Abstract
Purpose
This research aims to examine the complementary impact of Lean Manufacturing (LM) and Green Manufacturing (GM) on operational and environmental performance.
Design/methodology/approach
A survey was conducted in the Zimbabwean manufacturing industry. A total of 302 valid responses were obtained and analysed using partial least square structural equation modelling (PLS-SEM).
Findings
Both LM and GM impact environmental and operational performance; however, GM's effect on operational performance is indirect through environmental performance.
Research limitations/implications
This study only focusses on the Zimbabwean manufacturing industry, and the results may not readily apply to other developing countries.
Practical implications
The companies that have successfully implemented LM are able to implement GM more easily because of their complementary nature.
Social implications
The integration of LM and GM reduces most forms of waste, causing an improved environmental and operational performance. In addition, this will improve community relations and customer satisfaction.
Originality/value
This research investigates the complementary nature of LM and GM on how LM and GM impact organisational performance and whether a combined Lean-Green implementation leads to better organisational performance than when LM and GM are implemented individually. The research also examines whether being environmentally compliant leads to improved organisational performance, particularly in a developing country.
Keywords
Citation
Machingura, T., Adetunji, O. and Maware, C. (2024), "A hierarchical complementary Lean-Green model and its impact on operational performance of manufacturing organisations", International Journal of Quality & Reliability Management, Vol. 41 No. 2, pp. 425-446. https://doi.org/10.1108/IJQRM-03-2022-0115
Publisher
:Emerald Publishing Limited
Copyright © 2023, Tinotenda Machingura, Olufemi Adetunji and Catherine Maware
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
Whilst the rapid industrialisation of countries around the world has led to significant improvement in the economies, it also negatively impacted the environment (Ramos et al., 2018). Furthermore, customers have increased their demand for improved quality products at lower cost and, more recently, reduction of the environmental effects of the production of goods and services (Garza-Reyes, 2015). Environmental issues are, therefore, considered as a competitive differentiation tool (Leme et al., 2018). Also, the introduction of multicurrency in Zimbabwe induced instability in the economy (Maware and Adetunji, 2019a), and the gross domestic product (GDP) contracted by 8% between 2019 and 2020 (World Bank, 2021).
Such business environments pressure manufacturing organisations into implementing methodologies such as Lean Manufacturing (LM) and Green Manufacturing (GM) to help them address environmental issues (Ramos et al., 2018), improve customer satisfaction and improve profitability. LM aims to reduce operational non-value-added activities such as excess inventory, waiting and defects (Ohno, 1988), whilst GM focusses on reducing negative environmental impacts like pollution and greenhouse gas emissions (Mohanty and Deshmukh, 1999).
The integration of LM and GM has gained popularity in both industry and academia due to their synergistic effect and the improvements they bring to organisations (Ramos et al., 2018; Leme et al., 2018). LM and GM may be complementary in three main areas: waste minimisation, process centredness and a high degree of people involvement (Fercoq et al., 2016). They both seek to solve problems and search for improvements through employee involvement (Ramos et al., 2018). Although LM and GM have different approaches and origins, they both aim at cost reduction through efficient resource utilisation where possible (Bhattacharya et al., 2019). Also, they improve the company's image, reduce risks, increase revenue (Fercoq et al., 2016), improve productivity, optimise resource usage and improve the quality of products and services (Ramos et al., 2018). Integrating LM and GM can make manufacturing companies competitive and increase profits, which is the goal of most organisations (Fercoq et al., 2016; Bhattacharya et al., 2019; Thekkoote, 2022) and hence regarded as vital techniques that are deployed to improve financial and environmental performances (Kuo and Lin, 2020).
Whilst some aspects between Lean and Green may be contradictory, Green practices usually present opportunities to improve Lean performance, therefore, companies that adopt GM with LM may attain better results than those that don't (Fercoq et al., 2016; Cherrafi et al., 2018). King and Lenox (2001) emphasised that Lean can be considered Green as it acts as a catalyst to achieve improved GM results, and hence, researchers are exploring the synergistic effects between the two concepts to attain common benefits (Bhattacharya et al., 2019). Thus, the purpose of this research is to investigate the impact of LM and GM on environmental and operational performance and compare the effects of their joint and individual implementations.
To address the objectives of this research, a survey was conducted in the Zimbabwean manufacturing industry. Most studies that have been conducted in Zimbabwe have also focussed on the individual implementation of LM and GM. For example, Goriwondo et al. (2013) and Maware and Adetunji (2019a) highlighted the impact of implementing LM on operational performance, whilst Kusena et al. (2014) realised the improvements in environmental performance as a result of GM implementation. Thus, creating questions on whether these organisations should simultaneously adopt LM and GM or not. Hence, this research provides answers to such gaps.
2. Literature review
2.1 Lean manufacturing
LM considers waste as the use of resources for any goal that does not create value for the customer (Pampanelli et al., 2014). Fercoq et al. (2016) pointed out that traditionally LM focussed on seven types of waste, which are, defects, over-processing, excessive transportation, over-production, unnecessary inventory, unnecessary motion and waiting. They also noted that environmental waste could be considered the eighth waste. Clients are not keen to pay for these non-value-adding activities which impact quality, costs and performance (Cherrafi et al., 2018). LM has contributed to a high level of production efficiency for decades and has been denoted as a perfect way to run manufacturing organisations (Pampanelli et al., 2014). It has been adopted in management practices because it provides ways to improve performance (Kuo and Lin, 2020).
2.2 Lean manufacturing implementation in Zimbabwe
In Zimbabwe, various studies have been reported on the implementation of LM practices. Maware and Adetunji (2019a) reported an improvement in operational performance by applying Jidoka, stability and standardisation, just-in-time (JIT) and employee involvement. A study by Muchaendepi et al. (2019) on small and medium enterprises (SMEs) concluded that JIT is the most deployed strategy for inventory management and performance improvement. Madanhire and Mbohwa (2016) applied JIT and total quality management (TQM) in the aluminium foundry industry and realised improvement in operational performance. Ngwenya et al. (2016) examined the challenges faced in implementing TQM at a beverage company, some of which are economic challenges, resistance to change and inadequate funding.
2.3 Green manufacturing
GM is the application of environmental, economic and technological strategies to processes and products to improve the utilisation of resources and reduce the negative environmental impact over the entire life cycle of the products (Ramos et al., 2018; Leong et al., 2020). The fast rate of depletion of natural resources makes them scarce and expensive, making GM implementation a viable option; moreover, overuse of these resources leads to massive environmental damage (Fercoq et al., 2016). Hines (2004) stated that the negative environmental impact is caused by greenhouse gases, excessive power usage, pollution, eutrophication, poor health and safety control, excessive water usage, excessive resource usage and rubbish. Thus, GM protects the environment by reducing toxic materials, using environmental-friendly processes and raw materials, designing for the environment, recycling and remanufacturing (Leme et al., 2018).
2.4 Green manufacturing and its implementation in Zimbabwe
Evidence of GM implementation has been reported by Zimbabwe's manufacturing industry. Mbohwa (2002) stated that Zimbabwe could learn the development of GM technologies from Japanese companies in areas such as electronic environmental management. Mutubuki and Chirinda (2021) analysed how GM can be used in the food industry and suggested Green practices including recycle, reuse and reduce (3R) and green packaging. Masike and Chimbadzwa (2013) applied life cycle management (LCM), environmental accounting, eco-efficiency, energy and waste management in the foundry industry to improve material, operations, environmental and energy efficiency. Machingura and Zimwara (2020) outlined a GM framework that can be adopted by manufacturing companies in Zimbabwe.
2.5 Integration of LM and GM in developing countries
Whilst implementing LM and GM separately by many manufacturing companies has helped to improve their operations, Baumer-cardoso et al. (2020) stated that LM and GM, when combined, can yield better results than alone. No case of LM and GM integration has been reported in Zimbabwe; however, other developing countries have made attempts. A study by Farias et al. (2019) in Brazil developed a framework to evaluate the impact of LM and GM on organisational performance. Huo et al. (2019) concluded that Lean-Green positively impacts sustainable development in China. Thanki et al. (2016) identified international organisation for standardisation (ISO) 14001 and total preventive maintenance (TPM) as the most influential Lean-Green practices in India. Dawood and Abdullah (2018) applied value stream mapping (VSM) and 3R in a cement-manufacturing company in Iraq, stating that these practices have a significant impact.
2.6 Research gap and problem statement
Although GM can be complementary to LM on environmental efficiency improvement Farias et al. (2019) acknowledged that there is little evidence of their successful integration, and the elements that allow for assessing Lean-Green on performance are still unknown. Garza-Reyes (2015) added that research focussing on the impact of Lean-Green practices on organisational performance is limited and inconclusive. Furthermore, many organisations have not benefited from Lean-Green due to a lack of a systematic implementation system, leading to haphazard implementations (Leong et al., 2019).
It also seems like developing countries lag in implementing LM and GM, compared to developed countries (Panizzolo et al., 2012; Fu et al., 2017; Machingura and Zimwara, 2020). There is a lack of a standard measurement model to assess the impact of implementing these methodologies, and the companies are not sure which practices to adopt and the effect of such adoptions on their performance (Maware and Adetunji, 2019a). This makes management hesitant and sceptical about implementing these improvement philosophies (Maware and Adetunji, 2019b). Since both are based on continuous improvement, it is essential to assess the impact of their joint implementation on organisational performance (Farias et al., 2019). Further research is, therefore, needed to address this gap in Lean-Green implementation.
This research investigates whether integrating LM and GM yields better results than implementing either of these methodologies alone. To the best of the authors' knowledge, the research by Green et al. (2018) is the only paper that applied structural equation modelling (SEM) to evaluate the impact of simultaneously implementing JIT, TQM and Green supply chain management (GSCM) on environmental performance. Our research extends this knowledge by using four bundles of LM, namely JIT, TPM, human resource management (HRM) and TQM instead of using JIT and TQM only. In addition, instead of using GSCM only, our research used LCM, 3R and Green purchasing. A higher-order model was used in this research, where the factors for LM and GM were separated so that LM factors only affect LM directly and GM factors only affect GM directly, and their mediation is studied separately. More importantly, this research examines the impact of LM and GM on operational performance in addition to the mediatory environmental performance impact. Also, Inman and Green (2018) investigated the impact of LM and GSCM on environmental and operational performance. Although a higher-order model was used, that research did not investigate the impact of simultaneously implementing LM and GM, thus, not addressing whether simultaneous implementation yields better results than individual implementations.
3. Hypotheses formulation and development of the research model
A second-order structural model was developed to examine the impact of LM and GM on organisational performance. This model, as shown in Figure 1, consisted of one endogenous variable, which is the operational performance and three exogenous variables, namely GM, LM and environmental performance. LM and GM are second-order latent variables, whereas 3R, LCM and Green purchasing are first-order latent variables for GM, whilst JIT, TQM, TPM and employee involvement are the first-order latent variables for LM. Several previous studies grouped the LM practices into four bundles, namely JIT, TPM, HRM and TQM (Shah and Ward, 2003; Taj and Morosan, 2011; Bortolotti et al., 2015; Arumugam et al., 2020); therefore, these practices were adopted for this study. Additionally, Khan et al. (2019) applied Green purchasing whilst Dawood and Abdullah (2017) used 3R and realised an improvement in organisational performance, whereas Dües et al. (2013) mentioned that LCM is the principal GM tool. As a result, this motivated the authors to adopt all these LM and GM practices and examine the complementary impact of LM and GM implementations.
Elimination of wastes like defects, over-processing and overproduction are critical goals of LM, which have been reported to support the GM philosophy as they consequently result in efficient use of resources such as water, energy and raw materials, which are important aims of GM. Thus, LM outlines a way for the improved utilisation of resources (Pampanelli et al., 2014), and this indirectly helps in the achievement of GM objectives. Lean practices are, therefore, treated as Green because their objectives, in this sense, are in line with saving resources (Fercoq et al., 2016). The study by Thekkoote (2022) in South Africa's SMEs also found that LM has a positive relationship with GM. Kuo and Lin's (2020) study demonstrated that LM positively influences Green operations. It can, therefore, be hypothesised as follows:
LM is positively related to GM.
LM has been traditionally employed to minimise the seven wastes; however, Fercoq et al. (2016) acknowledged that Lean practices may also reduce negative environmental impact. Several articles have indicated that LM has a positive impact on environmental performance. For example, Kamble et al. (2020) concluded that LM had a significant effect on environmental performance. The research of Jabbour et al. (2013) in the automotive industry concluded that a strong relationship exists between LM and environmental performance. The Lean practices employed were TPM and JIT. The objective of JIT is to ensure that the right quantity of resources is provided at the right time, thus preventing unnecessary inventory (Arumugam et al., 2020). Balaji and Logesh (2020) added that the goal of LM is to eliminate defects and manage inventory. TPM aims to increase equipment efficiency and reduce waste through maintenance such as lubrication, cleaning and calibration (Jabbour et al., 2013). Thus, those organisations that adopt LM achieve high levels of pollution prevention due to inventory reduction, amongst other things. Therefore, it is hypothesised as follows:
LM is positively related to environmental performance.
Manufacturing companies are implementing Lean practices such as TQM, JIT and TPM to improve quality and productivity. In Zimbabwe, Maware and Adetunji's (2019a) study on manufacturing companies highlighted that LM positively impacts operational performance. The authors added that the integration of people in LM allows for the involvement, motivation and training of workers, hence creating room for improvement. Pampanelli et al. (2014) outlined that the main goal of LM is to improve delivery, quality and reduce cost. Farias et al. (2019) emphasised that the implementation of LM made organisations improve their operational performance. In addition, the authors stated that successful LM implementation leads to improved utilisation of resources. Baumer-cardoso et al. (2020) applied LM in a Brazilian job shop and realised a reduction in setup time and energy consumption leading to a significant decrease in costs. Hence, it can be hypothesised as follows:
LM is positively related to operational performance.
The GM philosophy has been well recognised for reducing negative ecological issues (Garza-Reyes, 2015). It aims to improve, control and monitor pollution levels, minimise the impact of manufacturing processes on the environment as well as provide for efficient use of resources (Farias et al., 2019). It examines environmental impact related to the unnecessary use of energy or water, eutrophication and the greenhouse effect (Baumer-cardoso et al., 2020). GM advocates for eliminating solid wastes, hazardous wastes, air emissions, wastewater discharge and other forms of pollution (Abualfaraa et al., 2020). It supports the use of processes and manufacturing products that do not harm the environment (Mudgal et al., 2009). Chiou et al. (2011) stated that greening the processes positively impacts environmental performance. GM was found to have a strong relationship with environmental performance (Belhadi et al., 2020). It can, therefore, be hypothesised as follows:
GM is positively related to environmental performance.
GM's objective is to reduce pollution levels and provide efficient resource usage (Qureshi et al., 2015). If water, energy, raw materials and other resources can be used efficiently, costs can also be reduced, leading to improved operational performance. The research in the Chinese fashion industry concluded that GM implementation positively affects the performance of organisations (Li et al., 2019). The study by Rehman et al. (2013) in the Indian steel industry concluded that the implementation of GM improves operational performance. Green practices were found to impact Pakistani manufacturing organisational performance (Khan et al., 2019). Thus, it can be hypothesised as follows:
GM is positively related to operational performance.
The study by Jabbour et al. (2013) in the Brazilian industry outlined that environmental performance positively influences operational performance. The operational performance measures used are cost, quality, flexibility and delivery. The study done on Chinese manufacturing companies concluded that the implementation of environmental policies positively impacts company performance (Zhang and Du, 2020). It was also noted that environmental collaboration plays a significant part on organisational performance (Chin et al., 2015). According to research in Thailand's food industry, environmental performance improves operational performance in this industry (Pipatprapa et al. 2016). Thus, it can be hypothesised as follows:
Environmental performance is positively related to operational performance.
Over the past years, LM and GM have been implemented separately to improve organisational performance. Nevertheless, currently, researchers have noted that when LM and GM are combined, they tend to yield better results than when implemented alone (Fercoq et al., 2016; Cherrafi et al., 2018; Ramos et al., 2018; Baumer-Cardoso et al., 2020). Green et al. (2018) combined JIT, TQM and GSCM and figured out that when these practices are combined, they have a larger impact than when implemented individually. Hence, it can be hypothesised as follows:
Integrated LM and GM have a greater impact on environmental performance than individually.
Integrated LM and GM have a greater impact on operational performance than individually.
All these hypotheses taken together allowed for the development of a structural model for evaluating the integrated impact of Lean–Green on environmental and operational performance. The model is illustrated in Figure 1.
4. Methodology
4.1 Questionnaire development
A self-administered questionnaire was developed to assess the impact of Lean-Green implementation on the environmental and operational performance of manufacturing companies. To enhance the validity of the questionnaire, it is usually recommended to adopt questions from the literature (Murillo-Luna et al., 2011; Huo et al., 2019; Shashi et al., 2019). The questions for this research were extracted from (Nawanir et al., 2013; Godinho Filho et al., 2016; Inman and Green, 2018; Iranmanesh et al., 2019; Yadav et al., 2019). The questionnaire contained four sections. Section A focussed on the general information about the company. Section B outlined the level of LM adoption by manufacturing companies. Section C covered the level of GM adoption. Section D focussed on the impact of implementing selected Lean-Green practices on environmental and operational performance. A five-point Likert scale was used with ratings: 1 = strongly disagree, 2 = disagree, 3 = neutral, 4 = agree and 5 = strongly agree. These ratings specified the degree of agreement or disagreement with the given statements. The questionnaire was pretested by sending it to experts from the industry and academia to improve its validity (Murillo-Luna et al., 2011; Jabbour et al., 2013; Huo et al., 2019; Cherrafi et al., 2018; Belhadi et al., 2020). As a result, some questions were removed, others were modified and some were added. The questions that were finally developed were used for data collection (see Appendix).
4.2 Data collection
Data was collected from manufacturing companies across Zimbabwe. Currently, they are 430 manufacturing companies registered with the Confederation of Zimbabwe Industries (CZI). A total of 782 questionnaires were sent to respondents within these 430 companies. The authors were targeting more than 1 response from each company and hence decided to send 2 to 3 questionnaires to each company so that in case of individual biases, the responses counterbalance each other as recommended by Maware and Adetunji (2019b). To increase the response rate, several follow-ups were made through emails, telephone calls (Jabbour et al., 2013; Huo et al., 2019; Belhadi et al., 2020) and WhatsApp messaging (Diabat and Govindan, 2011). Personnel in higher positions such as operations, quality and environmental managers were invited to participate in the study. The manufacturing and safety, health, environment and quality (SHEQ) departments were chosen because these are the areas that are responsible for the operational and environmental performance measures (Jabbour et al., 2013). The responses were kept anonymous with a high level of confidentiality (Murillo-Luna et al., 2011). Initially, 313 questionnaires were returned as some personnel did not respond. The questionnaires were screened, and 302 valid and useable responses were obtained. A total of 11 questionnaires were incomplete and were discarded. This gave a response rate of 38.6%. The response rate is high enough considering the questionnaire was completed by manufacturing personnel who are usually busy as also acknowledged by Kuo and Lin (2020). Also, based on the 10-times rule specified by Hair et al. (2017), the minimum sample size is 120; therefore, we considered the sample to be adequate as we were well above the minimum limit.
4.3 Non-response bias
Non-response bias was determined using the early and late responses method described by Armstrong and Overton (1977). A total of 5 items were randomly chosen from the questionnaires to compare the first 20 and last 20 responses. The results of the t-tests showed no significant difference at the 0.05 significance level, implying a lack of non-response bias that could have affected the results (Chavez et al., 2022).
5. Data analysis and results
Data analysis was done using the SmartPLS 3 and Statistical Package for Social Sciences (SPSS) version 26. SPSS was deployed for the descriptive statistics and Exploratory Factor Analysis (EFA), whilst SmartPLS was used for SEM to assess and validate the proposed relationships between the variables. PLS-SEM is more applicable when testing hypotheses and relationships that contain second-order latent variables (Inman and Green, 2018).
5.1 Profile of participants
The distribution of the companies is indicated in Table 1. The highest responses per sector were 89 from the food and beverage sector and 33 from the plastic and rubber sector.
The majority of the participants indicated that they have more than 5 years of experience in their current positions. This experience is good enough to respond to the items on the questionnaire (Huo et al., 2019).
5.2 Assessment of the measurement scale
The Bartlett's test of sphericity had a p-value less than 0.001, showing that it is significant. The sample size of 302 was adequate as indicated by the Kaiser–Meyer–Olkin (KMO) value of 0.903. Jabbour et al. (2013) noted that a KMO value closer to 1 indicates an adequate sample. The total variance explained obtained for the latent variables was 63.4%. The measurement scale's reliability was assessed using Cronbach's alpha and composite reliability (Green et al., 2018). The Cronbach's alpha values were all > 0.7; hence, they are acceptable (Nunnally, 1978; Zhu and Sarkis, 2004; Firmansyah and Maemunah, 2021). The composite reliability values should be > 0.7, reflecting high internal consistency. The composite reliability values were all > 0.7. The average variance extracted (AVE) is used to assess the convergent validity where values > 0.5 indicate a strong convergent validity (Hair et al., 2017). The AVE values obtained in this research were > 0.5. Firmansyah and Maemunah (2021) noted that outer loadings could be used to assess convergent validity, where variables with values > 0.5 are considered valid. As seen from the model in Figure 2, all the outer loadings were > 0.5 (see Table 2).
Discriminant validity was assessed using the Heterotrait-Monotrait ratio (HTMT) ratio. As shown in Table 3, all the constructs exhibited discriminant validity as the HTMT values were all < 0.85 (Hair et al., 2017). Therefore, the scale denotes enough reliability and validity; thus, the variables can be used for further research on hypotheses evaluation.
5.3 Structural model assessment
The variance inflation factor (VIF) values indicate that there was no collinearity problem as they were all below 5 and above 0.2 (Hair et al., 2017). The coefficient of determination (R2) indicates the predictive power of the model. According to Cohen (1988), R2 values greater than 0.26 are substantial, 0.13 are moderate and 0.02 are weak. Hair et al. (2017) also mentioned that the R2 values depend on how complex the model is; therefore, R2 value of 0.20 can be considered high. The R2 values of 35.6, 36.5 and 51.0% were obtained for GM, environmental performance and operational performance, respectively. The R2 for TQM was 73.5%, JIT was 73.1%, TPM was 74.2%, employee involvement was 57.2%, LCM was 79.7%, 3R was 48.5 and green purchasing was 86.1%. The results show that the model had high predictive power and that LM and GM constructs are good environmental and operational performance predictors.
The effect size, f2, is used to determine the impact of an omitted exogenous variable on the endogenous variable. The f2 values of 0.35, 0.15 and 0.02 demonstrate large, medium and small effects, respectively (Hair et al., 2017). Table 4 highlights that most of the relationships have a large effect. The relationship between GM and operational performance was denoted by a small effect whilst LM to environmental performance relationship had a medium effect. The Stone–Geisser's Q2 value indicates the predictive relevance of the model (Firmansyah and Maemunah, 2021). Q2 values greater than 0 shows the path model's predictive relevance (Hair et al., 2017). All the Q2 values obtained were larger than 0, showing good predictive power as shown in Table 5.
The significance of the paths was determined through the bootstrapping method using 5,000 subsamples (Godinho Filho et al., 2016; Ghobakhloo et al., 2018). Most of the proposed relationships are statistically valid as they have t-values above 1.96 and p-values lower than 0.05 at a 5% significant level (Hair et al., 2017). Thus, the t- and p-values failed to reject the hypotheses except for hypothesis H5. The H5 failed to satisfy the t- and p-values; hence, it was rejected as shown in Table 6.
To determine if the combined effect is stronger than singular impacts, the authors adopted the stepwise regression method, using LM first and GM second, and noted the increments in adjusted R2 (Green et al., 2018). Since GM is a newer methodology compared to LM, we assumed that organisations that are likely to implement GM have already adopted LM. In addition, since LM aims at reducing the seven wastes thereby having a positive impact on operational performance, whilst GM focusses on reducing environmental impact, organisations are likely to adopt LM before GM as most organisations are likely more interested in improving their operational performance ahead of environmental compliance.
LM and GM practices were stepwise regressed against environmental and operational performance. When LM was used as the first antecedent to environmental performance, the adjusted R2 found was 0.198. When GM was added as the second antecedent, the adjusted R2 increased by 0.16, from 0.198 to 0.358. Next, LM was also used as the first antecedent to operational performance and the adjusted R2 value of 0.282 was obtained. Again, GM was added as the second antecedent to operational performance and a 0.054 increase was noticed, yielding the adjusted R2 of 0.336. Finally, when environmental performance was added as the third antecedent to operational performance, the adjusted R2 increased to 0.502. The calculated t-values were greater than 1.96, indicating that these increments are significant at 0.05 level. Thus, the complementary relationship between LM and GM results in better environmental and operational performance, compared to individual practices. Therefore, hypotheses H7 and H8 are supported. This agrees with Leong et al. (2019) and Leong et al. (2020) who stated that integration of LM and GM practices yields improved environmental and operational performance.
To investigate if there is some form of heterogeneity in the pattern across industries based on possible levels of pollution, further analysis was done by clustering companies into two categories depending on their position in the supply chain. Since Zimbabwe as a country does not have manufacturing companies in sectors like oil exploration, refinery or steel manufacturing, industry clusters were created based on the type of supply chain processes involved and the level of integration inherent in the manufacturing processes. Category 1 consists of companies that work across an entire chain and convert raw materials to finished products. These sectors include food and beverage, agrochemical, tile and brick, wood and furniture, leather, paper and fertiliser. Category 2 is made up of companies that import semi-finished products and process them into finished products. These include chemical and petrochemical, plastic and rubber, pharmaceutical, electronics and electrical, textile, ceramic, steel working, automotive, battery and foundry. It is believed that the processes of these two categories should suffice to understand different GM footprints based on the manufacturing processes, and therefore, they might produce different results (see Table 7).
The results led to similar conclusions and indicated that Lean-Green yielded identical improvements in both categories. Lean-Green makes organisations improve their environmental and operational performance. LM has a positive relationship with operational and environmental performance, whilst GM has a positive relationship with environmental performance. Furthermore, GM has no positive relationship with operational performance, but the relationship is indirect through environmental performance.
6. Discussion of the results
This study investigated the impact of adopting LM and GM on the environmental and operational performance of manufacturing companies in Zimbabwe. Lean-Green has emerged as a new and essential manufacturing philosophy that can be adopted by manufacturing companies to achieve competitive advantage (Basha et al., 2020; Siegel et al., 2022). In addition, the renewed focus on environmental requirements by regulators and customers has pushed organisations to reduce environmental pollution by adopting techniques such as Lean-Green (Huo et al., 2019). Researchers have recently started investigating the relationship between LM and GM and how they mutually affect organisational performance. Nevertheless, there are still many opportunities for research in this area, especially in developing countries where such work seems to be lagging.
Many manufacturing companies seemed hesitant to implement Lean-Green. They are unsure which practices to implement and the benefits of such implementations. Therefore, this research tackles this by providing evidence of the benefits of implementing Lean-Green practices. The results support the assertion that when integrated, LM and GM positively impact environmental and operational performance. LM was found to directly impact both environmental and operational performance. This is consistent with earlier studies such as Inman and Green (2018). Earlier studies also reported a positive relationship between LM and environmental performance (Ghobakhloo et al., 2018; Green et al., 2018). The impact of LM on operational performance is also supported by Jabbour et al. (2013), Nawanir et al. (2013), Godinho et al. (2016) and Lara et al. (2022). In contrast, the research by Khalfallah and Lakhal (2020) highlighted that TQM, JIT and TPM do not have a positive influence on operational performance.
GM was found to have a positive relationship with environmental performance. This agrees with the study conducted in the Indonesian manufacturing and logistics industry (Firmansyah and Maemunah, 2021). The results failed to support the hypothesis that GM has a direct positive relationship with operational performance; nevertheless, it depicted that GM indirectly impacts operational performance through environmental performance. GM was found to be positively related to environmental performance, whilst environmental performance was found to have a positive relationship with operational performance. Thus, although there is no positive relationship between GM and operational performance, an indirect relationship exists through environmental performance. According to Figure 2, the direct path weight between GM and operational performance is −0.061, whilst the indirect effect through environmental performance is 5 times greater, thus 0.275 (0.498 times 0.553). The primary aim of GM is to reduce environmental impact regardless of the cost and lead time implications. In other words, the finding here is that improvement in operational performance is not directly achieved through GM implementation but from the consequences of improvements in environmental performance attained by implementing GM. This is consistent with the USA firms' survey (Inman and Green, 2018).
This finding is particularly important as the model by Green et al. (2018) that has previously studied the integrated Lean-Green impact on performance did not separate the direct impact of the lower level factors of Lean on Green and those lower level factors of Green on Lean, but rather connected all the lower level factors to each of these two factors. Consequently, this model might have lumped together both the direct and indirect effects of Lean and Green implementations on the performances measured. In addition, separating environmental effects from operational effects makes it possible to observe the role that environmental improvement plays in the integrated Lean-Green impact.
Therefore, those organisations integrating LM and GM, without paying attention to their environmental performance, may fail to realise the full benefits of the complementary relationship between LM and GM. Also, LM without GM significantly improved operational performance, but its impact on environmental performance is slightly lower. The indirect impact of LM on environmental performance through GM is greater than the direct impact, and this is another interesting finding. Thus, integrating LM and GM causes a significant improvement in environmental performance and further enhances operational performance. Furthermore, when the manufacturing companies were clustered into two different categories in the context of Zimbabwe, the results showed that Lean-Green positively impacts environmental and operational performance in both categories.
More importantly, the integration of LM and GM showed a greater impact, compared to the implementation of GM and LM separately. This agrees with an earlier study which found that combining LM and GM practices yields better results than implementing one of the methodologies (Green et al., 2018). This was also confirmed by Dües et al. (2013) who noted that LM acts as a catalyst for attaining better Green improvements. Lean practices aim to reduce non-value-adding operations, thereby increasing efficiency whilst GM aims to improve environmental performance (Firmansyah and Maemunah, 2021).
The results from this study also agree with other studies conducted in Zimbabwe. For instance, Maware and Adetunji (2019a) conducted a survey and reported improved operational performance through the implementation of LM, whilst in the pharmaceutical industry Goriwondo et al. (2013) adopted LM and also highlighted improved operational performance. In addition, the study by Kusena et al. (2014) indicated improvements in environmental performance through GM implementation in the cement industry.
In Zimbabwe, it seems no study has been conducted to evaluate the combined impact of Lean-Green on environmental and operational performance. Thus, this study sheds more light on the Zimbabwean manufacturing industry and encourages organisations to simultaneously implement LM and GM. Considering the economic challenges faced in Zimbabwe and also the increased environmental demands by regulators, combining LM and GM assists these organisations to meet both operational and environmental objectives.
7. Conclusion, implications, limitations and future research opportunities
7.1 Conclusion
This research examined the impact of implementing Lean-Green practices on organisational performance. The research objective was to explore the actual nature of the relationship between Lean and Green improvements and understand which paths in the relationship lead to which performance improvements, either directly or indirectly. It also seeks to shed more light on the impact of Lean-Green in the context of a developing country and assist those organisations that worry about adopting such methodologies. Particular attention was given to environmental and operational performance. It was discovered that Lean-Green has an impact on operational and environmental performance. Furthermore, integrating LM and GM practices has a significant influence, compared to LM and GM being implemented separately. Thus, those organisations that have already implemented LM should consider integrating it with GM to attain pronounced benefits. Furthermore, organisations intending to achieve operational benefits from their Green implementation need to pay particular attention to the role of environmental performance, as this is how the operational performance is enhanced. This makes sense since Green prescripts may demand large lot sizes, whilst Lean prescripts demand smaller lot sizes, which are generally contradictory, but the aggregate effect may produce better results than the sum of the individual parts.
7.2 Managerial implications
The research has demonstrated that Lean-Green positively impacts environmental and operational performance; therefore, the managers have been provided with knowledge on the benefits of integrating LM and GM. Particularly, the managers understand the relational paths of Lean-Green and their impacts on organisational performance, and consequently, the focus needs not only be on the direct impact, but also on the total impact. In addition, the study showed that although implementing Lean-Green requires resources, there are a lot of benefits associated with such implementations. Thus, the managers of manufacturing organisations should strive to implement Lean-Green and enjoy the benefits of such implementations. Furthermore, managers can benefit from reducing costs due to the elimination of waste and improvement in environmental sustainability. Hence, organisations can satisfy both Lean and Green customers as all their requirements will be fulfilled, thus increasing competitiveness.
Most studies that have been done focussed on the impact of implementing LM and GM separately. As a result, it seems managers are not sure of the actual impact of the simultaneous implementation of LM and GM and how it yields better results relative to the individual implementation of each. This study, however, bridges this gap by comparing the impact of simultaneously implementing LM and GM to their individual implementation and the pattern of achieving this result, especially the indirect paths. Hence, managers are now aware that when LM and GM are implemented simultaneously, they yield better results than their individual implementation. Also this research has demonstrated that GM may not have a direct impact on operational performance, but the relationship that is indirect through environmental performance is significant. Also the indirect impact of LM on environmental performance through GM provides further reinforcement of performance improvement. As a result, managers should know that to attain enhanced operational performance and improve competitiveness, there is a need to improve environmental performance through GM implementation. In addition, they now know that Lean-Green has a positive impact on companies regardless of where they operate within the supply chain.
7.3 Social implications
Traditional manufacturing methods tend to cause many negative environmental effects, such as increased carbon footprint, waste and energy consumption. However, socio-environmental issues are of great concern nowadays, with stakeholders, policymakers, communities and customers demanding organisations to adopt environmentally friendly and sustainable manufacturing. This research has demonstrated that both LM and GM positively impact environmental performance. The indirect impact of LM on environmental performance through GM is greater than the direct impact. Hence, organisations thinking of implementing LM alone should consider integrating it with GM for enhanced environmental performance. Improvements in environmental performance mean less environmental harm is caused to the communities and workplaces, thus probably improving the safety and health of workers and communities.
7.4 Study limitations and future opportunities
The research was conducted through a survey of the manufacturing companies in Zimbabwe only. Thus, the results are generalised as it focusses on many sectors of the manufacturing industry. Although Zimbabwe is a developing country, the business environment differs from one country to another; hence, the results may not be simply extrapolated for manufacturing companies in other developing countries, but may provide the norm for benchmark purposes. Thus, similar research can be conducted in other developing countries and results compared with those obtained in this study. Lean-Green is not limited to the manufacturing industry only; hence, it can be expanded to other sectors such as construction. Even though the research dwells on environmental sustainability, it may be imperative to extend it to different dimensions of sustainability; thus, the social construct may be further isolated in subsequent studies.
Figures
Type of industry
Type of industry | Number of respondents | % |
---|---|---|
Food and beverage | 89 | 29.5 |
Chemical and petrochemical | 24 | 7.9 |
Plastic and rubber | 33 | 10.9 |
Pharmaceutical | 6 | 2.0 |
Agrochemical | 17 | 5.6 |
Wood and furniture | 19 | 6.3 |
Electronics and electrical | 27 | 8.9 |
Fertiliser | 7 | 2.3 |
Textile | 15 | 5.0 |
Leather | 6 | 2.0 |
Paper | 10 | 3.3 |
Ceramic | 5 | 1.7 |
Steel working | 13 | 4.3 |
Tile and brick | 11 | 3.6 |
Automotive | 5 | 1.7 |
Battery | 7 | 2.3 |
Foundry | 8 | 2.6 |
Source(s): Author’s own work
Measurement reliability and validity
Cronbach's alpha | Composite reliability | AVE | |
---|---|---|---|
3R | 0.847 | 0.897 | 0.686 |
Employee Involvement | 0.751 | 0.834 | 0.502 |
Environmental performance | 0.886 | 0.913 | 0.636 |
Green Manufacturing | 0.926 | 0.936 | 0.501 |
Green Purchasing | 0.903 | 0.922 | 0.598 |
JIT | 0.83 | 0.876 | 0.543 |
Lean Manufacturing_ | 0.928 | 0.935 | 0.509 |
Life Cycle Management | 0.848 | 0.892 | 0.623 |
Operational performance | 0.856 | 0.893 | 0.582 |
TPM | 0.837 | 0.875 | 0.568 |
TQM | 0.86 | 0.891 | 0.507 |
Source(s): Author’s own work
HTMT values
3R | EI | EVP | GM | GP | JIT | LCM | LM | OP | TPM | |
---|---|---|---|---|---|---|---|---|---|---|
EI | 0.552 | |||||||||
EVP | 0.711 | 0.426 | ||||||||
GM | 0.788 | 0.517 | 0.652 | |||||||
GP | 0.519 | 0.404 | 0.505 | 0.763 | ||||||
JIT | 0.525 | 0.668 | 0.482 | 0.66 | 0.588 | |||||
LCM | 0.578 | 0.462 | 0.578 | 0.540 | 0.662 | 0.623 | ||||
LM | 0.519 | 0.317 | 0.496 | 0.639 | 0.575 | 0.556 | 0.587 | |||
OP | 0.515 | 0.541 | 0.758 | 0.515 | 0.42 | 0.568 | 0.46 | 0.596 | ||
TPM | 0.445 | 0.81 | 0.399 | 0.508 | 0.455 | 0.772 | 0.444 | 0.499 | 0.475 | |
TQM | 0.378 | 0.634 | 0.459 | 0.586 | 0.569 | 0.763 | 0.553 | 0.351 | 0.548 | 0.709 |
Note(s): EI = employee involvement, EP = environmental performance, GP = Green purchasing and OP = operational performance
Source(s): Author’s own work
The f2 values
3R | EI | EP | GM | GP | JIT | LCM | OP | TPM | TQM | |
---|---|---|---|---|---|---|---|---|---|---|
EP | 0.396 | |||||||||
GM | 0.943 | 0.352 | 6.207 | 3.918 | 0.024 | |||||
LM | 1.336 | 0.152 | 0.553 | 2.718 | 0.354 | 2.883 | 2.767 |
Source(s): Author’s own work
The Stone–Geisser's Q2 values
Endogenous variable | TPM | JIT | TQM | EI | LCM | 3R | GP | GM | EP | OP |
---|---|---|---|---|---|---|---|---|---|---|
Q2 | 0.340 | 0.390 | 0.364 | 0.282 | 0.490 | 0.320 | 0.509 | 0.161 | 0.224 | 0.288 |
Source(s): Author’s own work
t-statistics and p-values and decision on the hypotheses
t statistics | p values | Decision | |
---|---|---|---|
Environmental performance → Operational performance | 8.924 | 0.000 | Supported |
GM → Environmental performance | 6.777 | 0.000 | Supported |
GM → Operational performance | 0.973 | 0.331 | Not supported* |
LM → Environmental performance | 2.042 | 0.042 | Supported |
LM → GM | 11.955 | 0.000 | Supported |
LM → Operational performance | 5.377 | 0.000 | Supported |
Note(s): *The direct relation between GM and operational performance is not supported; the impact is indirect through environmental performance
Source(s): Author’s own work
Comparison of category 1 and category 2
Category 1 | Category 2 | |||||||
---|---|---|---|---|---|---|---|---|
Path weight | t-statistics | p-values | Decision | Path weight | t -tatistics | p-values | Decision | |
EP → OP | 0.390 | 2.105 | 0.036 | Supported | 0.546 | 4.933 | 0.000 | Supported |
GM → EP | 0.265 | 1.987 | 0.047 | Supported | 0.425 | 3.919 | 0.000 | Supported |
GM → OP | 0.073 | 0.312 | 0.755 | Not supported | −0.123 | 1.097 | 0.273 | Not supported |
LM → EP | 0.530 | 2.964 | 0.005 | Supported | 0.178 | 1.981 | 0.018 | Supported |
LM → GM | 0.756 | 8.688 | 0.000 | Supported | 0.650 | 10.776 | 0.000 | Supported |
LM → OP | 0.466 | 2.372 | 0.010 | Supported | 0.273 | 2.465 | 0.014 | Supported |
Source(s): Author’s own work
Appendix Measurement scale
Employee involvement
Our workers undergo cross-functional training;
The suggestions of the team members are considered before making decisions;
At our firm, we have an expansion of autonomy and responsibility;
In our company, the management takes all improvement suggestions seriously and
The employees are encouraged to work together to achieve common goals.
TPM
Our operators are trained to maintain their own machines;
Our equipment is always in a high state of readiness;
We keep the records of routine maintenance;
We maintain all our equipment regularly;
The equipment maintenance records are shared with all the shop floor employees;
Our operators understand the cause and effect of equipment deterioration;
Our operators inspect and monitor the performance of their own equipment and
Our operators can detect and treat abnormal operating conditions of their equipment.
JIT
Our customers receive just-in-time deliveries from us;
Our suppliers deliver to us on a just-in-time basis;
Our company involves all the key suppliers in the process;
The daily production schedule is met every day;
The daily production schedule is completed on time and
The layout of our shop floor facilitates low inventories and fast throughput.
TQM
Our equipment or processes are under statistical quality control;
We use statistical techniques to reduce variance;
Control charts are used to determine whether the manufacturing processes are in control;
The processes in the plant are designed to be “foolproof”;
The process ensures that all parts, materials, information and resources meet the specifications before use;
Our customers give us feedback on our quality and delivery performance;
We undertake programs for quality improvement and control and
Quality problems can be traced to their source and solved without reworking too many units.
3R
We optimise the processes to reduce water use;
We optimise the processes to reduce air emissions;
We optimise the processes to reduce energy use and
We design the products for reduced consumption of energy.
LCM
We systematically consider customer feedback for eco-design;
Our company considers its discharges as a wealth;
We recover the company's end-of-life products;
We consider the impact of products in their entire lifetime and
We monitor the environmental impact of the products at all stages.
GP
We coordinate with the suppliers for environmental objectives;
We perform the environmental audit for suppliers' internal management;
Our suppliers are ISO14000 certified;
We choose our suppliers by environmental criteria;
We urge/pressure our supplier(s) to take environmental actions;
We provide the design specification to suppliers that include environmental requirements for purchased items;
Our products are eco-labelled and
Our firm has an environmental purchasing policy in practice.
Environmental performance
We reduced the air emissions;
We reduced the solid waste;
We reduced the waste water;
We decreased the consumption of hazardous/harmful/toxic materials;
We decreased the frequency of environmental accidents and
We decreased the energy consumption.
Operational performance
The quality of our products increased (defects reduction, products that meet customer needs, rate of customer complaints and number of warranty claims);
We increased our flexibility (quick changes in product design, quick introduction of new products, quick changes in production volume and broad variety of products);
We reduced the costs (low production costs, offer price as low or lower than our competitors and low overhead costs);
Our delivery improved (quick delivery, on-time delivery and reliable delivery);
Our productivity increased and
We reduced the production lead time.
Source(s): Authors' own work
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Acknowledgements
Funding: The research was funded by the University of Pretoria doctoral bursary request number 2553.