre JM (1994) Reasonable mean-square fit values. Rasch Measurement Transactions 8(2)
  65. Yukalang N, Clarke B, Ross K (2017) Barriers to Effective municipal solid waste management in a rapidly urbanizing area in Thailand. Int J Environ Res Public Health 9–14. 10.3390/ijerph14091013. [DOI] [PMC free article] [PubMed]
  66. Zorpas AA, et al. Solid waste from the hospitality industry in Cyprus. WIT Press. 2021;166:41–49. [Google Scholar]

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