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SCM-Thesis-12
Master Thesis
Taking an Environmental Perspective on Supply
Chain Management – A Study on the German
Automobile Industry
Master Thesis to obtain the Master of Science in Supply Chain Management
from the Rotterdam School of Management, Erasmus University
Date
July 2013
Author Michelle Engert
Student Number 329909
University Supervisor
Dr. Erwin van der Laan
Department of Decision and Information Sciences
University Co-Reader Dr. Fabian Sting
Department of Management of Technology and
Innovation
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Taking an Environmental Perspective
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The copyright of the Master thesis rests with the author. The author is responsible for its
contents. RSM is only responsible for the educational coaching and cannot be held liable for the
content.
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ACKNOWLEDGEMENTS
The accompanying thesis – Taking an Environmental Perspective on Supply Chain Management: A Study
on the German Automobile Industry – was written to obtain the Master of Science Degree in Supply
Chain Management from the Rotterdam School of Management, Erasmus University.
After nearly 6 months the time has come to say thank you. First and foremost, I wish to thank my thesis
coach Professor Dr. Erwin van der Laan from the Department of Decision and Information Sciences at the
Rotterdam School of Management for his guidance, supervision and help throughout this thesis project.
One could not wish for a more patient and friendly supervisor. Furthermore, I would also like to thank my
thesis co-reader Professor Dr. Fabian Sting from the Department of Management of Technology and
Innovation at the Rotterdam School of Management. Lastly, a special thank you goes out to the
participants who have willingly shared their valuable time and responded to my survey questionnaire.
Thank you.
Michelle Engert
July 2013
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EXECUTIVE SUMMARY
This research has taken an environmental perspective on Supply Chain Management and has,
furthermore, made an attempt to address the, in previous literature, scantly discussed relationship between
resource dependence and Green Supply Chain Management (GSCM) performance. Having drawn on
knowledge from the Resource Dependence Theory as well as the Institutional Theory the relationship
between green supply chain practices and organizational performance has been explored.
This study is based on the study performed by Lee et al. (2012) who have investigated the relationship
between GSCM practice implementation and firm performance on small- and medium-sized suppliers in
the electronics industry in Korea. In contrast, this study was conducted focusing on small- and medium-
sized suppliers in the automotive industry in Germany. As stated by Oliver (1991) the external pressures
referred to by the Resource Dependence and Institutional Theories originate from the organizations
stakeholders. For Korean firms these pressures are originating from buying firms in the EU and for
German firms, which are regarded as early adopters of ISO 14001 standards (Welch et al., 2002), these
pressures are assumed to be insignificant.
Even though there is still enormous potential for further investigations, especially in regards to
investigating whether a moderating effect exists between GSCM Practice Implementation and Business
Performance, the results of this study reveal a number of interesting insights into the topic of Green
Supply Chain Management and organizational performance.
(1) Firstly, the most anticipated finding of there being a significant, direct relationship between GSCM
Practice Implementation and Overall Business Performance was weakly supported. (2) Furthermore, this
study also made a distinction between Environmental and Economic Performance and found supporting
evidence for the existence of a significant, direct relationship between GSCM Practice Implementation
and Environmental and Economic Performance. (3) The study results also reveal that organizations
should not only focus on achieving Overall Business Performance outcomes but should also recognize the
potential that increasing Employee Job Satisfaction, Operational Efficiency and Relational Efficiency
bring with it when trying to improve an organizations Environmental and Economic Performance. (4)
Additionally, when conducting the study on German suppliers it was found that improvements in all three
mediators (Employee Job Satisfaction, Operational Efficiency and Relational Efficiency) yielded stronger
improvements in Overall Business Performance as compared to the results found by Lee et al. (2012). (5)
In terms of the Relational Efficiency it can be concluded that the implementation of GSCM practices
helps a supplying firm improve its Relational Efficiency with its buying firms. This ability of a supplying
firm to build trust and credibility in the relationship with the buying firm by means of collaboration and
information sharing will eventually have a positive effect on Business Performance. More specifically,
the increased transparency and openness in business processes has a strong impact on Overall Business
Performance and Environmental Performance and a weak but still significant impact on Economic
Performance. The existence of a relationship between Relational Efficiency and Environmental and
Economic Performance provides new insights for managers who wish to increase their performance gains
by means of increased collaboration and trust with their supply chain partners. This study revealed that
performance gains are not only to be expected in regards to asset utilization and competitive position but
also in terms of a decrease of waste discharge and a reduction in water usage as well as waste disposal.
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(6) Lastly, it was found that even though German enterprises are operating in a rather mature environment
in regards to green supply chain initiatives, in comparison to companies located in Korea, there is still
enormous potential for increasing operations‘/ supply chain managers‘ awareness of differing
Environmental Management Standards.
In summary, it can be said that this study provides enormous potential for future research especially in
regards to investigating whether a moderating effect exists between GSCM Practice Implementation and
Business Performance. To what degree does market pressure, when differentiating between companies
that experience more pressure and ones that experience less pressure, have an impact on the Overall,
Environmental and Economic Performance? However, even though conclusions on the existence or non-
existence of a moderating effect could not be drawn this study has made a contributing attempt in
determining differences between countries with differing GSCM Practice Implementation maturity and in
differentiating between Economic and Environmental Firm Performance outcomes.
A drawback of this study is that it remains questionable if the findings can be generalized in consideration
of the low response rate. Nevertheless, this thesis has managed to identify several possible improvements
that can be made to the methodological approach and which will undoubtedly enable future research on
the topic to yield more generalizable and accurate results. The main recommendation for future research
is to conduct the study on a larger sample and to continuously refine the survey instrument. As measuring
GSCM Practice Implementation is a rather new discipline the development of good measurement tools
provides enormous potential for further research.
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TABLE OF CONTENTS
ACKNOWLEDGEMENTS ........................................................................................................................................ 7
EXECUTIVE SUMMARY ......................................................................................................................................... 9
TABLE OF CONTENTS .......................................................................................................................................... 11
LIST OF TABLES AND FIGURES......................................................................................................................... 13
1. INTRODUCTION ............................................................................................................................................ 15
1.1 Problem Introduction ............................................................................................................................................. 15
1.2 Research Contribution – Filling the Gap ............................................................................................................... 16
1.3 Research Outline .................................................................................................................................................... 17
2. THEORETICAL BACKGROUND ................................................................................................................. 19
2.1 Theoretical Background – Resource Dependence Theory.............................................................................. 19
2.1.1 Resource Dependence Theory – Achieving Organizational Performance ..................................................... 19
2.1.2 Resource Dependence Theory and Supply Chain Management ..................................................................... 20
2.1.3 Resource Dependence Theory and Green Supply Chain Management .......................................................... 21
2.2 Small- and Medium-Sized Suppliers and Green Supply Chain Management ....................................................... 22
2.3 The Automotive Industry ....................................................................................................................................... 23
2.4 Institutional Theory ............................................................................................................................................... 24
2.4.1 Institutional Theory Explained ....................................................................................................................... 24
2.4.2 The Evolution of Green Awareness - An Institutional Theory Perspective ................................................... 24
3. HYPOTHESES DEVELOPMENT ................................................................................................................. 26
3.1 GSCM Implementation, Overall Business Performance, Environmental Performance, and Economic
Performance ................................................................................................................................................................. 26
3.2 Employee Job Satisfaction, GSCM Implementation, Operational Efficiency, and Overall Business Performance
..................................................................................................................................................................................... 27
3.3 Operational Efficiency, GSCM Implementation, Relational Efficiency, Overall Business Performance,
Environmental Performance, and Economic Performance .......................................................................................... 29
3.4 Relational Efficiency, GSCM Implementation, Overall Business Performance, Environmental Performance, and
Economic Performance ................................................................................................................................................ 30
3.5 Moderating Effect of Market Pressure ................................................................................................................... 32
3.6 Mediating Effect of Employee Job Satisfaction, Operational Efficiency and Relational Efficiency ..................... 33
3.7 The Conceptual Model .......................................................................................................................................... 34
4. RESEARCH METHODS AND DATA ........................................................................................................... 38
4.1 Developing the Questionnaire – Constructs and Items .......................................................................................... 38
4.2 Population and Data Sources ................................................................................................................................. 39
4.3 Data Collection Procedure and Response Rate ...................................................................................................... 40
4.3.1 Sample Selection ............................................................................................................................................ 40
4.3.2 Selection of Key Informants ........................................................................................................................... 41
4.3.3 Questionnaire Design and Distribution .......................................................................................................... 41
4.3.4 Invalid Respondents and Missing Data .......................................................................................................... 42
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4.3.5 Final Response Rate ....................................................................................................................................... 42
5. DATA ANALYSIS ............................................................................................................................................ 44
5.1 Characterization - Responding Firms .................................................................................................................... 44
5.2 Awareness and Adoption of Environmental Management Standards (EMSs) ...................................................... 45
5.3 Correlation Matrix ................................................................................................................................................. 46
5.4 Validity, Reliability and Goodness-of-Fit of the Research Model (Original Model) ............................................ 46
5.4.1 Step 1 – Assessing Validity of the Constructs ................................................................................................ 47
5.4.2 Step 2 - Assessing Reliability of the Constructs ............................................................................................. 52
5.4.3 Step 3 - Goodness-of-Fit of the Research Model ........................................................................................... 53
5.5 Validity, Reliability and Goodness-of-Fit of the Research Model (Modified Model) ........................................... 62
5.5.1 Step 1 – Assessing Validity of the Constructs ................................................................................................ 62
5.5.2 Step 2 - Assessing Reliability of the Constructs ............................................................................................. 65
5.5.3 Step 3 - Goodness-of-Fit of the Research Model ........................................................................................... 66
6. HYPOTHESES TESTING AND DISCUSSIONS OF QUANTITATIVE DATA ....................................... 76
6.1 Original Model ...................................................................................................................................................... 76
6.1.1 Direct Effects ................................................................................................................................................. 76
6.1.2 Mediation Analysis ........................................................................................................................................ 77
6.1.3 Moderation Analysis ...................................................................................................................................... 79
6.2 Modified Model ..................................................................................................................................................... 82
6.2.1 Direct Effects ................................................................................................................................................. 82
6.2.2 Mediation Analysis ........................................................................................................................................ 82
6.2.3 Moderation Analysis ...................................................................................................................................... 84
6.3 Robustness of the Original Model ......................................................................................................................... 87
7. SUMMARY AND IMPLICATIONS .............................................................................................................. 88
7.1 Main Findings and Managerial Implications ......................................................................................................... 88
7.2 Limitations and Future Research Directions .......................................................................................................... 90
7.3 Conclusions ........................................................................................................................................................... 91
LIST OF REFERENCES .......................................................................................................................................... 93
APPENDIX .............................................................................................................................................................. 111
Appendix 1 – List of Questionnaire Items and the respective Measurement Scales ................................................. 111
Appendix 2 – Survey Questionnaire .......................................................................................................................... 114
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LIST OF TABLES AND FIGURES
List of Tables
Table 1: Summary of constructs, their definitions and the most important literature identified .................................. 36
Table 2: Summary description of hypotheses to be investigated ................................................................................. 37
Table 3: Characteristics of responding firms ............................................................................................................... 45
Table 4: Awareness and adoption of Environmental Management Standards ............................................................. 46
Table 5: Correlations between theoretical constructs .................................................................................................. 46
Table 6: Validity and reliability table (original model) ............................................................................................... 50
Table 7: Factor correlation matrix with the square root of the AVE on the diagonal (original model) ....................... 50
Table 8: Summary of validity and reliability measurement results (original model) .................................................. 51
Table 9: Defining internal consistency using cronbach‘s alpha................................................................................... 52
Table 10: Summary of cronbach‘s alpha and item-to-total correlations measurement results (original model) ......... 53
Table 11: Statistics of first- and second-order models (original model) ...................................................................... 55
Table 12: Fit indices for the mediators, moderator and dependent concepts (original model) .................................... 60
Table 13: Validity and reliability table (modified model) ........................................................................................... 63
Table 14: Factor correlation matrix with the square root of the AVE on the diagonal (modified model) ................... 64
Table 15: Summary of validity and reliability measurement results (modified model) .............................................. 65
Table 16: Defining internal consistency using cronbach‘s alpha................................................................................. 65
Table 17: Summary of cronbach‘s alpha and item-to-total correlations measurement results (modified model)........ 66
Table 18: Statistics of first- and second-order models (modified model) .................................................................... 67
Table 19: Statistics of first- and second-order models after performing model fit (modified model) ......................... 68
Table 20: Summary of validity and reliability measurement results after performing model fit (modified model) .... 69
Table 21: Summary of cronbach‘s alpha and item-to-total correlations measurement results after performing model
fit (modified model) ............................................................................................................................................ 70
Table 22: Fit indices for the mediators, moderator and dependent concepts (modified model) .................................. 74
Table 23: Summary of hypotheses test results and comparison to results found by Lee et al. (2012)......................... 77
Table 24: Summary of mediation analysis results (original model) ............................................................................ 79
Table 25: Summary of moderation analysis results (original model) .......................................................................... 79
Table 26: Results of path analysis and hypotheses tests (original model) ................................................................... 80
Table 27: Summary of mediation analysis results (modified model) .......................................................................... 84
Table 28: Summary of moderation analysis results (modified model) ........................................................................ 84
Table 29: Results of path analysis and hypotheses tests (modified model) ................................................................. 85
List of Figures
Figure 1: Hypotheses development: GSCM Implementation, Overall Business Performance, Environmental
Performance, and Economic Performance .......................................................................................................... 26
Figure 2: Hypotheses development: Employee Job Satisfaction, GSCM Implementation, Operational Efficiency, and
Overall Business Performance ............................................................................................................................ 27
Figure 3: Hypotheses development: Operational Efficiency, GSCM Implementation, Relational Efficiency, Overall
Business Performance, Environmental Performance, and Economic Performance ............................................ 29
Figure 4: Hypotheses development: Relational Efficiency, GSCM Implementation, Overall Business Performance,
Environmental Performance, and Economic Performance ................................................................................. 30
Figure 5: Hypothesized structural model ..................................................................................................................... 35
Figure 6: Path diagram of the first-order measurement model (original model) ......................................................... 57
Figure 7: Path diagram of the second-order measurement model (original model) ..................................................... 58
Figure 8: Path diagrams of the measurement models (original model) ....................................................................... 61
Figure 9: Path diagram of the first-order measurement model (modified model) ....................................................... 71
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Figure 10: Path diagram of the second-order measurement model (modified model) ................................................. 72
Figure 11: Path diagrams of measurement models (modified model) ......................................................................... 75
Figure 12: Hypothesized structural model results (original model) ............................................................................. 81
Figure 13: Hypothesized structural model results (modified model) ........................................................................... 86
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Taking an Environmental Perspective on Supply Chain Management
– A Study on the German Automobile Industry
Note: This is a replication (Lee, S., Kim, S. and Choi, D. (2012), “Green supply chain management and organizational performance”, Industrial
Management and Data Systems, Vol. 112, No. 8, pp. 1148-1180).
1. INTRODUCTION
The first chapter of this thesis will provide an introduction to the general research topic and will elaborate
on how this study aims to contribute to the findings of other researchers on the subject. The chapter will
conclude with an outline of how the research report is structured.
1.1 Problem Introduction
Globalization pressures, increasing competitiveness and advances in information technology are the key
contributors to the shortening of product life cycles. The fast pace of globalization continues to promote
not only challenges and uncertainties but also opportunities. Companies that have the ability to respond
rabidly to the dynamic needs of new consumer segments and growing markets are more apt to stay
competitive and continue to remain industry leaders.
In the past two to three decades, environmental issues have received increasing attention, particularly in
the West, where the negative side-effects of industrial production are more than ever threatening
conditions for future generations. Ever more severe natural disasters, global warming, the reduction of the
stratospheric ozone layer as well as an increase in the pollution of the earth‘s oceans, rivers and air have
prompted the need for local, regional, national and international change.
Environmental legislations and agreements in combination with a continuous strive to remain competitive
have pressed organizations worldwide to recognize the importance of adopting environmentally friendly
practices. The importance placed on environmental practices by competitors, governments and the market
have fostered the adoption of corporate environmental management practices which has become a rather
mature discipline over the years. Numerous companies have understood the importance of reducing their
environmental impact and have incorporated environmental considerations into their day-to-day business
activities. However, as stated by Lee and Klassen (2008) as well as Lee (2009) it is of the utmost
importance for multinationals to engage their upstream suppliers in adopting environmentally friendly
practices which will contribute to the entire supply chain‘s competitive ability. Furthermore, engaging
upstream and downstream supply chain partners in green supply chain management initiatives has gained
importance when taking into account the fact that customers and other stakeholders are not always
inclined to make a distinction between a company and its supplying firms (Bacallan, 2000).
Legislations are being imposed on a global basis with the European Union being a forerunner. The
European Union and the USA have recognized the importance of proper environmental management
(Guimares and Sato, 1996). However, at present quite a few countries in Asia have made a noteworthy
step towards becoming ISO 14001 (requirements for Environmental Management Systems) accredited.
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Asian countries are following the lead primarily because of the rising environmental awareness associated
with increasing pressures and to remain competitive in global trading.
China as the forerunner followed by Japan, Italy and Korea currently outperforms both the USA and
European countries which are falling behind the remarkable pace set by developing nations in regards to
green initiatives. (Welch et al., 2002)
As can be derived from the in 2011 conducted ―ISO Survey of Management System Standard
Certification‖ a total of 267,457 ISO 14001 certificates were in issuance in 158 countries in the year 2011
(ISO, 2011). In terms of the regional share East Asia and the Pacific are, with 51.3% of the total number
in issuance, the forerunners closely followed by Europe with 39.9%. With a noteworthy distance to
Europe, North America is on third place with 2.8%. It should also be noted that East Asia and the Pacific
managed to overtake Europe for the first time in the year 2005.
Bansal and Roth (2000) in their qualitative study on the motivations for becoming more ecologically
responsive have found there to be three forces that induce companies to adopt environmentally sound
practices. These are regulatory, market and social pressures. Numerous researchers have recognized the
importance of regulatory pressures in pushing companies to be environmentally responsible (Newton and
Harte, 1997; Lawrence and Morell, 1995). Firms not only seek to avoid penalties or fines by complying
with legislations but also opt to remain competitive by actively engaging in environmental activities to
stay ahead of changes in regulations (Rondinelli and Vastag, 1996; Clark, 1999 cited in Vastag, 2004).
Market pressures originating from customers and suppliers as well as social pressures from the general
public and environmental activists also contribute to an increase in environmental awareness amongst
firms (Starik and Rands, 1995; Lawrence and Morell, 1995).
As stated by Welch et al. (2002) early adopters of ISO 14001 standards in Japan are likely to be larger,
greener and most of all less motivated by competitive, media or regulatory pressures. In comparison, later
adopters were found to have been more pressured by competitive, regulatory and media forces and were
likely to be smaller and less green.
Lee et al. (2012) expect that as pressures from external stakeholders such as governments and large
buying firms, which continuously extend the environmental requirements set for supplying firms, increase
the employees of the supplying firms are assumed to become increasingly dissatisfied and resistant to
change.
1.2 Research Contribution – Filling the Gap
From the amount of previous literature, addressing the relationship between resource dependence and
Green Supply Chain Management (GSCM) performance, it can be concluded that this topic is fertile for
investigation. Thus, the subsequent research, drawing on knowledge from the Resource Dependence
Theory as well as the Institutional Theory, will explore the relationship between green supply chain
practices and organizational performance. Scott (1992) (cited in Rowley, 1997) stated that both the
Resource Dependence Theory and the Institutional Theory emphasize the importance of managing
external demands and expectations as well as being responsive to these pressures in order to survive.
Furthermore, Oliver (1991) concluded that the external pressures referred to by the Resource Dependence
and Institutional Theories originate from the organizations stakeholders. The stakeholders to a business
are actors which have the control over scarce resources and who have the power to enforce institutional
values and guidelines. An organizations survival is dependent on its ability and the degree to which it is
able to satisfy its stakeholders (Brenner and Cochran, 1991).
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In this study, the independent concept (GSCM Implementation) and dependent concepts (Overall
Business Performance, Environmental Performance and Economic Performance) will be related by means
of three organizational variables, namely: Employee Job Satisfaction, Operational Efficiency and
Relational Efficiency which are assumed to have a mediating effect on the dependent concepts.
Furthermore, it will be investigated in how far Market Pressure moderates the relationship between
GSCM Implementation and Business Performance.
The study will be conducted from the supplier‘s point of view focusing on small- and medium-sized
suppliers in the automotive industry in Germany. German suppliers are considered to be operating in a
rather mature environment in regards to green supply chain initiatives in comparison to companies located
in Korea. As stated by Welch et al. (2002) early adopters of ISO 14001 standards might be more inclined
to adopt environmental practices and late adopters are assumed to require an increasing amount of
external pressure to adopt green initiatives. It is, thus, expected that German enterprises are less pressured
by regulatory, media or competitive forces and in turn staff members of these suppliers are assumed to be
more satisfied. This increased employee satisfaction, in turn, is assumed to more positively influence
business performance than is the case with companies operating in Korea, which are assumed to be more
pressured in becoming environmentally friendly. Furthermore, early adopters of ISO standards are
assumed to have the resources and motivation to pursue the adoption of environmental initiatives. This, in
turn, will be beneficial in the long-run as the early adoption of GSCM practices enables companies to
better position themselves for survival (Welch et al., 2002). However, it should be noted that followers
face less risk as they are able to learn from early adopters and, thus, are able to make more informed
choices as to which initiatives to adopt and which have not proven to be beneficial in the past. Lastly, it is
expected that the relationship between GSCM Implementation and Environmental Performance will be
stronger in European firms facing higher market pressures as opposed to firms facing lower
environmental pressures from buying firms. In contrast, however, economic performance is assumed to be
lower in European firms facing higher market pressures than in firms experiencing lower pressures.
In conclusion, a more significant indirect relationship between Green Supply Chain Practice
Implementation and Overall Business Performance is expected when conducting the study on German
Enterprises as opposed to Korean suppliers. This study is expected to provide new insights as to whether
business performance will increase or decrease as pressures from large customer firms begin to cease.
More explicitly, the following study will make a contribution to previous literature in making a
distinction between environmental and economic performance improvements and assesses the effects
market pressures have on early and late adopters in the industry. The study will differentiate between
German suppliers that are facing higher environmental pressures and companies that are facing lower
environmental pressures to determine the effects on business performance.
Additionally, the study will also provide new insights as to the relationship between relational efficiency
and environmental and economic performance.
1.3 Research Outline
This research report is structured as follows. Subsequent to this introductory chapter in which the problem
to be investigated and the research objectives were outlined the study proceeds with a detailed description
of the theoretical background. This description will provide the basis for Chapter 3 which elaborates on
the hypotheses development process and is rounded off with a depiction of the hypothesized conceptual
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model. Chapter 4 will provide a short description of how the questionnaire was developed and distributed.
Additionally, characteristics of the population to be studied will be identified subsequent to which the
chapter provides a description of how the final sample was obtained. In Chapter 5 a more detailed
description of the final sample characteristics will be provided and the gathered data will be analyzed by
means of various statistical methods. In Chapter 6 the hypotheses will be tested and the quantitative
outcomes will be discussed. The final chapter of this thesis, Chapter 7, will provide a summary of the
main findings, describe the study‘s limitations and will offer avenues for future research.
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2. THEORETICAL BACKGROUND
Chapter 2 will provide an outline of this study‘s theoretical background. First off, the literature review
will delve into the topic of the Resource Dependence Theory drawing a relationship to organizational
performance, supply chain management and green supply chain initiatives. Additionally, two further
important topics dealt with in this research paper are elaborated on, namely: small- and medium-sized
firms and the automotive industry. Subsequently, this chapter will also draw on literature about
Institutional Theory which will prove to be of use in building the conceptual model.
2.1 Theoretical Background – Resource Dependence Theory
The first section will delve into the topic of the Resource Dependence Theory drawing a link to
organizational performance, supply chain management and green supply chain initiatives.
2.1.1 Resource Dependence Theory – Achieving Organizational Performance
Resource Dependence Theory Explained
According to Pfeffer and Salancik (1978) (cited in Lee et al., 2012) Resource Dependence Theory (RDT)
proposes that dependence and collaboration are to be seen as key characteristics of member firms in a
supply chain which strive to increase their performance gains. Firms are said to be interdependent when
not one actor is in control of achieving a desired outcome but each member firm requires another actors‘
resources in order to sustain growth (Handfield, 1993). The aim should be to achieve higher performance
outcomes in the long-term as opposed to pursuing short-term benefits to the detriment of others. The
Resource Dependence Theory assumes that firms cannot be entirely self-sufficient with regards to
strategically vital resources. They are reliant on external resources and need to cautiously manage these
resources in order to remain competitive (Heide, 1994). Cook (1977), furthermore, states that these
developed dependencies facilitate the degree of influence partners have on one another‘s business
practices.
Uncertainty Explained
Taking this definition of Resource Dependence Theory one step further, Bordonaba-Juste and Cambra-
Fierro (2009) assert that to improve a firms performance, in the highly dynamic environment with
increasing globalization in which they are operating, it is of essence to adapt to the surroundings, while
those that are unsuccessful in doing so are condemned to fail. Considering the ongoing rise in
environmental complexity and dynamism firms are experiencing increasing uncertainty and managing
this uncertainty will be one of the main challenges facing companies all over the globe in the years to
come.
Literature on uncertainty presents a range of definitions of the concept; however, the most appropriate
characterization of uncertainty in the context of this study is the circumstance in which a company is
lacking sufficient knowledge and information in decision making (Duncan, 1972; Lawrence and Lorsch,
1967). Furthermore, uncertainty is characterized by the inability to know the out-come of a decision
beforehand and the inability to assign probabilities to how environmental factors will affect business
success (Duncan, 1972). The environment can be segmented into a total of four dimensions of uncertainty
(Jabnoun et al., 2003), namely:
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(1) Macro-environmental uncertainty: This dimension relates to a firms general environment
encompassing regulatory, political and economic conditions.
(2) Competitive uncertainty: This uncertainty type refers to a firm‘s inability to characterize their
competition in terms of their strategies, their competitive position and their prospective course of action.
(3) Market (and demand) uncertainty: The market is ever changing and this turbulence is making it ever
more difficult for firms to predict future demand and supply conditions.
(4) Technology uncertainty: This dimension relates to the change in the industry‘s technological know-
how and expertise.
The Resource Dependence Theory postulates that firms manage dependence and seek to reduce
uncertainty by means of creating formal linkages (Ulrich and Barney, 1984) such as negotiating and
arriving at agreements with collaborating firms (Koberg and Ungson, 1987; Cai and Yang, 2008). In
addition, it is also important to establish and maintain semiformal ties with other firms (Ulrich and
Barney, 1984) to facilitate the creation of a socially-bonded and trust-based relationship.
Linking Organizational Performance and Resource Dependence Theory
Drawing the link between Resource Dependence Theory and organizational performance it can be
concluded that with the increase in uncertainty and the ever faster changing environment a single firm is
hard pressed to acquire all resources it necessitates to develop and uphold its existing competitive
advantages whilst building new ones (Dyer and Singh, 1998). Thus, creating customer and supplier
linkages will contribute to reducing the uncertainty faced by firms in their operating environment (Carter
and Rogers, 2008). Additionally, integrating complementary resources can lead to the realization of
unique synergy which will in turn facilitate the creation of competitive advantages and thereby contribute
to increased firm performance (Harrison et al., 2001). Harrison et al. (2001) further state that
complementary resources are also advantageous in facilitating learning and expediting the development of
new capabilities. The resource bundle developed through interdependencies will provide the partnering
firms with capabilities that are superior to the ones they would have been able to build on their own.
These interdependencies enable firms to obtain sustainable competitive advantage and, in turn, enable the
improvement of the organizations performance (Sambharya and Banerji, 2006; Paulraj and Chen, 2007).
2.1.2 Resource Dependence Theory and Supply Chain Management
Having elaborated on the relationship between the Resource Dependence Theory and an organizations
performance the following paragraphs will now draw the link between the Resource Dependence Theory
and the entire supply chain.
Supply Chain Management
The focus of the term Supply Chain Management has shifted throughout the years. The traditional supply
chain was characterized by organizations which feared dependence and were more inclined to make use
of the business processes and facilities which were in their possession as opposed to collaborating with
the members of their supply chain (Thomas and Griffin, 1996). According to Ketchen and Hult (2007)
having others become dependent on an organization could be advantageous in being superior. Harland
(1996) in his study identified and addressed a range of differing definitions of Supply Chain
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Management. He stated that the term Supply Chain Management comprised of the functions of
purchasing, manufacturing and distributing the product.
Globalization and ever faster changing customer demands have increased the complexity of managing
supply chains. Thus, the definition of Supply Chain Management has shifted to account for rapidly
changing markets and an increasing globalization.
Hervani et al. (2005) define Supply Chain Management as the coordination and management of a network
of interconnected businesses and activities with the goal of providing a product or service to the end-
customer. A supply chain structure comprises of suppliers, distributors, manufacturers, wholesalers,
retailers and customers. Supply Chain Management is considered to be a critical business function
encompassing all activities which are related to the transformation and flow of goods from the sourcing of
raw materials and parts, the manufacturing and assembly of products, as well as the storage, distribution
and the delivery to the end-customer.
Linking Supply Chain Management and Resource Dependence Theory
Today, as never before, companies all over the globe are designing ever more efficient supply chains
which can withstand the complexities of globalization and the indefinite and unpredictable uncertainties it
brings with it. The terms outsourcing and offshoring have in recent years become increasingly important.
Companies source internationally to benefit from a reduction in production and service costs, increased
revenues and better reliability (Ferdows, 1997). MacCormack et al. (1994) have identified additional
benefits such as better access to overseas markets and close proximity to customers and suppliers which
facilitates organizational learning and improves reliability, respectively.
Having elaborated on the benefits of outsourcing and offshoring it is also important to bear in mind the
risks and challenges companies are encountering on a day to day basis in a world comprising of invisible
boundaries. MacCarthy and Atthirawong (2003) state that global supply chains in comparison to domestic
supply chains are harder to manage. This is mainly due to the geographical distance, an increase in lead-
times and the difference in language, culture and skills. Additionally, global supply chains are
characterized by risks and challenges which have an effect on every single member of the chain.
Economic and political instability, currency exchange rates and risks relating to changes in the regulatory
environment have made the supply chain more vulnerable to disruptions.
To counteract these strategic weaknesses that supply chains are facing the Resource Dependence Theory
stipulates that inter-organizational linkages and relationships will enable firms to achieve sustainable
growth. The theory emphasizes the need for buyer-supplier relationships which focus on cooperation and
organization in order to jointly benefit (Kanter, 1994).
2.1.3 Resource Dependence Theory and Green Supply Chain Management
Green Supply Chain Management
Increasing levels of pollution, the escalating deterioration of the environment and diminishing raw
material resources have contributed to an increase in environmental awareness. Institutional forces such
as regulatory requirements and consumer pressures are also drivers of change. Businesses have realized
the importance of integrating environmentally sound practices not only at an organizational level but
throughout the entire supply chain.
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Srivastava (2007) defines Green Supply Chain Management as the integration of environmental
awareness into supply chain related processes. By means of collecting and classifying previous literature
on the topic Srivastava (2007) was able to define the scope of Green Supply Chain Management as
ranging from green material choice and sourcing, to product design, manufacturing processes, product
delivery and end-of-life management. Drawing from past literature Zhu and Sarkis (2004) have developed
four factors for Green Supply Chain Management practices, namely:
(1) Internal environmental management: This factor describes the company‘s internal activities aimed at
becoming more environmentally-friendly. The dimension addresses the degree of commitment received
from top management as well as the company‘s obtainment of environmental compliance programs such
as ISO 14001 certification.
(2) External Green Supply Chain Management: This dimension encompasses the external relationships. It
deals with the purchasing of eco-friendly products and with the building of relationships with customers
and suppliers to become more environmentally sound.
(3) Investment recovery: Investment recovery deals with the sale of used materials and scrap as well as
the selling of excess inventory materials.
(4) Eco-design: This factor includes the design of products for recycling, reuse or recovery.
Linking Green Supply Chain Management and Resource Dependence Theory
Recovering materials and designing products in an economically friendly way has increased the need for
inter-organizational collaboration to an ever greater extent to realize potential gains and to, in turn,
achieve improved overall performance objectives (Zhu et al., 2010; Zhu and Sarkis, 2004; Zhu et al.,
2005; Shang et al., 2010).
In the context of Green Supply Chain Management, adopting Green Supply Chain Management related
practices, for example green purchasing and customer cooperation, does not only require the internal
adoption of environmental practices but the cooperation of the entire supply chain in becoming more
environmentally sound. González et al. (2008) have found that given the superiority of larger firms over
their smaller supply chain partners the large firms will opt for environmentally friendly practices to be
adopted by the smaller supplying firms. Thus, a diffusion of environmentally responsive practices
throughout the entire supply chain will take place. This diffusion can, however, only take place if firms
recognize the need of forming partnerships. As stated by the Resource Dependence Theory, partnerships
are indispensable if individual firms are lacking the required resources to achieve the desired outcomes.
2.2 Small- and Medium-Sized Suppliers and Green Supply Chain Management
Large, multinational enterprises are dominating the headlines with new international expansion strategies,
multi-billion Euro takeovers or bankruptcies. However, according to the European Commission (2012)
SMEs play the most important role in the economy. 99.8 per cent of all European businesses are small-
and medium-sized enterprises the majority of which, with 92.2 per cent, are characterized as micro-
businesses with less than 10 employees. Approximately 6.5 per cent of SMEs in the EU are small
enterprises which employ between 10 and 49 workers and the medium-sized enterprises account for 1.1
per cent (employing 50 to 249 people). Lastly, large businesses with a minimum of 250 employees make
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up merely 0.2 per cent of the total number of firms in the European Union. Thus, SMEs can be considered
as the back-bone of the European economy being mainly atone for advances in innovation and Resource
and Development as well as contributing to the prosperity and expansion of the economy. In the private
sector these businesses provide employment for two out of three workers and account for more than 50%
of the total value-added created by firms in the European Union. (European Commission, 2012)
Thus, it comes as no surprise that the involvement of small- and medium-sized suppliers is a critical first
task to take when endeavoring to achieve environmental change (Holt et al., 2001).
For companies to reap the greatest benefit from their environmental management practices it is of the
utmost importance to integrate both upstream and downstream members of the supply chain into their
environmental initiatives. Considering the suppliers‘ deciding role in improving the overall performance
of a supply chain (Sarkar and Mohapatra, 2006) it has become increasingly important for manufacturers
to collaborate with their upstream supply chain partners to enable the development of a competitive
advantage (Sheth and Sharma, 1997; Cannon and Homburg, 2001).
Lee (2008) has identified two drivers for firms and governments to include small- and medium-sized
enterprises in the environmental initiatives undertaken to make the entire supply chain more
environmentally friendly. The first reason for extending the environmental responsibility also to small-
and medium-sized suppliers is the risk of disruption. Suppliers that are not aware or are not concerned
with complying with the latest environmental standards can cause both excessive financial and
reputational damage to a buying firm. The second driver deals with the number of SMEs making up a
supply chain‘s base or a country‘s industrial base.
Micro, small- and medium-sized enterprises, however, often lack the resources, strategy, environmental
know-how and awareness to improve their processes to contribute to the entire supply chain becoming
more environmentally friendly (Pimenova and Vorst, 2003). These enterprises, thus, often have
difficulties implementing the requirements set by their larger buying firms and in consequence hinder
their customer firms from achieving their greening objectives (Lee and Klassen, 2008).
Concluding, it is important, as stated by the Resource Dependence Theory, to build strong relationships
amongst supply chain partners and to share the resources required to achieve the set goals. Partnerships
and the integration of complementary resources are a requisite to facilitate the development of new
capabilities and thereby contribute to the creation of competitive advantage.
2.3 The Automotive Industry
In the past three decades the automotive industry underwent several major developments. In the 1980s,
the industry experienced a turnaround in management practices with an increasing focus on quality
management and lean manufacturing (Oliver et al., 1996). The 1990s were characterized by a rapid
increase in globalization which brought about the expansion of the industry (Okada, 2004) as well as an
increase in customization, customer expectations and requirements.
The automotive supply chain, with its worldwide scope, provides a unique case for exploration in regards
to the implementation of GSCM practices and the resulting performance gains. The auto industry has a
pervasive global environmental impact and has been driven by competitive, regulatory and economic
reasons to adopt green supply chain initiatives. Furthermore, this industry is one of a small number of
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global industries in which customers have prescribed minimum environmental performance standards
with which suppliers have to comply. Companies have recognized the need for ensuring that their
upstream supply chain partners comply with environmental standards. It has been stated by Orsato and
Wells (2007) that, from an economic viewpoint, suppliers provide up to 80 per cent of the value,
consisting of the materials and parts, required to manufacture the end-product.
According to the European Automobile Manufacturers‘ Association (ACEA) (2012) Europe with a yearly
production quantity of more than 17 million vehicles (passenger cars, vans, buses and trucks), which is 24
per cent of the world total, is the worldwide forerunner in vehicle production. Germany is Europe‘s
largest car manufacturer closely followed by France which is the world‘s fifth largest. The top four
manufacturers worldwide are the United States, Japan, Germany and China (ACEA, 2013). The European
auto industry comprises of a few global lead manufacturers such as BMW, Daimler and Renault which
are supplied by a large number of small- and medium-sized enterprises. Goodyear, Bridgestone and
Magna are three of the largest auto industry suppliers in Europe. Suppliers in supporting sectors such as
electronics and electrical engineering, metal manufacturing and plastics and glass production are also
highly concentrated in the European area.
2.4 Institutional Theory
The fourth section of this chapter will delve into Institutional Theory and elaborate on the role of
institutional pressures in firms‘ willingness to adopt green supply chain practices.
2.4.1 Institutional Theory Explained
Institutional Theory tries to explain how external pressures such as market, regulatory and competitive
forces influence a company to implement a specific organizational practice or structure (Hirsch, 1975; Lai
et al., 2006). DiMaggio and Powell (1983) state that within Institutional Theory three isomorphic
processes exist, namely: coercive, normative, and mimetic. Coercive isomorphic drivers mainly originate
from parties who are in power such as governmental agencies. Governments are in the position to
coercively influence organizations by means of fines and trade barriers (Rivera, 2004). Normative
isomorphic pressures on the other hand mainly originate from consumers. Enterprises are driven to
conform so as to be perceived as operating legitimately. The third driver, namely mimetic isomorphism
takes place when organizations endeavor to become as successful as their industry competitors by
mimicking or imitating their actions (Aerts et al., 2006).
Drawing the link to GSCM practice implementation, Jennings and Zandbergen (1995) as well as
Lounsbury (1997) state that the Institutional Theory provides an important theoretical background to
assess in how far external pressures impact a company‘s adoption of green supply chain practices.
Kilbourne et al. (2002) have identified there to be a relationship between coercive forces and the
implementation of environmental change initiatives. Furthermore, normative pressures exerted from
consumers, foreign and domestic, have also driven companies to adopt environmentally-friendly practices
(Ball and Craig, 2010). Lastly, mimetic isomorphism was also found to play a contributing role in green
practice implementation.
2.4.2 The Evolution of Green Awareness - An Institutional Theory Perspective
The environmental revolution has changed the way companies do business. The 1960s and 1970s were
characterized by corporations denying the fact that their business activities were negatively impacting the
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environment. A series of ecological problems initiated organizations to rethink the way they do business.
Today, almost four decades later, going green is an imperative not many companies can afford to ignore.
The corporations of the twenty-first century have accepted their responsibility towards the environment
and they are in a better state than ever having the motivation, the resources and the know-how to act and
achieve sustainability.
According to Lee and Rhee (2007) Korea‘s concern for the environment emerged two decades ago when
the country experienced first-hand environmental impacts. Up until the 1990s Korea‘s number one
priority had been economic growth (Lin and Sheu, 2012). The Korean economy grew at a tremendously
fast rate for three decades until environmental events and accidents increased the country‘s awareness for
the environment. Furthermore, almost simultaneously, Korean companies experienced an increase in
external pressures especially from the European Union which has implemented laws and regulations to
reduce the environmental impact of a firm‘s entire supply chain.
In conclusion, the European Union can be seen as a forerunner when it comes to establishing and
implementing laws and regulations to pressure businesses in increasing their environmental awareness.
Thus, the EU is a rather mature continent as compared to Korea which has only just recently started to be
concerned about the country‘s environmental impact.
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3. HYPOTHESES DEVELOPMENT
Chapter 3 outlines the hypotheses development process and draws on additional literature from
Economics and Business Administration, Marketing and Supply Chain Management. The chapter
concludes with a conceptual model, a summarizing table of the concepts and their respective definitions
as well as a table summarizing the hypotheses.
3.1 GSCM Implementation, Overall Business Performance, Environmental Performance, and
Economic Performance
Independent Concept Dependent Concepts
Figure 1: Hypotheses development: GSCM Implementation, Overall Business Performance, Environmental Performance, and
Economic Performance
Chien and Shih (2007) have studied the effects of implementing green initiatives on firm performance at
manufacturing firms operating in the electrical and electronics industry in Taiwan. The authors were able
to conclude a positive relationship between implementing green supply chain practices and the
environmental and financial performance of firms. More specifically, the increase in the environmental
performance of a firm will inevitably yield an increase in market share and corporate profits. Rao (2002)
has found there to be a relationship between green supply chain management, competitiveness and
economic performance. Becoming more environmentally committed, for instance, by means of employing
waste and emission reduction initiatives in combination with cutting costs and enhancing product quality
and production efficiency to remain competitive, firms can achieve economic performance gains. Porter
and van der Linde (1995) also support the existence of a relationship between cost savings or product
value increases and the degree of company competitiveness.
However, as stated by Aragón-Correra and Sharma (2003) temporarily implementing a proactive
environmental approach does not guarantee the obtainment of a competitive advantage. A continuous
development is required in terms of innovations and constant learning to maintain and improve the
competitive position (Ulhøi and Madsen 2003).
The empirical research of Zhu and Sarkis (2004) provides evidence for there to be a noteworthy
relationship between GSCM implementation and the environmental and economic performance of a firm.
In a more recent study Zhu et al. (2007) were able to show that apart from there being a significant
relationship between GSCM implementation and a firm‘s environmental and economic performance there
is also an association to be made to the operational performance outcomes of a company. Operational
performance encompasses the quality of products, the capacity and inventory levels.
It is also important to mention that for firms to effectively benefit from GSCM practice adoption Chen
(2008) as well as Yang et al. (2009) have identified the need for successfully integrating and managing
internal (for instance top management commitment) as well as external (e.g. collaborating with suppliers
and customers) green supply chain practices. Moreover, Geffen and Rothenberg (2000) (cited in Zhu et
GSCM
Implementation
Overall Business Performance
Environmental Performance
Economic Performance
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al., 2005), Vachon (2007) and Seuring and Mueller (2008) were able to conclude that the performance
gains reaped from implementing GSCM practices are both financial and non-financial in nature.
Furthermore, it should be noted that the adoption of green supply chain practices is linked to the firm‘s
image of being socially responsible (Montiel, 2008; Cruz and Pedrozo, 2009). As a matter of fact,
McGuire et al. (1988) studied the relationship between perceptions of a firms‘ social responsibility and
the corresponding financial performance. The authors found there to be a positive association between
corporate social responsibility and a firm‘s business performance evaluated in terms of accounting and
stock-market-based measures.
Therefore, the following hypotheses are being proposed:
H1a: The implementation of GSCM practices is positively related to the overall business performance at
the firm level.
H1b: The implementation of GSCM practices is positively related to the environmental performance at
the firm level.
H1c: The implementation of GSCM practices is positively related to the economic performance at the
firm level.
3.2 Employee Job Satisfaction, GSCM Implementation, Operational Efficiency, and Overall
Business Performance
Independent Concept Mediators Dependent Concept
Figure 2: Hypotheses development: Employee Job Satisfaction, GSCM Implementation, Operational Efficiency, and Overall
Business Performance
Valentine and Fleischman (2008) in their exploratory study on ethics programs, the perceived corporate
social responsibility and the corresponding employee job satisfaction have found there to be a positive
relationship between ethics programs and employee work attitudes mediated by corporate social
responsibility. The authors suggest management to place an increasing focus on the organizations ethics
codes, culture and corporate social responsibility to increase the positive beliefs about the company.
GSCM
Implementation
Overall Business Performance
Employee Job
Satisfaction
Operational
Efficiency
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Somers (2001) found there to be a positive relationship between ethics code awareness and accountants‘
organizational commitment. Valentine and Barnett (2003) also concluded that sales managers‘
organizational commitment was higher in firms that had an ethics code as opposed to firms that did not.
The presence and the employee‘s awareness of the existence of an ethics code was found to be positively
related to job satisfaction.
Mansoor et al. (2011), in their study examining the impact of job stress on employees‘ work satisfaction,
concluded there to be a negative relationship between job stress and the employees‘ resulting satisfaction.
These results are in line with the conclusions drawn by Keller (1975). Mansoor et al. (2011) categorize
job stress into stress resulting from the workload, from role conflict and job stress resulting from the
physical environment. The physical environment encompasses not only the noise, temperature, lighting
and the air circulation but also the exposure of employees to dangerous and toxic substances. According
to Davey et al. (2001) job stress is experienced mainly due to organizational aspects such as a lack of
support and commitment from top managers, long working hours or conflicts at the work place.
Job satisfaction is characterized as the extent to which employees derive pleasure from their jobs
comprising of both cognitive and affective factors (Hulin and Judge, 2003, p. 259 cited in Scott and
Judge, 2006). Edwards et al. (2008) take this definition of job satisfaction one step further and found there
to be a positive relationship between job satisfaction and task performance. Researchers in the last few
decades have found numerous explanations for a relationship to exist between employee work satisfaction
and job performance (Schleicher et al., 2004; Locke, 1976). Social Cognitive Theories state there to be a
link between employee attitude toward the job and the resulting behavior on the job which will be
reflected in job performance (Kraus, 1995). Furthermore, Expectancy-Based Theories draw a link
between the expected outcomes of a particular performance and the attitudes one has toward the job
(Naylor et al., 1980 cited in Edwards et al., 2008).
Homburg and Stock (2004), in their dyadic analysis on the link between salespeople‘s job satisfaction and
the satisfaction of the company‘s customers, were able to conclude that an increase in employee
satisfaction is positively related to customer satisfaction. A link between employee satisfaction and
financial performance which is mediated through the constructs of customer loyalty, customer satisfaction
and employee loyalty is suggested by the service profit chain model (Heskett et al., 1997).
Furthermore, Patterson et al. (2004) found supporting evidence for the existence of a relationship between
company climate and company productivity mediated by average job satisfaction level. The concept of
company climate was measured by assessing the perceptions employees had of the organizations‘ guiding
principles and practices. The authors stated there to be a link between company climate and company
performance which is mediated by employee job satisfaction.
Therefore, the following hypotheses are being proposed:
H2a: The implementation of GSCM practices is positively related to employee job satisfaction.
H2b: Employee job satisfaction is positively related to overall business performance at the firm level.
H2c: Employee job satisfaction is positively related to the operational efficiency of the firm that
implemented GSCM practices.
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3.3 Operational Efficiency, GSCM Implementation, Relational Efficiency, Overall Business
Performance, Environmental Performance, and Economic Performance
Independent Concept Mediators Dependent Concepts
Figure 3: Hypotheses development: Operational Efficiency, GSCM Implementation, Relational Efficiency, Overall Business
Performance, Environmental Performance, and Economic Performance
Operational outcomes, as stated by Zacharia et al. (2009), receive a great deal of attention from supply
chain members. The parties aim to reduce costs, improve product quality and customer service as well as
attempt to reduce the required cycle time (Koufteros at al., 2002).
Lin and Sheu (2012) surveyed U.S. and Taiwanese manufacturing plants operating in the electric and
electronics industry to examine the impact of Institutional Theory on GSCM practice adoption and how
the implementation of green initiatives in turn influences the supply chain‘s performance. The findings
prove the existence of a positive relationship between implementing green supply chain practices and the
manufacturer‘s operational efficiency.
Yang et al. (2010), furthermore, have identified there to be a positive relationship between the degree of
supplier partnership collaboration and the development of proactive environmental management
programs. The study further posits that this increase in adopting green supply chain practices positively
influences the competitive advantage by means of product quality enhancements, cost savings and
increased innovativeness. Evidence for the existence of a correlation between GSCM practice adoption
and a reduction in costs and cycle time was also provided by the firm interview responses obtained by
Lippman (2001).
Szwilski (2000) stated that an environmental management system, which is characterized to be an
information and environmental policy management mechanism, will enable the industry to facilitate the
improvement of an individual organization‘s operational performance.
In regards to the link between operational efficiency and environmental performance it can be said that
only a limited number of studies have explored this relationship. Slack et al. (2009) (cited in Ramanathan
and Akanni, 2010) posit that lean principles such as waste reductions, continuous improvements and
stakeholder involvements positively influence a company‘s environmental performance. Porter and van
der Linde (1995) underline this statement made by Slack et al. (2009) and conclude that an increase in a
firm‘s operational efficiency will inevitably lead to a reduction in waste and scrap. Toffel and Lee (2009)
state there to be a relationship between environmental performance indicators and the process efficiency
GSCM
Implementation Overall Business Performance
Environmental Performance
Economic Performance
Operational
Efficiency
Relational
Efficiency
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programs (programs such as lean manufacturing and six-sigma quality improvements). In conclusion, it
can be said that organizations characterized by higher operational efficiency are, as opposed to
organizations with lower operational efficiency, probably able to reduce waste more efficiently.
Cohen et al. (1995) concluded that firms which are able to more efficiently manufacture their products
pollute less. Efficiencies in manufacturing are said to result in improved resource efficiencies and are also
associated with a reduction in operating and environmental compliance costs (Berman et al., 1999). Thus,
it can be posited that firms managing to achieve environmental performance improvements also tend to be
able to achieve improved financial performance.
In regards to the effect of operational efficiency on relational efficiency, Goffin et al. (2006) in their
empirical study were able to conclude that an improvement in the operational performance of firms
supports the building of trust. Firms that accomplish their performance goals are more inclined to trust
their collaboration partner. This can be underlined by the fact that firms managing to increase their
performance gains as a result of close collaboration with another entity are under the impression that the
partnering firm made a considerable, valuable contribution to the successful outcome. This in turn
increases the reliability and credibility of the partnering firm.
Therefore, the following hypotheses are being proposed:
H3a: The implementation of GSCM practices is positively related to the operational efficiency of the firm.
H3b: Operational efficiency is positively related to overall business performance at the firm level.
H3c: Operational efficiency is positively related to environmental performance at the firm level.
H3d: Operational efficiency is positively related to economic performance at the firm level.
H3e: The improved supplier’s operational efficiency has a positive impact on the relational efficiency
between the supplier and the large customer firm.
3.4 Relational Efficiency, GSCM Implementation, Overall Business Performance, Environmental
Performance, and Economic Performance
Independent Concept Mediator Dependent Concepts
Figure 4: Hypotheses development: Relational Efficiency, GSCM Implementation, Overall Business Performance,
Environmental Performance, and Economic Performance
GSCM
Implementation
Overall Business Performance
Environmental Performance
Economic Performance
Relational
Efficiency
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Global supply chains as compared to their domestic counterparts are increasingly challenged by
differences in economies (e.g. tax and exchange rates, inflation and transfer prices) (Nelson and
Toledano, 1979), infrastructures, political factors, local cultures and competitive environments (Schmidt
and Wilhelm, 2000). The available modes of transport, the number of intermediaries and the quality of
documentation (Mentzer and Samli, 1981) as well as differences in politics such as the law, governmental
regulations and sanctions are contributing to increasing the risks, in terms of uncertainty and variability,
faced in managing these boundary spanning supply chains.
Drawing the link to Resource Dependence Theory, Ulrich and Barney (1984) stated that firms attempt to
reduce the environmental uncertainty encountered in managing global supply chains by creating formal
and informal linkages. These long-lasting inter-firm relationships facilitate the creation of a socially-
bonded and trust-based relationship which in turn increases the respective performance gains of both
supplying and buying firms (Dyer and Nobeoka, 2000).
Trust has been acknowledged to play a very significant role in any supply chain relationship (Doney and
Cannon, 1997; Monczka et al., 1998). A relationship of trust is characterized by having confidence in a
partner and being able to rely on the fact that the party will not behave opportunistically (Jap, 2001).
Thus, it can be concluded that an increase in the extent of trust between the parties increases the degree of
commitment (Gundlach et al., 1995).
The Transaction-Cost Framework first described by Williamson (1975) is also important to consider. The
original explanatory framework focuses on the amount of cost and effort that is required for two entities
to complete a transaction. Buyers and suppliers aim to minimize the costs associated with completing the
activity (Lai et al., 2005). David and Han (2004) and Grover and Malhotra (2003) have utilized the
framework to assess in how far the increase of transaction costs and the decrease of uncertainty benefit
the performance gains achieved by the transacting entities.
Kim et al. (2011) in their empirical study on 125 companies in South Korea have found there to be a
positive relationship between GSCM orientation and firm performance. The relationship has been found
to be mediated by the supply chain partners‘ trust and the degree of information sharing. The authors
concluded that trust among corroborating partners facilitates the amount of information sharing in terms
of general product and risk information which in turn yields an improvement in firm performance.
Zacharia et al. (2009) have found there to be a positive relationship between the degree of inter-firm
collaboration and business performance which is mediated by operational and relational outcomes.
Operational outcomes, which are mainly focused on in supply chain collaboration, are the reduction of
cost, improving quality and the value delivered to the customer as well as reducing the cycle time
(Koufteros et al., 2002). Relational outcomes are relationship specific and characterized by effectiveness,
trust and credibility between suppliers and buying firms.
Drawing the connection to GSCM implementation, it is suggested that making a joint effort to implement
GSCM practices between manufacturers and suppliers will yield an improvement in the resulting
performance gains for both parties (Liao, 2010).
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Therefore, the following hypotheses are being proposed:
H4a: The implementation of GSCM practices has a positive influence on the relational efficiency between
the supplier and the large customer firm.
H4b: Relational efficiency between the supplier and the large customer firm is positively related to the
supplier’s overall business performance.
H4c: Relational efficiency between the supplier and the large customer firm is positively related to the
supplier’s environmental performance.
H4d: Relational efficiency between the supplier and the large customer firm is positively related to the
supplier’s economic performance.
3.5 Moderating Effect of Market Pressure
As stated previously, there are three major external pressures which influence a company to implement
green supply chain practices. These pressures are, namely: market, regulatory and competitive forces
(Hirsch, 1975; Lai et al., 2006). DiMaggio and Powell (1983) state that within Institutional Theory three
isomorphic processes exist, namely: coercive, normative, and mimetic. The current study focuses on
normative isomorphic drivers which mainly originate from consumers. Enterprises are driven to conform
so as to be perceived as operating legitimately. More specifically, the study will focus on how market
pressures, in this study characterized as exports and sales to foreign customers, moderate the relationship
between Green Supply Chain Practice Implementation and Business Performance (Overall Business
Performance, Environmental Performance and Economic Performance) (Zhu and Sarkis, 2007).
Supporting evidence for non-market and market pressures to moderate the relationship between
environmental practices and organizational performance was given by Hoffman and Ventresca (1999).
Manufacturers are forced to improve their environmental performance by means of market pressures
originating from customers and suppliers as well as non-market pressures arising from the general public,
regulators and environmental activists who also contribute to an increase in environmental awareness
amongst firms (Starik and Rands, 1995; Lawrence and Morell, 1995; Zhu and Sarkis, 2007).
As was stated by Welch et al. (2002) early adopters of ISO 14001 standards are likely to be larger,
greener and most of all less motivated by competitive, media or regulatory pressures. Later adopters were
found to have been more pressured by competitive, regulatory and media forces and were likely to be
smaller and less green. German suppliers are considered to be operating in a rather mature environment in
regards to green supply chain initiatives in comparison to companies located in Korea.
It is, thus, expected that German enterprises are less pressured by regulatory, media or competitive forces
and this, in turn, is assumed to more positively influence the relationship between GSCM practice
implementation and economic performance than is the case with companies operating in Korea, which are
assumed to be more pressured in becoming environmentally friendly. Companies that are more pressured
are assumed to experience increased environmental performance but at the same time are said to
experience a decrease in the economic performance (Zhu and Sarkis, 2007).
However, it should be noted that according to Kagan et al. (2003) market pressures are a necessity for
organizations to experience performance improvements. In the absence of market pressures companies
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would be reluctant to incorporate innovative environmental practices which would be beneficial in
improving the economic situation.
Therefore, the following hypotheses are being proposed:
H5a: The positive relationship between GSCM practice implementation and overall business
performance is weaker in German suppliers facing higher environmental pressure from buying firms
(market pressures) than in German suppliers facing lower environmental pressure from buying firms.
H5b: The positive relationship between GSCM practice implementation and environmental performance
is stronger in German suppliers facing higher environmental pressure from buying firms (market
pressures) than in German suppliers facing lower environmental pressure from buying firms.
H5c: The positive relationship between GSCM practice implementation and economic performance is
weaker in German suppliers facing higher environmental pressure from buying firms (market pressures)
than in German suppliers facing lower environmental pressure from buying firms.
3.6 Mediating Effect of Employee Job Satisfaction, Operational Efficiency and Relational Efficiency
As was stated previously, Homburg and Stock (2004), in their dyadic analysis on the link between
salespeople‘s job satisfaction and the satisfaction of the company‘s customers, were able to conclude that
an increase in employee satisfaction is positively related to customer satisfaction. A link between
employee satisfaction and financial performance which is mediated through the constructs of customer
loyalty, customer satisfaction and employee loyalty is suggested by the service profit chain model
(Heskett et al., 1997).
Furthermore, Patterson et al. (2004) found supporting evidence for the existence of a relationship between
company climate and company productivity mediated by average job satisfaction level. The concept of
company climate was measured by assessing the perceptions employees had of the organizations guiding
principles and practices.
In regards to the mediating effect of operational efficiency Lin and Sheu‘s (2012) findings, as was
previously stated, proved there to be a positive relationship between GSCM practice implementation and
operational efficiency. Yang et al. (2010), furthermore, were able to conclude that operational efficiency
mediates the relationship between GSCM practice adoption and company performance.
Kim et al. (2011) in their empirical study have found there to be a positive relationship between adopting
environmentally friendly practices and firm performance. The relationship is mediated by the supply
chain partners‘ trust and the degree of information sharing. The authors concluded that trust among
corroborating partners facilitates the amount of information sharing in terms of general product and risk
information which in turn yields an improvement in firm performance.
Furthermore, Zacharia et al. (2009) were able to conclude that operational and relational outcomes
mediate the positive relationship between the degree of inter-firm collaboration and business
performance.
Master Thesis 2013 Supply Chain Management-Taking an Environmental Perspective Michelle Engert 329909
34
Therefore, the following hypotheses are being proposed:
H6a: Employee job satisfaction and operational efficiency in the supplier firm, and relational efficiency
between the supplier and the large buyer firm mediate the relationship between GSCM practice
implementation and the supplier’s overall business performance.
H6b: Operational efficiency in the supplier firm and relational efficiency between the supplier and the
large buyer firm mediate the relationship between GSCM practice implementation and the supplier’s
environmental performance.
H6c: Operational efficiency in the supplier firm and relational efficiency between the supplier and the
large buyer firm mediate the relationship between GSCM practice implementation and the supplier’s
economic performance.
3.7 The Conceptual Model
This section, more specifically this chapter, concludes with the conceptual model depicted on the next
page (Figure 5). Furthermore, Table 1 and Table 2 provide a summary of the constructs and hypotheses,
respectively.
The Conceptual Model
Independent Concept Mediators and Moderator Dependent Concepts
GSCM
Implementation
Overall Business Performance
Environmental Performance
Economic Performance
Employee Job
Satisfaction
Operational
Efficiency
Relational
Efficiency
Market
Pressure
H2a
+
H4a
+
H3a
+
H3e
+
H2c
+
H2b
+
H4b, H4c, H4d
+
H5a, H5b, H5c
+
H1a, H1b, H1c
+
H3b, H3c, H3d
+
Figure 5: Hypothesized structural model
Master Thesis 2013 Supply Chain Management-Taking an Environmental Perspective Michelle Engert 329909
Construct Definitions
The following table provides a summary of the constructs, their respective definition (as made use of in
this study) and the most important literature identified in the theoretical background.
Construct Definition Literature Base
Ind
epen
den
t
Co
nce
pt
GSCM Practice
Implementation
Adopting green supply chain practices such as internal
environmental management (IEM), green purchasing
(GP), cooperation with customers (CC), and eco-design
(ECO) will enable the company to achieve environmental
sustainability.
Zhu et al. (2008)
Dep
end
ent
Co
nce
pts
Overall Business
Performance
The non-financial and financial performance of a
company resulting from the implementation of GSCM
practices as well as an improvement in the operational
and relational efficiency and the employee job
satisfaction.
Zhu et al. (2008), Zacharia
et al. (2009), Zhou et al.
(2008)
Environmental Performance
The environmental performance in terms of a reduction in
air emissions, waste water or solid waste resulting from
the implementation of GSCM practices as well as an
improvement in the operational and relational efficiency.
Zhu et al. (2007), Zhu et al.
(2008)
Economic Performance
- Positive
Positive economic performance is achieved when benefits
are gained through implementing green supply chain
practices. Benefits are here described as a decrease in fee
for waste discharge, for waste treatment or for example a
decrease in the cost for energy consumption.
Rao and Holt (2005), Zhu
and Sarkis (2007), Zhu et
al. (2007), Zhu et al. (2008)
Med
iato
rs
Employee Job Satisfaction The extent to which employees like their jobs related to
working climate and the relationship with supervisors
which is expected to result in improved performance
outcomes.
Zhou et al. (2008),
Homburg and Stock (2004),
Patterson et al. (2004)
Operational Efficiency The supplying firm‘s ability to have greater success in
achieving cost and cycle time reductions, improve service
or value delivery to the customer and the ability to
improve product quality.
Koufteros et al. (2002),
Rusinko (2007), Zhu et al.
(2008), Zacharia et al.
(2009)
Relational Efficiency The supplying firm‘s ability to build trust and credibility
in the relationship with buying firms by means of
collaboration and information sharing which increases the
transparency and openness in business processes.
Zacharia et al. (2009), Kim
et al. (2011), Pfeffer and
Salancik (1978) (cited in
Lee et al., 2012)
Mo
der
ato
r
Market Pressure Organizations experience both formal an informal
pressures from downstream customers and consumers.
More specifically, this paper defines market pressure in
terms of two items, namely: exports and sales to foreign
customers.
Zhu and Sarkis (2007),
DiMaggio and Powell
(1983)
Table 2: Summary of constructs, their definitions and the most important literature identified
Master Thesis 2013 Supply Chain Management-Taking an Environmental Perspective Michelle Engert 329909
37
Hypotheses Summary
Table 2 provides a summary description of the hypotheses to be investigated in this study.
Hypotheses Summary
H1 H1a:
The implementation of GSCM practices is positively related to the overall business performance at the firm
level.
H1b:
The implementation of GSCM practices is positively related to the environmental performance at the firm level.
H1c:
The implementation of GSCM practices is positively related to the economic performance at the firm level.
H2 H2a: The implementation of GSCM practices is positively related to employee job satisfaction.
H2b:
Employee job satisfaction is positively related to overall business performance at the firm level.
H2c:
Employee job satisfaction is positively related to the operational efficiency of the firm that implemented GSCM
practices.
H3 H3a:
The implementation of GSCM practices is positively related to the operational efficiency of the firm.
H3b:
Operational efficiency is positively related to overall business performance at the firm level.
H3c:
Operational efficiency is positively related to environmental performance at the firm level.
H3d: Operational efficiency is positively related to economic performance at the firm level.
H3e:
The improved supplier‘s operational efficiency has a positive impact on the relational efficiency between the
supplier and the large customer firm.
H4 H4a:
The implementation of GSCM practices has a positive influence on the relational efficiency between the supplier
and the large customer firm.
H4b:
Relational efficiency between the supplier and the large customer firm is positively related to the supplier‘s
overall business performance.
H4c:
Relational efficiency between the supplier and the large customer firm is positively related to the supplier‘s
environmental performance.
H4d:
Relational efficiency between the supplier and the large customer firm is positively related to the supplier‘s
economic performance.
H5 H5a: The positive relationship between GSCM practice implementation and overall business performance is weaker in
German suppliers facing higher environmental pressure from buying firms (market pressures) than in German
suppliers facing lower environmental pressure from buying firms.
H5b: The positive relationship between GSCM practice implementation and environmental performance is stronger in
German suppliers facing higher environmental pressure from buying firms (market pressures) than in German
suppliers facing lower environmental pressure from buying firms.
H5c: The positive relationship between GSCM practice implementation and economic performance is weaker in
German suppliers facing higher environmental pressure from buying firms (market pressures) than in German
suppliers facing lower environmental pressure from buying firms.
H6 H6a: Employee job satisfaction and operational efficiency in the supplier firm, and relational efficiency between the
supplier and the large buyer firm mediate the relationship between GSCM practice implementation and the
supplier‘s overall business performance.
H6b: Operational efficiency in the supplier firm and relational efficiency between the supplier and the large buyer firm
mediate the relationship between GSCM practice implementation and the supplier‘s environmental performance.
H6c: Operational efficiency in the supplier firm and relational efficiency between the supplier and the large buyer firm
mediate the relationship between GSCM practice implementation and the supplier‘s economic performance.
Table 3: Summary description of hypotheses to be investigated
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4. RESEARCH METHODS AND DATA
Hereunder, a brief overview of this study‘s research methods is provided. The chapter starts off with a
short description of how the questionnaire was developed after which the population to be studied and the
data sources are elaborated on. The final section will provide a detailed explanation on how the sample
was selected.
4.1 Developing the Questionnaire – Constructs and Items
In reference to the study performed by Lee et al. (2012) this study will also make use of a survey
questionnaire to obtain the required data. However, as stated by Dul and Hak (2008), the preferred
research strategy to test causal relationships is to conduct experiments. Lee et al. (2012), however, made
use of a single-method, namely a survey, which is according to Dul and Hak (2008) the second-best
preferred strategy to test a probabilistic relation. It should be mentioned that, in the actual practice of
business research and in this specific situation, conducting an experiment would not have been reasonable
as manipulating the independent concept (GSCM Practice Implementation) would have proven to be
somewhat difficult. Thus, it can be concluded that the research strategy chosen by Lee et al. (2012) is
indeed the best alternative to conducting an experiment and hence this research will also administer a
survey questionnaire to obtain the required data. A drawback of this approach is the fact that making use
of a single research method at the same moment in time will most likely lead to information bias as well
as common method variance (Dul and Hak, 2008).
In accordance with Lee et al. (2012), the independent concept will be measured by means of four
dimensions, namely: Internal Environmental Management (IEM), Green Purchasing (GP), Cooperation
with Customers (CC), and Eco-Design (ECO). Lee et al. (2012) have adopted these four GSCM practices
from the five factors identified by Zhu and Sarkis (2006) who additionally made use of the construct
Investment Recovery (IR).
The study will look at GSCM Practice Implementation from three different perspectives:
(1)Internal Perspective – internal environmental management: This dimension describes how the
company is internally improving processes and practices to become more environmentally friendly. This
includes the support received for green initiatives from top management as well as establishing
environmental compliance programs and obtaining ISO 14001 certification.
(2)External Perspective – external relationships: Encompasses the cooperation with customers and
suppliers as well as the purchasing of eco-friendly products.
(3)Interacting with the entire supply chain – product design: This dimension includes the design of
products for recycling, reuse or recovery.
The measurement items for the four dimensions of GSCM Practice Implementation were adopted from
Lee et al. (2012) who in turn adopted the measurement items from Zhu and Sarkis (2006). Lee et al.
(2012) made modifications to the measurement items Internal Environmental Management and Green
Purchasing. Furthermore, for the constructs Cooperation with Customers and Eco-Design the authors
Master Thesis 2013 Supply Chain Management-Taking an Environmental Perspective Michelle Engert 329909
39
chose to make use of additional items mentioned by Zhou et al. (2008), Chen (2005), Hsu and Hu (2008),
Matos and Hall (2007), and Rusinko (2007).
The four dimensions, namely: Internal Environmental Management (IEM), Green Purchasing (GP),
Cooperation with Customers (CC), and Eco-Design (ECO) will be measured by 5, 4, 4, and 5 items,
respectively, on a 5-point scale (1: not considering it, 2: planning to consider it, 3: considering it
currently, 4: initiating implementation, and 5: currently implementing).
The three mediators (Employee Job Satisfaction, Operational Efficiency and Relational Efficiency) will
be measured by 5 items, 6 items and 6 items, respectively, on a 5-point scale (1: strongly disagree, 2:
disagree, 3: neutral, 4: agree, and 5: strongly agree). (Lee et al., 2012; Zhu and Sarkis, 2007)
The dependent concept Overall Business Performance will be measured by 4 items on a 5-point scale (1:
strongly disagree, 2: disagree, 3: neutral, 4: agree, and 5: strongly agree) (Lee et al., 2012; Zhu and
Sarkis, 2007). The remaining two dependent concepts, namely: Environmental Performance and
Economic Performance will be measured by 6 and 9 items, respectively, on a 5-point scale (1: not at all,
2: a little bit, 3: to some degree, 4: relatively significant, and 5: significant).
Lastly, the measurement items for the moderator, Market Pressure, were adopted from Zhu and Sarkis
(2007). The moderator will be measured by means of 2 items on a 5-point scale (1: not at all important, 2:
not important, 3: not thinking about it, 4: important, and 5: extremely important).
Please refer to Appendix 1 for item descriptions and please refer to Appendix 2 for the complete
questionnaire.
4.2 Population and Data Sources
The population to be studied consists of operations/supply chain managers of small- and medium-sized
auto mobile enterprises in Germany.
The population of interest has the following three characteristics:
- small- and medium-sized suppliers;
- only in the automotive industry; and
- only German firms.
Operations/ supply chain managers were chosen as the population to be studied as they, according to
Walton et al. (1998), are in the position and have the influence to enable the company to obtain a
competitive advantage by means of adopting green practices. The operations and supply chain managers
are responsible for supplier selection, evaluation and activities such as purchasing which ideally positions
them to impact the environmental friendliness of the company. Furthermore, Stock (1998) (cited in
Srivastava, 2007) stated that 95 per cent of total costs in recycling are attributable to logistics activities.
Thus, it can be noted that Supply Chain Management plays a deciding role in becoming more
environmentally friendly and operations- and supply chain-managers have the power to change company
processes and activities. Gupta (1995) in his study takes an operations point of view and discusses the
impact that environmental management has on the production and operations of a company. The author
was able to conclude that operations managers are required to play a proactive role in the development
Master Thesis 2013 Supply Chain Management-Taking an Environmental Perspective Michelle Engert 329909
40
and implementation of green practice management systems. Handfield et al. (2005), in their paper
addressing the issue of environmental supply chain strategy development, state that the increase in the
adoption of environmental practices has raised awareness about the importance of adopting the right
supply chain strategy in order to manage these new challenges faced by companies all over the world.
This study will focus on small- and medium-sized suppliers as these often lack the resources,
environmental know-how, awareness and strategy to improve their processes to contribute to the entire
supply chain becoming more environmentally friendly (Pimenova and Vorst, 2003). Lee and Klassen
(2008) concluded that the small- and medium-sized enterprises encounter difficulties in implementing the
requirements set by their larger buying firms and, thus, are often considered as a bottleneck in enabling
the customer firms to implement green initiatives. Furthermore, SMEs can account for 70 per cent of total
industrial pollution when regarded as a sector (Hillary, 2004). These enterprises make up 99.8 per cent of
all firms in the EU, they are said to account for 65 per cent of the business revenue generated and 66 per
cent of all employed workers work for a SME (Ilomaki and Melanen, 2001).
The second characteristic of the population of interest is that the firms are operating in the automotive
industry. This industry was selected because of its worldwide scope and its pervasive global
environmental impact. Additionally, as stated by Orsato and Wells (2007) suppliers to the auto mobile
industry provide up to 80 per cent of the value required to manufacture the end-product and, thus,
contribute significantly to the environmental footprint of the entire supply chain. Lastly, the sample was
only taken from the auto mobile industry to control for any potential confounding variables. Market
conditions and environmental regulations differ from one industry to another and by means of studying
solely one industry these variations affecting the independent variable are minimized.
Lastly, the decision was made to perform the study on European suppliers, more specifically German
suppliers, as Europe is the worldwide forerunner in vehicle production and is consequently also home to a
large number of enterprises supplying Europe‘s auto mobile manufacturers. It is expected that, as Europe
is one of the early adopters of ISO 14001 standards, West-European firms are less motivated by media,
competitive and regulatory forces. Consequently, it is assumed that external stakeholders do not exert as
much pressure on suppliers as do governments and buying firms in countries which are considered to be
late adopters of ISO 14001 standards (Welch et al., 2002). This in turn would lead to employees being
more satisfied and would in turn result in increased business performance gains.
4.3 Data Collection Procedure and Response Rate
This last section, which is split into five subsections, outlines the data collection process and provides a
detailed description of how the final respondent number was obtained.
4.3.1 Sample Selection
The survey questionnaire was administered to a subset of the population to be studied, namely
operations/supply chain managers of small- and medium-sized auto mobile enterprises in Germany. The
list of firms in the auto mobile industry was made available by www.marklines.com (2012). The database
enlisted a total of 1071 firms. As a second step the database had to be verified before using the firms as
the target sample. To this end the firm contact details were verified by means of the company websites.
Additionally, if available, the number of full-time employees working at the respective firm was obtained
from the company website. A total of 483 firms were found to not meet the criteria of being a SME thus
the total number of firms which were assumed to meet the expected characteristics were a total of 588. It
should here be noted that the majority of the company websites failed to mention the number of full-time
Master Thesis 2013 Supply Chain Management-Taking an Environmental Perspective Michelle Engert 329909
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employees working at the respective firm, thus, these firms were also taken into account and assumed to
be part of the population of interest. It should also be noted that www.marklines.com (2012) fails to
explicitly state how the 1071 supplying firms in the auto mobile industry were selected from the total
number of instances in the population (the sampling frame).
According to Dul and Hak (2008) the preferred option to guarantee that each instance has the same chance
of being selected is probability sampling (randomly sampling instances from the population).
4.3.2 Selection of Key Informants
As has been stated earlier operations/ supply chain managers were chosen as the population to be studied
as they, according to Walton et al. (1998), are in the position and have the influence to enable the
company to obtain a competitive advantage by means of adopting green practices. More specifically, as
recommended by Mitchell (1994), the survey questionnaire was targeted at the qualified employee of the
supplying firm who has the knowledge and means to implement GSCM practices in the firms supply
chain. Thus, the key informant selected for this study was either the manager or owner of the firm or any
other individual who is actively involved in supply chain issues relating to the respective firm. According
to Mitchell (1994) these high-ranked informants are considered to be more reliable and enable the
standardization of information across differing firms. Sub-sections 4.3.3 and 4.3.4 outline the approach
that was taken to guarantee that only responses from employees dealing with supply chain related
activities were obtained.
It should here be noted that a limitation of this study is the fact that information was only gathered from
one source within each firm. According to Podsakoff et al. (2003) making use of multiple respondents per
firm would be advantageous in reducing common method variance.
4.3.3 Questionnaire Design and Distribution
The choice was made to gather data by means of a self-administered electronic mail survey. The main
advantages/ strengths of this method are anonymity, free expression and confidentiality (Bush and Hair,
1985; Davis, 2000 cited in Saleh, 2006). Furthermore, according to Sutton (2001) (cited in Saleh, 2006)
electronic mail surveys facilitate adequate record keeping and enable the generation of uniform data from
different respondents. Moreover, it can also be noted that this method in comparison to other methods is
not extensively costly. In consideration of these advantages this study made use of an electronic mail
survey for its ability to collect data in a very short period of time from diversely scattered sources.
As has been stated by Greer et al. (2000) industrial populations, characterized as respondents who receive
survey questionnaires at their place of employment, are less likely to respond to survey questionnaires
than consumer groups. The difference in response rates is mainly due to the fact that industrial
populations are preoccupied with work, because of company rules and policies as well as confidentiality
and anonymity issues. Greer et al. (2000) found that a recipients‘ willingness to respond to a
questionnaire did not to a great extent depend on pre-notifications and follow-ups. Decisions on whether
to cooperate or not were more based on the trade-off between perceived costs and benefits to be obtained
from participating in a mail questionnaire. Thus, the following factors were taken into account during the
design of the questionnaire to ensure the obtainment of an adequate number of responses. The choice was
made to make use of the online survey website www.thesistools.com (n.a.) and to distribute the link to the
survey questionnaire via e-mail. The e-mail was not individualized but written in the respondents‘ native
language (German). Furthermore, a description of the project was provided, a detailed explanation on
Master Thesis 2013 Supply Chain Management-Taking an Environmental Perspective Michelle Engert 329909
42
how to fill in the questionnaire and the benefits (incentives) to be obtained. The actual survey
questionnaire started off with a cover letter describing the project, the fact that all information is
confidential and anonymous, and instructions on the procedure were provided. Additionally, respondents
were given an incentive to answer the questionnaire. Respondents were given the opportunity to insert
their e-mail address upon completion of the questionnaire and would receive a copy of the Executive
Summary or Master Thesis subsequent to its completion. In regards to the design of the questionnaire it
can be said that great care was taken to make it as user-friendly as possible with page numbers indicating
the current page position and the number of pages that still needed to be completed. Furthermore, all
questions relating to the topic under investigation were fixed alternative questions (structure of questions),
required a qualitative response (nature of response), sought for an individual‘s opinion (information
sought) and were assessed by means of non-comparative scales (measurement scales). Moreover, to
minimize the possibility of context effects, in which one or more questions has an influence on how an
individual interprets subsequent questions, the choice was made to ask the questions relating to the
dependent concepts (Overall Business Performance, Environmental Performance and Economic
Performance) first and to ask questions relating to GSCM Practice Implementation towards the end to
decrease the potential for prior questions to influence how respondents answer the remainder of the
questions (Tourangeau, 1999). Additionally, the questions which requested more personal information
from the respondent were situated at the end of the survey questionnaire. This, according to Babbie
(2001) and Dillman (2000), enables respondents after having read the cover letter to proceed straight onto
answering the main questions of the survey. On the very last page of the survey questionnaire respondents
were thanked for having completed the survey.
The questionnaire was sent out on the 28 May 2013 and one week subsequent to having distributed the
survey questionnaire telephone follow-up calls were made (4 June 2013). As the questionnaire was
answered anonymously it was not possible to know which firms had replied and which had not thus the
decision was made to make use of simple random sampling when deciding on which firms to contact via
telephone call. This sampling technique is an unbiased surveying technique and guarantees that each
individual has the same probability of being selected at any moment in time (Podsakoff et al., 2003).
4.3.4 Invalid Respondents and Missing Data
In consideration of the fact that this research utilized a self-administered questionnaire the occurrence of
response error (Hyman et al., 1954) had to be taken into account as there was no control over how the
questionnaire was completed. Hence, in order to perform the statistical analysis it was important to
remove data that was invalid or respondents who had not completed the entire survey. A total of 28
people responded in the first round. However, a total of 4 responses had to be deleted and were not taken
into account as these respondents had failed to complete the entire questionnaire. In the second round
telephone follow-up calls were made and a total of 41 people responded. Two responses had to be deleted
due to insufficient data. It should be noted that all respondents that answered the entire questionnaire
(N=63) answered that they were involved in supply chain related activities (Question 16 of the
questionnaire; Appendix 2).
4.3.5 Final Response Rate
After excluding invalid respondents 63 firms remained for data analysis. Chapter 5 will provide a detailed
description of the responding firms‘ characteristics.
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The final number of responses is the first major limitation identified in this study. 63 responses were
received from small- and medium-sized German automobile suppliers which corresponds with a response
rate of 10.71% (=63/588). Thus, it can be concluded that when comparing the sample (N=588) to all
responses (N=63) it is probable that the total responses are not representative for the population implying
non-response bias. In consequence, making generalizations from the sample to the population is not
possible/ advisable. Thus, in future research case study research (comparative case study) is encouraged
to verify the findings.
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5. DATA ANALYSIS
Chapter 5 is divided into five sections each of which has several subsections. The first two sections will
provide a detailed description of the characteristics of the responding firms and also delve into the topic
of Environmental Management Standards adoption. The data analysis will be conducted in Sections 5.3,
5.4 and 5.5 by means of the statistical software programs Statistical Package for Social Science (SPSS)
version 17.0 and Structural Equation Modeling (Amos) version 21.0 using maximum likelihood
estimates. Section 5.4 will determine validity, reliability and goodness-of-fit of the original research
model. In Section 5.5 the same analysis is performed, however, in this last section the model will be
adjusted to more accurately fit the data and to minimize validity and reliability issues.
Note: The model constructs are reflective. Furthermore, making use of Structural Equation Modeling is
deemed most appropriate for this study as, according to Gefen et al. (2000), this method has great
potential for advancing theory development and by utilizing Structural Equation Modeling the researcher
is also able to simultaneously assess numerous interrelated dependence relationships. Moreover, Hair et
al. (1998) (cited by Sridharan, 2010) noted that this modeling technique permits the incorporation of
latent variables representing unobserved concepts while at the same time accounting for measurement
errors.
5.1 Characterization - Responding Firms
Table 3 provides a summary of the responding firms‘ characteristics. From the table it can be derived that
92.1% of the respondents are middle managers which implies that GSCM Practice Implementation is a
supply chain issue mainly dealt with by higher-level management. It should, however, be noted that
respondents might have found the terms employee in charge and middle manager to be interchangeable
especially when considering that the targeted firms are small- and medium-sized companies which cannot
be compared to large hierarchical firms. The question about the respondents‘ work experience in the
industry does not show any clear pattern. 34.9% of respondents have been working in the industry for
more than 15 years and 55.5% of the respondents answered that they have been working in the industry
for a maximum of 10 years.
Even though the European Union classifies large businesses to have a minimum of 250 employees Lee et
al. (2012) took all responding firms up to a maximum employee number of 500 into account. Thus, this
study will also make the cutoff at 500 and from Table 3 it can be derived that all responding firms were
small- and medium-sized. The distribution is as follows: 31 (49.2%) of the firms that responded have less
than 50 employees, 12 (22.2%) have 50-100 employees, 11 (17.5%) have 101-200 employees, and 7
(11.1%) employee 201-500 workers. In regards to the industry classification of the buying firms, all
respondents answered that their buying firms were in the automobile industry and 22 firms also said that
their buying firms operate in the electronics industry.
The last question asked respondents to indicate what their firm‘s primary business goal in the supply
chain is. The majority of the SMEs (65.1%) reported that they are first-tier suppliers to major firms.
28.6% of the firms indicated that they are second-tier suppliers.
Master Thesis 2013 Supply Chain Management-Taking an Environmental Perspective Michelle Engert 329909
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Frequency Percentage Value
Respondents’ job title
Employee in charge
Middle manager
Senior executive
Top executive
Total
5
58
0
0
63
7.9
92.1
0.0
0.0
100.0
Respondents’ work experience in the industry (in years)
Less than 5
5-10
11-15
More than 15
Total
16
19
6
22
63
25.4
30.2
9.5
34.9
100.0
Firm size (no. of full-time employees)
Less than 50
50-100
101-200
201-300
301-400
401-500
More than 500
Total
31
14
11
5
2
0
0
63
49.2
22.2
17.5
7.9
3.2
0.0
0.0
100.0
Industry classification of the buying firms (multiple answers are possible)
Automobile
Electronics
Telecommunication
Retail
Total
63
22
6
3
63
100.0
Firm’s primary business goal in the supply chain
First-tier supplier to major firms
Second-tier supplier
Supplier to government
Other
Total
41
18
0
4
63
65.1
28.6
0.0
6.3
100.0
Table 4: Characteristics of responding firms
5.2 Awareness and Adoption of Environmental Management Standards (EMSs)
The administered survey questionnaire not only asked respondents to provide information about their firm
but also to answer questions in regards to their awareness and degree of adoption of Environmental
Management Standards. From Table 4 it can be concluded that all responding firms were aware of the
existence of the ISO 14000 series and 57 (90.5%) of the firms also adopted ISO 14000. 18 (28.6%) of the
operations/ supply chain managers are aware of the existence of Environmental, Health and Safety (EHS)
programs but the majority (71.4%) have never heard of such a program. In terms of the adoption rate, 12
(19%) firms have adopted EHS programs. Another interesting finding is that 52 (82.5%) of the managers
that responded have never heard of Life Cycle Analysis (LCA) and of those who have heard of LCA only
8 (12.7%) have adopted LCA. The survey results reveal that the most widely adopted EMS is ISO 14000
series – 57 out of 63 firms (90.5%) have implemented it, however, the results also show that there is
limited use of other EMS‘s. This comes as a surprise as this study is based on the assumption that
Germany operating in a mature industry would be seen as a forerunner in EMS adoption. In conclusion it
can be said that in contrast to initial assumptions even in a quite mature country in terms of environmental
regulations there is definite informational potential.
Master Thesis 2013 Supply Chain Management-Taking an Environmental Perspective Michelle Engert 329909
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Awareness Adoption EMSs Yes No Yes No
ISO 14000 Series 63 (100.0%) 0 (0.0%) 57 (90.5%) 6 (9.5%)
Electronic Product Environmental Assessment Tool 8 (12.7%) 55 (87.3%) 6 (9.5%) 57 (90.5%)
European EMAS 7 (11.1%) 56 (88.9%) 0 (0.0%) 63 (100.0%)
EU Eco-Label Award Scheme 2 (3.2%) 61 (96.8%) 0 (0.0%) 63 (100.0%)
EHS Programmers 18 (28.6%) 45 (71.4%) 12 (19.0%) 51 (81%)
LCA 11 (17.5%) 52 (82.5%) 8 (12.7%) 55 (87.3%)
Total Quality Environmental Management 3 (4.8%) 60 (95.2%) 2 (3.2%) 61 (96.8%)
Table 5: Awareness and adoption of Environmental Management Standards
5.3 Correlation Matrix
Table 5 depicts the means (M) and standard deviations (SD) of all the constructs included in the analysis
with the exception of Market Pressure as well as the bivariate Spearman‘s rho correlation results between
them. The constructs were derived by averaging the corresponding scale items. Cohen‘s (1988) (cited in
Sridharan et al., 2010) rule of thumb states that correlations with a value less than 0.2 can be considered
as weak, whereas correlations between 0.2 and 0.5 are regarded to be moderate. Correlations with a value
greater than 0.5 are, according to Cohen (1988) (cited in Sridharan et al., 2010), considered to be strong.
The results show significant relationships among Internal Environmental Management, Green Purchasing,
Customer Cooperation and Eco-Design with Environmental Performance and Economic Performance.
Only Green Purchasing and Eco-Design were found to have a significant relationship with Overall
Business Performance. The correlations between GSCM practices and the three dependent performance
constructs are in the expected direction. Furthermore, there are no excessive correlations between the
constructs in the model. According to Field (2005) multicollinearity is avoided when the correlations
between the constructs do not exceed a value of 0.9.
Factors M SD IEM GP CC ECO SAT OE RE OBP EP ECP
IEM Internal Environmental
Management
3.01 0.74 1.00
GP Green Purchasing
2.76 0.72 0.667
**
1.00
CC Customer Cooperation
2.49 0.70 0.530
**
0.628
**
1.00
ECO Eco-Design
2.70 0.67 0.560 **
0.656 **
0.532 **
1.00
SAT Employee Job
Satisfaction
3.11 0.55 0.219 0.328
**
0.200 0.497
**
1.00
OE Operational Efficiency
2.98 0.60 0.248
*
0.285
*
0.060 0.189 0.258
*
1.00
RE Relational Efficiency
3.51 0.69 0.421 **
0.423 **
0.055 0.193 0.351 **
0.681 **
1.00
OBP Overall Business
Performance
3.41 0.70 0.179 0.278
*
0.186 0.370
**
0.384
**
0.465
**
0.465
**
1.00
EP Environmental Performance
3.02 0.66 0.457 **
0.355 **
0.339 **
0.509 **
0.213 0.306 *
0.351 **
0.265 *
1.00
ECP Economic Performance
3.04 0.65 0.625
**
0.559
**
0.452
**
0.672
**
0.305
*
0.150 0.202 0.268
*
0.443
**
1.00
Table 6: Correlations between theoretical constructs
Notes: ** Correlation is significant at the 0.01 level (2-tailed); * Correlation is significant at the 0.05 level (2-tailed)
5.4 Validity, Reliability and Goodness-of-Fit of the Research Model (Original Model)
In the following the measurement properties of the constructs will be assessed making use of reliability
and item-to-total correlation analysis, after which a confirmatory factor analysis (CFA) is performed to
examine the goodness-of-fit of the research models proposed by Zhu et al. (2008). According to Hooper
et al. (2008) it is foremost, before determining model fit, of importance to assess the fit of each construct
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and its respective items individually. It should here be noted that Section 5.4 will solely identify validity
and reliability issues but no changes to the constructs will be made to improve validity and reliability.
This is of importance to enable a better comparison of this study‘s outcomes to the study performed by
Lee et al. (2012). In Section 5.5 the same analysis is performed again, however, the model will be
adjusted to account for validity and reliability issues.
5.4.1 Step 1 – Assessing Validity of the Constructs
Firstly, before performing reliability estimation it is of importance to determine if the constructs are valid.
Validity can be defined as the degree to which a measuring procedure captures the specific concept that
the researcher aims to measure. Construct validity can be defined as the extent to which a specific number
of variables really represent the theoretical latent construct they are expected to measure (Said, 2011).
Construct validity is made up of four components, namely: face validity, convergent validity, discriminant
validity, and nomological validity.
Face Validity is a subjective determination of whether a measure (the content of the items) appears to
measure what it is supposed to measure. (Schwab, 2005)
Convergent Validity is the extent to which indicators of a construct that theoretically should be related are
indeed related (converge) and thus share a high proportion of variance. (Schwab, 2005)
Discriminant Validity is the extent to which two constructs that are theoretically assumed to be unrelated
are indeed unrelated (truly distinct from each other). (Schwab, 2005)
Nomological Validity is present if a construct correlates as expected within a system of related constructs.
(Schwab, 2005)
In order to establish construct validity using confirmatory factor analysis two components have been
made use of, namely: (1) convergent validity and (2) discriminant validity. Convergent validity will be
examined by means of factor loadings, average variance extracted (AVE) and construct/ composite
reliability. Note: construct/ composite reliability will be determined in Sub-Section 5.4.2.
1. Convergent Validity
Standardized Factor Loadings and t-Values
To determine convergent validity it is foremost of importance to assess the standardized loadings
(standardized regression weights). Standardized loadings characterize the degree of correlation amongst
each observed variable (indicator) and the corresponding factor (latent construct). According to Johnson
et al. (2001) and Nunnally (1978) (cited in Abdul-Halim, 2009) all loadings should be at least 0.5 and
preferably 0.7 or higher (Chin et al., 1995). When assessing the standardized loadings it can be inferred
that a total of six items score slightly lower than 0.5 (Table 8). More specifically, a great deal of variance
in each observed variable is accounted for with the exception of the following variables: IEM5
(R2=0.489
2=0.239), CC1 (R
2=0.486
2=0.236), SAT4 (R
2=0.468
2=0.219), SAT5 (R
2=0.492
2=0.242), ECP1
(R2=0.455
2=0.207) and ECP2 (R
2=0.433
2=0.187). Thus, all loadings except these five are significant
(p<0.05) as is required for convergent validity. Even though this study uses the threshold of 0.5
recommended by Johnson et al. (2001) and Nunnally (1978) (cited in Abdul-Halim, 2009) it should also
be mentioned that other researcher such as Lee and Crompton (1992) as well as Saris et al. (2009, p. 571)
set the threshold at 0.4 stating that any loading above 0.4 still indicates a reasonable and sufficient fit.
However, as the sample size in this study is quite low higher loadings are preferable.
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According to Hooper et al. (2008) one can also assess the R2 value of the items. Items with an R
2 value
below 0.20 should be removed from the analysis as a low R2
value indicates a high level of error. From
Table 8 it can be inferred that all R2 values except the R
2 value for ECP2 (R
2=0.433
2=0.187) are
acceptable.
Furthermore, it is of importance to examine the statistical significance through t-values (Dunn et al.,
1994). The t-values are referred to as critical ratio (C.R.) in the Amos text output file. The critical ratio is
the parameter estimate divided by its standard error. According to Segar (1997) and Byrne (2001)
statistical significance is implied when the t-value is greater than 1.96 or smaller than negative 1.96. The
evidence of there being a relationship between the observed indicators and their latent factor is stronger if
the factor loadings or coefficients are, when compared to their standard errors, larger (Bollen, 1989 and
Koufteros, 1999). In conclusion, it can be inferred from Table 8 that all t-values (critical ratio‘s) for the
individual paths are significantly related to their underlying construct.
Average Variance Extracted
To further draw conclusions about the degree of convergent validity achieved the average variance
extracted (AVE) was also determined. The average variance extracted summarizes the convergence
among a set of items making up a construct. This measure draws a relationship between the amount of
variance that is captured by the construct and the variance arising from measurement error (Fornell and
Larcker, 1981). Amos software is not able to calculate these values, thus, in the following the average
variance extracted (AVE) will be calculated manually.
The AVE is calculated by means of the following formula (Fornell and Larcker, 1981):
AVE= Average Variance Extracted= Variance Extracted
= 𝑠𝑢𝑚 𝑜𝑓 (𝑠𝑡𝑎𝑛𝑑𝑎𝑟𝑑𝑖𝑧𝑒𝑑 𝑙𝑜𝑎𝑑𝑖𝑛𝑔𝑠 𝑠𝑞𝑢𝑎𝑟𝑒𝑑 )
𝑠𝑢𝑚 𝑜𝑓 𝑠𝑡𝑎𝑛𝑑𝑎𝑟𝑑𝑖𝑧𝑒𝑑 𝑙𝑜𝑎𝑑𝑖𝑛𝑔𝑠 𝑠𝑞𝑢𝑎𝑟𝑒𝑑 + (𝑠𝑢𝑚 𝑜𝑓 𝑖𝑛𝑑𝑖𝑐𝑎𝑡𝑜𝑟 𝑚𝑒𝑎𝑠𝑢𝑟𝑒𝑚𝑒𝑛𝑡 𝑒𝑟𝑟𝑜𝑟𝑠 )
𝐼𝑛𝑑𝑖𝑐𝑎𝑡𝑜𝑟 𝑀𝑒𝑎𝑠𝑢𝑟𝑒𝑚𝑒𝑛𝑡 𝐸𝑟𝑟𝑜𝑟 = 1 − (𝑠𝑡𝑎𝑛𝑑𝑎𝑟𝑑𝑖𝑧𝑒𝑑 𝑙𝑜𝑎𝑑𝑖𝑛𝑔)2
Alternatively:
AVE= Average Variance Extracted= Variance Extracted
= 𝑠𝑢𝑚 𝑜𝑓 (𝑠𝑡𝑎𝑛𝑑𝑎𝑟𝑑𝑖𝑧𝑒𝑑 𝑙𝑜𝑎𝑑𝑖𝑛𝑔𝑠 𝑠𝑞𝑢𝑎𝑟𝑒𝑑 )
𝑛
As can be derived from Table 8 the average variance extracted (AVE) of the majority of constructs is
greater than 0.5 (Fornell and Larcker, 1981), thus exhibiting convergence validity. Five constructs
(Cooperation with Customers, Employee Job Satisfaction, Operational Efficiency, Environmental
Performance and Economic Performance) score slightly beneath 0.5 indicating that on average the error
remaining in the items is larger than the variance that is actually explained by the latent factor structure.
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2. Discriminant Validity
As has been stated above discriminant validity is the extent to which two constructs that are theoretically
assumed to be unrelated are indeed unrelated (truly distinct from each other and uncorrelated). Variables
should relate more strongly to the factor they are actually supposed to measure than to another factor. In
essence, variables should load significantly on only one factor. Table 8 provides the calculated
discriminant validity values for each factor.
Discriminant Validity values can be obtained by utilizing the following formula (Said et al., 2011):
DV= 𝐴𝑉𝐸
According to Fornell and Larcker (1981) the existence of discriminant validity can be determined by
comparing the AVE estimates to the squared correlation coefficients between two latent constructs.
Discriminant validity is said to exist if the items measuring one construct share more common variance
than this particular construct shares with any other construct. In essence the AVE estimates for each
individual construct should be greater than the squared correlation coefficient between two constructs
(Hair et al., 2010) (cited in Gaskin, 2012a). More specifically, the thresholds for discriminant validity are
MSV<AVE and ASV<AVE. Having made use of the Sats Tools Package developed by Gaskin (2012b)
Table 6 and Table 7 were obtained. Table 6 provides a summary of the values for composite reliability
(CR), average variance extracted (AVE), maximum shared squared variance (MSV) and the average
shared squared variance (ASV).
Maximum Shared Squared Variance (MSV) is the maximum correlation (squared covariance) with
another factor. (Hair et al., 2010 cited in Gaskin, 2012a)
Average Shared Squared Variance (ASV) is the average of all correlations with other variables. (Hair et
al., 2010 cited in Gaskin, 2012a)
Table 7 is a factor correlation matrix depicting the square root of the average variance extracted (the
discriminant validity values) on the diagonal. All underlined values show validity issues. More
specifically, the AVE for IEM, CC, ECO, GP, OE and ECP is smaller than the MSV (Table 6) implying
validity concerns. Furthermore, the square root of the AVE (Table 7 and Table 8) for IEM, CC, ECO, GP,
OE and ECP is less than the absolute value of the correlations with another factor.
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Validity and Reliability Table
Table 7: Validity and reliability table (original model)
Factor Correlation Matrix with the Square Root of the AVE on the Diagonal
Table 8: Factor correlation matrix with the square root of the AVE on the diagonal (original model)
Factors CR AVE MSV ASV
EP Environmental Performance 0.845 0.477 0.430 0.232
IEM Internal Environmental Management 0.875 0.592 0.682 0.269
OBP Overall Business Performance 0.884 0.655 0.286 0.150
CC Customer Cooperation 0.737 0.414 0.694 0.263
ECO Eco-Design 0.833 0.502 0.594 0.360
GP Green Purchasing 0.784 0.479 0.694 0.384
SAT Employee Job Satisfaction 0.792 0.443 0.428 0.196
OE Operational Efficiency 0.831 0.452 0.672 0.170
RE Relational Efficiency 0.926 0.676 0.672 0.210
ECP Economic Performance 0.882 0.466 0.599 0.328
Factors EP IEM OBP CC ECO GP SAT OE RE ECP
EP Environmental Performance 0.691
IEM Internal Environmental Management 0.499 0.770
OBP Overall Business Performance 0.405 0.187 0.810
CC Customer Cooperation 0.439 0.645 0.216 0.644
ECO Eco-Design 0.656 0.590 0.438 0.725 0.709
GP Green Purchasing 0.494 0.826 0.316 0.833 0.764 0.692
SAT Employee Job Satisfaction 0.305 0.220 0.447 0.367 0.654 0.485 0.665
OE Operational Efficiency 0.395 0.229 0.466 0.058 0.250 0.336 0.376 0.672
RE Relational Efficiency 0.458 0.379 0.535 0.101 0.271 0.453 0.436 0.820 0.822
ECP Economic Performance 0.590 0.671 0.331 0.590 0.771 0.774 0.540 0.332 0.316 0.683
Master Thesis 2013 Supply Chain Management-Taking an Environmental Perspective Michelle Engert 329909
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Summary of Validity and Reliability Measurement Results (Original Model) Factors Item
Number
Standardized
Loading
R2 Average
Variance
Extracted
(AVE)
Discriminant
Validity
Construct/
Composite
Reliability
Critical Ratio
(t-Value)
Internal
Environmental Management
IEM1
IEM2 IEM3
IEM4
IEM5
0.881
0.952 0.705
0.703
0.489
0.776
0.906 0.497
0.494
0.239
0.583 0.764 0.875 _a
10.553 6.623
6.602
4.085
Green Purchasing GP1
GP2
GP3 GP4
0.611
0.850
0.767 0.573
0.373
0.722
0.588 0.328
0.503 0.709 0.784 _a
4.541
4.457 3.654
Cooperation with
Customers
CC1
CC2
CC3 CC4
0.486
0.584
0.795 0.684
0.236
0.341
0.632 0.468
0.419 0.647 0.737 _a
2.951 (p=0.003)
3.210 (p=0.001) 3.162 (p=0.002)
Eco-Design ECO1
ECO2 ECO3
ECO4
ECO5
0.784
0.807 0.715
0.684
0.509
0.615
0.651 0.511
0.468
0.259
0.501 0.708 0.833 _a
6.090 5.456
5.203
3.800
Employee Job Satisfaction
SAT1 SAT2
SAT3
SAT4 SAT5
0.848 0.800
0.611
0.468 0.492
0.719 0.640
0.373
0.219 0.242
0.439 0.663 0.792 _a 5.963
4.682
3.511 3.701
Operational
Efficiency
OE1
OE2 OE3
OE4
OE5 OE6
0.686
0.710 0.548
0.776
0.558 0.733
0.471
0.504 0.300
0.602
0.311 0.537
0.454 0.674 0.831 _a
4.789 3.813
5.129
3.876 4.914
Relational
Efficiency
RE1
RE2 RE3
RE4
RE5 RE6
0.790
0.810 0.837
0.904
0.756 0.829
0.624
0.656 0.701
0.817
0.572 0.687
0.676 0.822 0.926 _a
7.087 7.403
8.203
6.480 7.305
Market Pressure MP1
MP2
0.889
0.536
0.790
0.287
0.539 0.734 0.557 -
Overall Business Performance
OBP1 OBP2
OBP3
OBP4
0.759 0.794
0.873
0.807
0.576 0.630
0.762
0.651
0.655 0.809 0.884 _a 6.254
6.840
6.362
Environmental Performance
EP1 EP2
EP3
EP4 EP5
EP6
0.676 0.686
0.761
0.751 0.612
0.649
0.457 0.471
0.579
0.564 0.375
0.421
0.478 0.691 0.845 _a 4.632
5.029
4.983 4.194
4.416
Economic Performance
ECP1 ECP2
ECP3
ECP4 ECP5
ECP6
ECP7 ECP8
ECP9
0.455 0.433
0.671
0.667 0.730
0.918
0.681 0.659
0.795
0.207 0.187
0.450
0.445 0.533
0.843
0.464 0.434
0.632
0.466 0.683 0.882 _a 2.644 (p=0.008)
3.355
3.348 3.476
3.746
3.377 3.330
3.588
Table 9: Summary of validity and reliability measurement results (original model)
Notes: _a a parameter fixed at 1.0 in the measurement model.; all critical ratios (t-values), unless otherwise stated, are significant at p<0.001
Master Thesis 2013 Supply Chain Management-Taking an Environmental Perspective Michelle Engert 329909
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5.4.2 Step 2 - Assessing Reliability of the Constructs
After having assessed the validity of the constructs it is of importance to determine the reliability.
Reliability can be defined as the extent to which a measuring procedure, if repeatedly administered, yields
consistent results (Said, 2011). To assess reliability the following will make use of two methods, namely:
cronbach‘s alpha and construct/ composite reliability.
1. Cronbach’s alpha
One of the most commonly used methods is cronbach‘s alpha which measures the intercorrelation of
items. To test the measurement properties of the model constructs reliability and item-to-total correlation
analysis was made use of. The reliability test and item-to-total correlation analysis was performed by
means of the statistical software SPSS and the obtained values have been summarized in Table 10. From
the table it can be inferred that there is a reasonable fit between the data collected and the latent factors.
According to George and Mallery (2003) as well as Kline (1999) the internal consistency using
cronbach‘s alpha can be described as follows:
Cronbach’s alpha Internal Consistency α≥ 0.9 Excellent
0.8≤ α < 0.9 Good
0.7≤ α < 0.8 Acceptable (Survey)
0.6≤ α < 0.7 Questionable
0.5≤ α < 0.6 Poor
α < 0.5 Unacceptable
Table 10: Defining internal consistency using cronbach‘s alpha
The cronbach‘s alpha values are all greater than the suggested value of 0.7 (Nunnally and Bernstein,
1994, pp. 264–265) (cited in Iacobucci and Duhachek, 2003) with the exception of the cronbach‘s alpha
value for the moderator Market Pressure which has a value of 0.645. This value is, however, according to
Malhotra and Birks (2007, p.358) still acceptable. The authors state that an alpha value below 0.6 would
indicate unsatisfactory internal consistency reliability. Furthermore, the rather low value for the
cronbach‘s alpha is assumed to be resulting from the comparatively small number of items. Whereas the
remaining factors are comprised of a minimum of 4 items Market Pressure only consists of 2 items. It
should here be kept in mind that a greater number of items can artificially inflate the value for the
cronbach‘s alpha whereas a small number of items can falsely deflate the value of alpha. The last column
of the table (range of corrected item-to-total correlations) displays the range of the correlation of one item
and the composite score of all the other remaining items. More specifically, it is being determined
whether there is a strong, positive correlation between one item and the combined score of the remaining
items comprising the respective construct. When assessing the item loadings on the factors it can be
concluded that all item scores are internally consistent with the composite scores from the remaining
items of the respective construct (> 0.3) (de Vaus, 2001 cited in Tek and Ruthven, 2003). According to
de Vaus (2001) (cited in Tek and Ruthven, 2003) any score below 0.30 is considered to be a weak
correlation for item-analysis intentions. The item would have to be removed. Furthermore, a value greater
than 0.75 would indicate that the item is responsible for the majority of the correlation and nearly
measuring the whole scale thus implying redundancy (de Vaus, 2001 cited in Tek and Ruthven, 2003).
Master Thesis 2013 Supply Chain Management-Taking an Environmental Perspective Michelle Engert 329909
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Factors Number of
Items
Mean SD Cronbach’s
alpha
Range of corrected item-
to-total correlations
Internal Environmental
Management
5 3.01 0.74
0.866 0.487-0.842
Green Purchasing 4 2.76 0.72 0.794 0.562-0.680
Cooperation with
Customers
4 2.49 0.70 0.729 0.437-0.618
Eco-Design 5 2.70 0.67 0.822 0.478-0.692
Employee Job
Satisfaction
5 3.11 0.55 0.789 0.42-0.67
Operational Efficiency 6 2.98 0.60 0.819 0.535-0.665
Relational Efficiency 6 3.51 0.69 0.924 0.710-0.862
Market Pressure 2 2.78 0.69 0.645 0.476-0.476
Overall Business
Performance
4 3.41 0.70 0.875 0.708-0.791
Environmental
Performance
6 3.02 0.66 0.844 0.562-0.681
Economic Performance 9 3.04 0.65 0.878 0.443-0.853
Table 11: Summary of cronbach‘s alpha and item-to-total correlations measurement results (original model)
2. Construct/ Composite Reliability
Construct/ composite reliability is a measure of reliability and internal consistency which is based on the
square of the sum of standardized factor loadings of a construct.
Construct reliability is determined by making use of the following formula (Said et al., 2011):
CR= Construct Reliability
= 𝑠𝑞𝑢𝑎𝑟𝑒 𝑜𝑓 𝑡𝑜𝑡𝑎𝑙 𝑠𝑡𝑎𝑛𝑑𝑎𝑟𝑑𝑖𝑧𝑒𝑑 𝑙𝑜𝑎𝑑𝑖𝑛𝑔
𝑠𝑞𝑢𝑎𝑟𝑒 𝑜𝑓 𝑡𝑜𝑡𝑎𝑙 𝑠𝑡𝑎𝑛𝑑𝑎𝑟𝑑𝑖𝑧𝑒𝑑 𝑙𝑜𝑎𝑑𝑖𝑛𝑔 + (𝑠𝑢𝑚 𝑜𝑓 𝑖𝑛𝑑𝑖𝑐𝑎𝑡𝑜𝑟 𝑚𝑒𝑎𝑠𝑢𝑟𝑒𝑚𝑒𝑛𝑡 𝑒𝑟𝑟𝑜𝑟𝑠 )
The threshold for construct reliability is 0.8 according to Koufteros (1999). From Table 8 it can be
inferred that almost all constructs show construct reliability. This implies that almost all constructs
capture significantly more of the variance than the variance revealed by the error components. However,
Hair et al. (2010) (cited in Gaskin, 2012a) set the threshold for construct reliability at 0.7 which would
imply that all constructs except the one for Market Pressure show construct reliability.
5.4.3 Step 3 - Goodness-of-Fit of the Research Model
The following section will calculate goodness-of-fit indices for both the first- and second-order
measurement models developed by Zhu et al. (2008) as well as for the mediators, moderator and the
dependent concepts. This will provide information on the extent to which the statistical model represents
a set of observations. By means of goodness-of-fit indices researchers are able to identify discrepancies
between the observed and expected values obtained by utilizing a specific statistical model. (Maydeu-
Olivares and Garcia-Forero, 2010)
Scale Independent Concept - GSM Practice Implementation
Lee et al. (2012) adopted the measurement model for GSCM Practice Implementation from Zhu et al.
(2008) who developed both first- and second-order measurement models for the construct. Lee et al.
(2012) were able to establish validity and reliability for both the first- and second-order models.
Master Thesis 2013 Supply Chain Management-Taking an Environmental Perspective Michelle Engert 329909
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1. Goodness-of-Fit Indices
In confirmatory factor analysis, as opposed to most statistical methods, model fit is assessed by means of
multiple statistical tests. This is of importance as a single fit index only reflects one specific aspect of
model fit and is thus not able to provide information on overall model fit. The following will determine
how plausible the models are. According to Kline (2005) (cited in Hooper et al., 2008) the following
statistics ought to be reported: chi-squared test, root mean square error of approximation (RMSEA), the
comparative fit index (CFI), and the standardized root mean square residual (SRMR).
Chi-Squared Test is a statistical test utilized to compare data that is expected to be obtained according to a
specific hypothesis with data that is actually obtained/ observed. The chi-square test tests the null
hypothesis which states there to be no significant difference between the expected and the actually
observed results. (Koufteros and Marcoulides, 2006; Hu and Bentler, 1999) Even though the chi-square is
the most commonly used method to determine model fit Hair et al. (2006) (cited in Bigné Alcañiz, 2009)
criticize it to be highly sensitive to sample size. When making use of the chi-square difference test as well
as the chi-squared test it was found that minor differences when using large samples may be found to be
significant while in rather small samples large differences may test as non-significant. Thus, the authors
propose to additionally evaluate the CFI and RMSEA.
Root Mean Square Error of Approximation (RMSEA) is a measure of goodness-of-fit for statistical
models. According to Kaplan (2000, p.111) (cited in Schermelleh-Engel, 2003) the goal is for the
population to have a close fit with the model as opposed to having an exact fit which is said to not be
convenient when dealing with large populations.
The computational formula is as follows:
RMSEA = (𝜒2−𝑑𝑓)
[𝑑𝑓 𝑁−1 ]
Note: N is the sample size and df depicts the degrees of freedom.
Comparative Fit Index (CFI) is also known as the Bentler Comparative Fit Index. Here, the existing
model is compared to a null model also called the independence model in which it is assumed that the
latent variables are uncorrelated. The CFI compares the covariance matrices of the predicted and the
observed model and also compares the covariance matrix of the null model (covariance matrix of 0‘s) to
the observed covariance matrix to determine the percentage value of lack of fit when deciding to use the
new model instead of the null model. The value for CFI ranges from 0 to 1, the latter indicating a good fit.
(Bollen and Long, 1993) It should be noted that Bentler (1989) (cited in Medcof and Hausdorf, 1995) and
Kline (1998) recommend using the CFI when dealing with fewer than 200 respondents as the comparative
fit index is likely to produce biased estimates.
The computational formula is as follows:
𝐶𝐹𝐼 =𝑑 𝑁𝑢𝑙𝑙 𝑀𝑜𝑑𝑒𝑙 − 𝑑(𝑃𝑟𝑜𝑝𝑜𝑠𝑒𝑑 𝑀𝑜𝑑𝑒𝑙)
𝑑(𝑁𝑢𝑙𝑙 𝑀𝑜𝑑𝑒𝑙)
Note: 𝑑 = 𝜒2 − 𝑑f
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Standardized Root Mean Square Residual (SRMR) is an absolute measure of fit (a value of zero indicates
perfect fit) and depicts the standardized difference between the observed and predicted correlation. The
standardized root mean square residual is a positively biased measure and the bias is said to be greater for
studies which are characterized by a small N and low degrees of freedom. (Hu and Bentler, 1999)
Having made use of the statistical software Amos Table 11 depicts the goodness-of-fit indices for the two
models. The CFI for the first-order model as well as for the second-order model with values of 0.858 and
0.860, respectively, were slightly below the acceptable value of 0.9 (Hu and Bentler, 1999). The SRMR
values were acceptable for both models (≤ 0.09) (Hu and Bentler, 1999) and the χ2 statistics of 208.843
at 129 degrees of freedom implying that χ2/df=1.619 for the first-order model and the χ2 statistics of
210.097 at 131 degrees of freedom implying that χ2/df=1.604 for the second-order model were less than
the benchmark of 2.0 considered optimal by Koufteros and Marcoulides (2006). It can, thus, be concluded
that the items constituting the construct GSCM Practice Implementation are plausible (to a great extent
represent the same theoretical construct/ scales; are unidimensional to a great extent); however, the
models could be adjusted to more accurately fit the data.
It should here be noted that according to Hooper et al. (2008) it is not uncommon to discover that the
proposed model has a poor fit with the data in consideration of the complexity of structural equation
modeling. Even though basing the decision on whether to modify the model or not on modification
indices is not recommended some modifications can, however, considerably improve the obtained results.
Note: the modification analysis will be performed in Section 5.5.
Model Statistics First-Order Second-Order Recommended Value
χ2 208.843 210.097
df 129 131
χ2/df (cmin/df) 1.619 1.604 <2 good (Tabachink and Fidell, 2007 cited in
Hooper et al., 2008 and Koufteros and
Marcoulides, 2006); <5 sometimes permissible
(Wheaton et al. 1977)
p-value for the model 0.000 0.000 >0.05 (Barrett, 2007)
CFI 0.858 0.860 ≥ 0.95 great; >0.90 traditional; >0.08
sometimes permissible (Hair et al., 2010, p.
654)
>0.90 (Hu and Bentler, 1999)
SRMR 0.0863 0.0859 ≤ 0.09 (Hu and Bentler, 1999)
RMSEA 0.100 0.099 <0.08 good; 0.08-0.10 moderate; >0.10 bad
(MacCullum et al., 1996)
<0.07 (Steiger, 2007)
Table 12: Statistics of first- and second-order models (original model)
2. Chi-Square Difference Test
Before making a decision on which model would be best to make use of it is necessary to statistically
compare the fit of the first-order model with the higher-order model. Marsh and Hocevar (1985)
recommend performing the likelihood ratio test also known as the chi-square difference test to evaluate
the efficacy of the two models. This method tests the null hypothesis of there being no significant
difference in fit by determining whether the chi-square difference is significant taking into account the
known degrees of freedom and the chosen significance level. The null hypothesis is rejected if the
difference is significant. As stated previously, a limitation of this test is that it is sensitive to sample size.
In large samples minor differences may be found to be significant while in rather small samples large
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differences may test as non-significant. To compute the chi-square difference test, the difference of the
chi-square values as well as the difference between the degrees of freedom of both models is taken.
𝜒𝑑𝑖𝑓𝑓2 = 𝜒𝑀1
2 − 𝜒𝑀22 𝜒𝑑𝑖𝑓𝑓
2 = 210.097-208.843 = 1.254
𝑑𝑓𝑑𝑖𝑓𝑓 = 𝑑𝑓𝑀1 − 𝑑𝑓𝑀2 𝑑𝑓𝑑𝑖𝑓𝑓 = 131-129 = 2
M1 denotes the ‗smaller‘ model which in comparison to the ‗larger‘ model M2 has more degrees of
freedom (fewer parameters). The value for χdiff2 = 1.254 is distributed with dfdiff = 2 and checking the
significance by means of a χ2-table it can be concluded that the null hypothesis is not rejected. The results
show that the difference between the χ2 statistics for the first- and second-order models is 1.254 which is
smaller than 5.991 where the degree of freedom is 2 at p≤ 0.05. Thus, it can be concluded that there is no
statistically significant difference between the ‗smaller‘ model (the first-order model) and the higher-
order model. Furthermore, Beltrάn-Martίn et al. (2008) were able to conclude that the existing covariation
between the first-order factors and the observable variables can in its entirety be explained by their
regression onto the second-order factor. Hence, taking this into account and to be able to compare the
results of this study to the study performed by Lee et al. (2012) the decision was made to make use of the
second-order model throughout this study to test the hypothesized relationships.
Figure 6 depicts the path diagram of the first-order model and Figure 7 depicts the second-order factor
measurement model for GSCM Practice Implementation. Latent constructs are shown as an oval. Each
measured variable is associated with an error term which, for simplicity, are not shown in the exhibits.
Two headed connections are a sign of covariance between constructs and one headed connectors reveal
there to be a path from a construct to an indicator variable (a measured variable). Measured variables are
labeled corresponding to those in the questionnaire.
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Path Diagram of the Measurement Model (First-Order-Model)
IEM
GP
CC
ECO
IEM1
IEM2
IEM3
IEM4
IEM5
ECO1
ECO2
ECO3
ECO4
ECO5
CC1
CC2
CC3
CC4
GP1
GP2
GP3
GP4
0.77
0.88
0.52
0.51
0.26
0.59
0.55
0.44
0.37
0.32
0.49
0.47
0.37
0.58
0.64
0.52
0.51
0.27
0.58
0.80
0.84
0.74
0.64
0.77
0.88
0.94
0.72
0.71
0.51
0.77
0.74
0.66
0.61
0.56
0.70
0.69
0.61
0.80
0.72
0.71
0.52
0.76
Figure 6: Path diagram of the first-order measurement model (original model)
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Path Diagram of the Measurement Model (Second-Order-Model)
IEM
GP
CC
ECO
IEM1
IEM2
IEM3
IEM4
IEM5
ECO1
ECO2
ECO3
ECO4
ECO5
CC1
CC2
CC3
CC4
GP1
GP2
GP3
GP4
0.77
0.88
0.52
0.51
0.26
0.57
0.57
0.46
0.36
0.33
0.49
0.45
0.37
0.57
0.62
0.53
0.50
0.28
0.94
0.72
0.71
0.51
0.76
0.76
0.68
0.60
0.57
0.70
0.67
0.61
0.79
0.73
0.71
0.53
0.76
0.88
GSCM
0.78
0.99
0.86
0.79
Figure 7: Path diagram of the second-order measurement model (original model)
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Scale Mediators, Moderator and Dependent Concepts
To assess the construct validity of the mediators, moderator and dependent concepts the
unidimensionality of all seven constructs was determined (Steenkamp and van Trijp, 1991). This is a
necessary step to ensure that the indicator variables of a construct measure the same thing. There are
several methods which can be made use of to test unidimensionality. The most prominent method for
testing unidimensionality is cronbach‘s alpha. Assessing reliability in terms of cronbach‘s alpha has
already been done previously (Sub-Section 5.4.2) thus the following will focus on a second method –
confirmatory factor analysis - to determine whether the model fit indices indicate a good fit to the data.
Confirmatory Factor Analysis in Structural Equation Modeling
Here, the measurement models will be assessed separately from the structural model. For each model the
model fit indices were determined by making use of the statistical software Amos. Table 12 summarizes
the results obtained.
From the table it can be concluded that only one SRMR is not less than 0.09 thus the majority of
constructs satisfy the cutoff point suggested by Hu and Bentler (1999). The CFI‘s range from 0.788 to
1.000, however, the cutoff point suggested by Hu and Bentler (1999) is at a minimum of 0.90 implying
that the constructs Employee Job Satisfaction and Operational Efficiency need further analysis. In terms
of the χ2 statistic, even though almost all χ2/df ratios of the constructs were greater than 2.0 Medsker et
al. (1994) state that any χ2/df ratios which are below 10 can be regarded as indicating a good fit with the
data. In terms of the RMSEA, the majority of the values do not satisfy the upper limit of 0.07 suggested
by Steiger (2007). The value for RMSEA tends to improve as more items are added and is said to
artificially inflate if df and N are low (Kenny et al., 2011 cited in Filippov et al., 2012). Thus, Kenny et al.
(2011) (cited in Filippov et al., 2012) argue to refrain from computing the RMSEA for low df models. It
should here be noted that from the table it can be inferred that the construct Market Pressure with zero
degrees of freedom is just-identified. Identification is defined as the degree to which there is a satisfactory
number of equations enabling the solving for every coefficient (unknown) which has to be estimated. The
model is just-identified when there are zero degrees of freedom and the number of equations is equal to
the number of estimated coefficients. As structural equation models are always over-identified it is
probable that the construct Market Pressure does not have enough items. Thus, it is highly likely that
when performing the moderator analysis no results will be obtained. (Kenny, 2011) The analysis will be
performed in Chapter 6, Section 6.1.3.
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Model 𝛘𝟐 df p 𝛘𝟐/𝐝𝐟 CFI SRMR RMSEA
GSCM Practice
Implementation First-Order
179.551 125 0.001 1.436 0.903 0.0825 0.084
GSCM Practice
Implementation Second-
Order
155.445 113 0.005 1.376 0.919 0.0842 0.08
Employee Job Satisfaction
Scale
27.140 5 0.000 5.428 0.788 0.1062 0.267
Operational Efficiency
Scale
26.148 9 0.002 2.905 0.867 0.0793 0.175
Relational Efficiency Scale 26.843 9 0.001 2.983 0.935 0.0474 0.179
Market Pressure Scale 0.000 0 - - 1.000 0.000 0.491
Overall Business
Performance Scale
0.945 2 0.624 0.472 1.000 0.0139 0.000
Environmental Performance
Scale
8.647 9 0.470 0.961 1.000 0.0422 0.000
Economic Performance
Scale
52.625 27 0.002 1.949 0.900 0.0885 0.124
Table 13: Fit indices for the mediators, moderator and dependent concepts (original model)
Figure 8 depicts the path diagrams of the measurement models for Employee Job Satisfaction,
Operational Efficiency, Relational Efficiency, Market Pressure and the three dependent concepts (Overall
Business Performance, Environmental Performance and Economic Performance). Latent constructs are
shown as an oval. Each measured variable is associated with an error term which, for simplicity, are not
shown in the exhibits. Two headed connections are a sign of covariance between constructs and one
headed connectors reveal there to be a path from a construct to an indicator variable (a measured
variable). Measured variables are labeled corresponding to those in the questionnaire.
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Path Diagrams of the Measurement Models
SAT
SAT1
SAT2
SAT3
SAT4
SAT5
0.72
0.64
0.37
0.22
0.24
0.80
0.61
0.47
0.49
0.85 0.47
0.50
0.30
0.60
0.31
0.54
OE1
OE2
OE3
OE4
OE6
OE5
0.71
0.55
0.78
0.56
0.69
0.73
0.62
0.65
0.70
0.82
0.57
0.69
RE1
RE2
RE3
RE4
RE5
RE6
0.81
0.84
0.90
0.76
0.79
0.83
RE MP1
MP2
0.79
0.29 0.54
0.89
OBP1
OBP2
OBP3
OBP4
0.58
0.53
0.76
0.65
0.76
0.79
0.87
0.81
0.46
0.47
0.58
0.56
0.37
0.42
EP1
EP2
EP3
EP4
EP5
EP6
EP
0.68
0.69
0.76
0.75
0.61
0.65
OBP
MP
OE
0.21
0.19
0.45
0.45
0.53
0.84
ECP1
ECP2
ECP3
ECP4
ECP5
ECP6
ECP
0.45
0.43
0.67
0.67
0.73
0.92
0.46
0.43
0.63
ECP7
ECP8
ECP9
0.68
0.66
0.80
Figure 8: Path diagrams of the measurement models (original model)
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5.5 Validity, Reliability and Goodness-of-Fit of the Research Model (Modified Model)
In the following the measurement properties of the constructs will be assessed making use of reliability
and item-to-total correlation analysis, after which a confirmatory factor analysis (CFA) is performed to
examine the goodness-of-fit of the research models proposed by Zhu et al. (2008). It should here be noted
that Section 5.5 will identify validity and reliability issues and changes will be made to the constructs to
improve validity and reliability. This is of importance to determine the robustness of the model. However,
by making adjustments it will not be possible to compare the outcomes to the study performed by Lee et
al. (2012).
5.5.1 Step 1 – Assessing Validity of the Constructs
Firstly, before performing reliability estimation is of importance to determine if the constructs are valid.
In order to establish construct validity using confirmatory factor analysis two components have been
made use of, namely: (1) convergent validity and (2) discriminant validity. Convergent validity will be
examined by means of factor loadings, average variance extracted (AVE) and construct/ composite
reliability. Note: construct/ composite reliability will be determined in Sub-Section 5.5.2.
1. Convergent Validity
Standardized Factor Loadings and t-Values
To determine convergent validity it is foremost of importance to assess the standardized loadings
(standardized regression weights). According to Johnson et al. (2001) and Nunnally (1978) (cited in
Abdul-Halim, 2009) all loadings should be at least 0.5 and preferably 0.7 or higher (Chin et al., 1995).
From Table 8 it was previously inferred that a total of five items score slightly lower than 0.5. More
specifically, a great deal of variance in each observed variable is accounted for with the exception of
IEM5 (R2=0.2892=0.239), CC1 (R2=0.486
2=0.236), SAT4 (R2=0.468
2=0.219), SAT5
(R2=0.4922=0.242), ECP1 (R2=0.455
2=0.207) and ECP2 (R2=0.492
2=0.187). Thus, all loadings except
these five are significant (p<0.05) as is required for convergent validity. To increase validity and after
having determined the effects on the remaining items of removing each problematic item individually the
decision was made to remove problematic items (IEM5, CC1, SAT4, OE3, OE5, EP5, ECP1 and ECP2)
which loaded relatively lowly. Table 15 provides a summary of the adjusted constructs and the new
standardized loadings.
Furthermore, it is of importance to examine the statistical significance through t-values (Dunn et al.,
1994). Form Table 15 in can be inferred that all t-values (critical ratio‘s) for the individual paths were
significantly related to their underlying construct.
Average Variance Extracted
To further draw conclusions about the degree of convergent validity achieved the average variance
extracted (AVE) was also determined. Amos software is not able to calculate these values, thus, the
average variance extracted (AVE) will be calculated manually.
As can be derived from Table 8 the average variance extracted (AVE) estimates of the majority of
constructs are greater than 0.5 (Fornell and Larcker, 1981), thus exhibiting convergence validity. Three
constructs (Cooperation with Customers, Operational Efficiency and Environmental Performance) score
slightly beneath 0.5 indicating that on average the error remaining in the items is larger than the variance
that is actually explained by the latent factor structure. The decision was made not to delete any items
relating to Cooperation with Customers due to the fact that this construct would then only be measured by
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a total of two items. Items OE3, OE5 and EP5 were, however, deleted and proved to have a positive
impact on the average variance extracted values which now are greater than 0.5 for Operational
Efficiency and Environmental Performance (Table 15).
2. Discriminant Validity
As has been stated previously discriminant validity is the extent to which two constructs that are
theoretically assumed to be unrelated are indeed unrelated (truly distinct from each other and
uncorrelated). Table 15 provides the calculated discriminant validity values for each factor.
The thresholds for discriminant validity are MSV<AVE and ASV<AVE (Hair et al., 2010 cited in
Gaskin, 2012b). Having made use of the Sats Tools Package developed by Gaskin (2012b) Tables 13 and
14 were obtained. Table 13 provides a summary of the values for composite reliability (CR), average
variance extracted (AVE), maximum shared squared variance (MSV) and the average shared squared
variance (ASV). Table 14 is a factor correlation matrix depicting the square root of the average variance
extracted (the discriminant validity values) on the diagonal. All underlined values show validity issues.
More specifically, the AVE for CC, ECO, GP, OE and ECP is smaller than the MSV (Table 13) implying
validity concerns. Furthermore, the square root of the AVE (Table 14 and Table 15) for CC, ECO, GP,
OE and ECP is less than the absolute value of the correlations with another factor.
Validity and Reliability Table
Table 14: Validity and reliability table (modified model)
Factors CR AVE MSV ASV
EP Environmental Performance 0.831 0.497 0.393 0.212
IEM Internal Environmental Management 0.890 0.672 0.645 0.253
OBP Overall Business Performance 0.884 0.655 0.285 0.137
CC Customer Cooperation 0.723 0.466 0.591 0.253
ECO Eco-Design 0.832 0.502 0.612 0.359
GP Green Purchasing 0.787 0.483 0.645 0.366
SAT Employee Job Satisfaction 0.787 0.492 0.423 0.177
OE Operational Efficiency 0.820 0.534 0.546 0.138
RE Relational Efficiency 0.926 0.677 0.546 0.186
ECP Economic Performance 0.892 0.546 0.612 0.320
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Factor Correlation Matrix with the Square Root of the AVE on the Diagonal
Table 15: Factor correlation matrix with the square root of the AVE on the diagonal (modified model)
Summary of Validity and Reliability Measurement Results (Modified Model) Factors Item
Number
Standardized
Loading
R2 Average
Variance
Extracted
(AVE)
Discriminant
Validity
Construct/
Composite
Reliability
Critical Ratio
(t-value)
Internal
Environmental Management
IEM1
IEM2 IEM3
IEM4
0.874
0.962 0.704
0.692
0.764
0.925 0.496
0.925
0.666 0.816 0.890 _a
10.308 6.600
6.432
Green Purchasing GP1 GP2
GP3
GP4
0.611 0.850
0.767
0.573
0.373 0.722
0.588
0.328
0.503 0.709 0.787 _a 4.541
4.457
3.654
Cooperation with Customers
CC2 CC3
CC4
0.536 0.824
0.693
0.287 0.679
0.480
0.482 0.694 0.723 _a 3.172
3.434
Eco-Design ECO1 ECO2
ECO3
ECO4 ECO5
0.784 0.807
0.715
0.684 0.509
0.615 0.651
0.511
0.468 0.259
0.501 0.708 0.832 _a 6.090
5.456
5.203 3.800
Employee Job
Satisfaction
SAT1
SAT2 SAT3
SAT5
0.863
0.820 0.550
0.493
0.745
0.672 0.303
0.243
0.594 0.771 0.787 _a
5.673 4.154
3.697
Operational
Efficiency
OE1
OE2 OE4
OE6
0.675
0.765 0.779
0.717
0.456
0.585 0.607
0.514
0.540 0.735 0.820 _a
4.870 4.918
4.658
Relational Efficiency
RE1 RE2
RE3
RE4 RE5
RE6
0.790 0.810
0.837
0.904 0.756
0.829
0.624 0.656
0.701
0.817 0.572
0.687
0.676 0.822 0.926 _a 7.087
7.403
8.203 6.480
7.305
Market Pressure MP1
MP2
0.889
0.536
0.790
0.287
0.539 0.734 0.557 -
Overall Business
Performance
OBP1
OBP2
OBP3 OBP4
0.759
0.794
0.873 0.807
0.576
0.630
0.762 0.651
0.655 0.809 0.884 _a
6.254
6.840 6.362
Environmental
Performance
EP1
EP2 EP3
EP4
0.687
0.673 0.759
0.762
0.472
0.453 0.576
0.581
0.500 0.707 0.831 _a
4.548 5.001
5.011
Factors EP IEM OBP CC ECO GP SAT OE RE ECP
EP Environmental Performance 0.705
IEM Internal Environmental Management 0.463 0.820
OBP Overall Business Performance 0.370 0.184 0.809
CC Customer Cooperation 0.452 0.620 0.244 0.682
ECO Eco-Design 0.627 0.578 0.442 0.733 0.708
GP Green Purchasing 0.480 0.803 0.315 0.769 0.767 0.695
SAT Employee Job Satisfaction 0.275 0.204 0.449 0.388 0.650 0.476 0.702
OE Operational Efficiency 0.373 0.229 0.345 0.059 0.279 0.354 0.255 0.731
RE Relational Efficiency 0.415 0.358 0.534 0.067 0.274 0.452 0.398 0.739 0.823
ECP Economic Performance 0.581 0.665 0.323 0.581 0.782 0.764 0.503 0.335 0.313 0.739
Master Thesis 2013 Supply Chain Management-Taking an Environmental Perspective Michelle Engert 329909
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EP6 0.639 0.408 4.350
Economic
Performance
ECP3
ECP4
ECP5
ECP6 ECP7
ECP8
ECP9
0.659
0.651
0.746
0.901 0.694
0.677
0.814
0.434
0.424
0.557
0.812 0.482
0.458
0.663
0.547 0.740 0.892 _a
4.583
5.149
5.952 4.845
4.739
5.531
Table 16: Summary of validity and reliability measurement results (modified model)
Notes: _a a parameter fixed at 1.0 in the measurement model.; all critical ratios (t-values), unless otherwise stated, are significant at p<0.001
5.5.2 Step 2 - Assessing Reliability of the Constructs
After having assessed the validity of the constructs it is of importance to determine the reliability.
Reliability can be defined as the extent to which a measuring procedure, if repeatedly administered, yields
consistent results (Said, 2011). To assess reliability the following will make use of two methods, namely:
cronbach‘s alpha and construct/ composite reliability.
1. Cronbach’s alpha
One of the most commonly used methods is cronbach‘s alpha which measures the intercorrelation of
items. To test the measurement properties of the model constructs reliability and item-to-total correlation
analysis was made use of. The reliability test and item-to-total correlation analysis was performed by
means of the statistical software SPSS and the obtained values have been summarized in Table 17. From
the table it can be inferred that there is a reasonable fit between the data collected and the latent factors.
According to George and Mallery (2003) as well as Kline (1999) the internal consistency using
cronbach‘s alpha can be described as follows:
Cronbach’s alpha Internal Consistency α≥ 0.9 Excellent
0.8≤ α < 0.9 Good
0.7≤ α < 0.8 Acceptable (Survey)
0.6≤ α < 0.7 Questionable
0.5≤ α < 0.6 Poor
α < 0.5 Unacceptable
Table 17: Defining internal consistency using cronbach‘s alpha
The cronbach‘s alpha values are all greater than the suggested value of 0.7 (Nunnally and Bernstein,
1994, pp. 264–265) (cited in Iacobucci and Duhachek, 2003) with the exception of the cronbach‘s alpha
value for the moderator Market Pressure which has a value of 0.645. This value is, however, according to
Malhotra and Birks (2007, p.358) still acceptable. The authors state that an alpha value below 0.6 would
indicate unsatisfactory internal consistency reliability. Furthermore, the rather low value for the
cronbach‘s alpha is assumed to be resulting from the comparatively small number of items. Whereas the
remaining factors are comprised of a minimum of 3 items Market Pressure only consists of 2 items. It
should here be kept in mind that a greater number of items can artificially inflate the value for the
cronbach‘s alpha whereas a small number of items can falsely deflate the value of alpha. The last column
of the table (range of corrected item-to-total correlations) displays the range of the correlation of one item
and the composite score of all the other remaining items. More specifically, it is being determined
whether there is a strong, positive correlation between one item and the combined score of the remaining
items comprising the respective construct. When assessing the item loadings on the factors it can be
concluded that all item scores are internally consistent with the composite scores from the remaining
Master Thesis 2013 Supply Chain Management-Taking an Environmental Perspective Michelle Engert 329909
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items of the respective construct (> 0.3) (de Vaus, 2001 cited in Tek and Ruthven, 2003). According to
de Vaus (2001) (cited in Tek and Ruthven, 2003) any score below 0.30 is considered to be a weak
correlation for item-analysis intentions. The item would have to be removed. Furthermore, a value greater
than 0.75 would indicate that the item is responsible for the majority of the correlation and nearly
measuring the whole scale implying redundancy (de Vaus, 2001 cited in Tek and Ruthven, 2003).
Factors Number
of Items
Mean SD Cronbach’s
alpha
Change in
Cronbach’s
alpha
Range of corrected
item-to-total
correlations
Internal
Environmental
Management
4 2.96 0.81 0.883
↑
0.674-0.863
Green Purchasing 4 2.76 0.72 0.794 - 0.562-0.680
Cooperation with
Customers
3 2.59 0.77 0.713 ↓
0.453-0.616
Eco-Design 5 2.70 0.67 0.822 - 0.478-0.692
Employee Job
Satisfaction
4 3.23 0.57 0.775 ↓
0.466-0.687
Operational
Efficiency
4 3.08 0.64 0.811 ↓
0.619-0.676
Relational
Efficiency
6 3.51 0.69 0.924 -
0.710-0.862
Market Pressure 2 2.78 0.69 0.645 - 0.476-0.476
Overall Business
Performance
4 3.41 0.70 0.875 -
0.708-0.791
Environmental
Performance
5 3.06 0.67 0.813 ↓
0.571-0.601
Economic
Performance
7 3.16 0.71 0.889 ↑
0.589-0.842
Table 18: Summary of cronbach‘s alpha and item-to-total correlations measurement results (modified model)
2. Construct/ Composite Reliability
Construct/ composite reliability is a measure of reliability and internal consistency which is based on the
square of the sum of standardized factor loadings of a construct.
The threshold for construct reliability is 0.8 according to Koufteros (1999). From Table 17 it can be
inferred that a total of four constructs show construct reliability issues. This implies that the majority with
the exception of these four constructs capture significantly more of the variance than the variance
revealed by the error components. However, Hair et al. (2010) (cited in Gaskin, 2012a) set the threshold
for construct reliability at 0.7 which would imply that all constructs except the one for Market Pressure
show construct reliability.
5.5.3 Step 3 - Goodness-of-Fit of the Research Model
The following section will calculate goodness-of-fit indices for the modified first- and second-order
measurement models which were originally developed by Zhu et al. (2008). Furthermore, the goodness-
of-fit indices for the mediators, moderator and the dependent concepts will be determined. This will
provide information on the extent to which the statistical model represents a set of observations.
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Scale Independent Concept - GSM Practice Implementation
Lee et al. (2012) adopted the measurement model for GSCM Practice Implementation from Zhu et al.
(2008) who developed both first- and second-order measurement models for the construct. Lee et al.
(2012) were able to establish validity and reliability for both the first- and second-order models.
1. Goodness-of-Fit Indices
In confirmatory factor analysis, as opposed to most statistical methods, model fit is assessed by means of
multiple statistical tests. The following will determine how plausible the models are. According to Kline
(2005) (cited in Hooper et al., 2008) the following statistics ought to be reported: chi-squared test, root
mean square error of approximation (RMSEA), the comparative fit index (CFI), and the standardized root
mean square residual (SRMR).
Having made use of the statistical software Amos Table 18 depicts the goodness-of-fit indices for the two
models. The CFI for the first-order model as well as for the second-order model with values of 0.899 and
0.899, respectively, were slightly below the acceptable value of 0.9 (Hu and Bentler, 1999). The SRMR
values were acceptable for both models (≤ 0.09) (Hu and Bentler, 1999) even though the SRMR of the
first-order model was slightly above the recommended threshold of 0.09. In regards to the χ2 statistics of
148.796 at 98 degrees of freedom implying that χ2/df=1.518 for the first-order model and the χ2 statistics
of 150.756 at 100 degrees of freedom implying that χ2/df=1.508 for the second-order model were less
than the benchmark of 2.0 considered optimal by Koufteros and Marcoulides (2006). It can, thus, be
concluded that the items constituting the construct GSCM Practice Implementation are plausible (to a
great extent represent the same theoretical construct; scales are unidimensional to a great extent),
however, the models can be adjusted to more accurately fit the data.
Model Statistics First-Order Second-Order Recommended Value
χ2 148.796 150.756
df 98 100
χ2/df (cmin/df) 1.518 1.508 <2 good (Tabachink and Fidell, 2007 cited in
Hooper et al., 2008 and Koufteros and
Marcoulides, 2006); <5 sometimes permissible
(Wheaton et al. 1977)
p-value for the model 0.001 0.001 >0.05 (Barrett, 2007)
CFI 0.899 0.899 ≥ 0.95 great; >0.90 traditional; >0.08
sometimes permissible (Hair et al., 2010, p.
654)
>0.90 (Hu and Bentler, 1999)
SRMR 0.091 0.0824 ≤ 0.09 (Hu and Bentler, 1999)
RMSEA 0.0822 0.090 <0.08 good; 0.08-0.10 moderate; >0.10 bad
(MacCullum et al., 1996)
<0.07 (Steiger, 2007)
Table 19: Statistics of first- and second-order models (modified model)
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2. Performing Model Fit in the Confirmatory Factor Analysis
In the following both models will be adjusted to more accurately fit the obtained data. With the help of
the modification indices and the standardized residual covariance matrix provided by Amos output the
following decisions were made.
Adjustments made to the First-Order Model
To improve model fit the decision was made to delete items IEM3, GP3 and ECO5. Table 19 provides a
summary of the improved values for the goodness-of-fit indices.
Adjustments made to the Second-Order Model
To improve model fit of the second-order model Amos suggested deleting several items. The decision
was made to delete items GP3 and ECO5. This contributed to improving the overall model fitting. Table
19 provides a summary of the improved values for the goodness-of-fit indices.
Model Statistics First-Order Change Second-Order Change Recommended Value
χ2 75.683 93.361
df 59 73
χ2/df (cmin/df) 1.283 ↓ 1.279 ↓ <2 good (Tabachink and Fidell,
2007 cited in Hooper et al.,
2008 and Koufteros and
Marcoulides, 2006); <5
sometimes permissible
(Wheaton et al. 1977)
p-value for the
model
0.071 ↑ 0.054 ↑ >0.05 (Barrett, 2007)
CFI 0.957 ↑ 0.952 ↑ ≥ 0.95 great; >0.90 traditional;
>0.08 sometimes permissible
(Hair et al., 2010, p. 654)
>0.90 (Hu and Bentler, 1999)
SRMR 0.074 ↓ 0.078 ↓ ≤ 0.09 (Hu and Bentler, 1999)
RMSEA 0.068 ↓ 0.067 ↓ <0.08 good; 0.08-0.10
moderate; >0.10 bad
(MacCullum et al., 1996)
<0.07 (Steiger, 2007)
Table 20: Statistics of first- and second-order models after performing model fit (modified model)
3. Chi-Square Difference Test
Before making a decision on which model would be best to make use of it is necessary to statistically
compare the fit of the first-order model with the higher-order model. Marsh and Hocevar (1985)
recommend performing the likelihood ratio test also known as the chi-square difference test to evaluate
the efficacy of the two models. This method tests the null hypothesis of there being no significant
difference in fit by determining whether the chi-square difference is significant taking into account the
known degrees of freedom and the chosen significance level. The null hypothesis is rejected if the
difference is significant. To compute the chi-square difference test, the difference of the chi-square values
as well as the difference between the degrees of freedom of both models is taken.
𝜒𝑑𝑖𝑓𝑓2 = 𝜒𝑀1
2 − 𝜒𝑀22 𝜒𝑑𝑖𝑓𝑓
2 = 93.361-75.683= 17.678
𝑑𝑓𝑑𝑖𝑓𝑓 = 𝑑𝑓𝑀1 − 𝑑𝑓𝑀2 𝑑𝑓𝑑𝑖𝑓𝑓 = 73-59= 14
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M1 denotes the ‗smaller‘ model which in comparison to the ‗larger‘ model M2 has more degrees of
freedom (fewer parameters). The value for χdiff2 = 17.678 is distributed with dfdiff = 14 and checking the
significance by means of a χ2-table it can be concluded that the null hypothesis is not rejected. The results
show that the difference between the χ2 statistics for the first-and second-order models was 17.678 which
is smaller than 23.685 where the degree of freedom is 14 at p≤ 0.05. Thus, it can be concluded that there
is no statistically significant difference between the ‗smaller‘ model (the first-order model) and the
higher-order model. Furthermore, Beltrάn-Martίn et al. (2008) were able to conclude that the existing
covariation between the first-order factors and the observable variables can in its entirety be explained by
their regression onto the second-order factor. Thus, the decision was made to make use of the second-
order model to test the hypothesized relationships and to better conclude on the robustness of the Original
Model.
4. Validity and Reliability Analysis of Adjusted Constructs of the Second-Order Model
Convergent Validity
Standardized Factor Loadings and t-Values
From Table 20 it can be inferred that the standardized factor loadings of both adjusted constructs (Green
Purchasing and Eco-Design) are not optimal but better than before the adjustment was made. In regards to
the t-values it can be noted that all are significantly related to their underlying construct.
Average Variance Extracted
The average variance extracted (AVE) estimate of Green Purchasing decreased from 0.503 to 0.489 thus
dropping below the minimum threshold of 0.5 (Fornell and Larcker, 1981).
Factors Item
Number
Standardized
Loading
R2 Average
Variance
Extracted (AVE)
Discriminant
Validity
Construct/
Composite
Reliability
Critical Ratio
(t-value)
Internal environmental
management
IEM1 IEM2
IEM3
IEM4
0.874 0.962
0.704
0.692
0.764 0.925
0.496
0.479
0.666 0.816 0.890 _a 10.308
6.600
6.432
Green purchasing GP1
GP2
GP4
0.790
0.687
0.610
0.624
0.472
0.372
0.489 0.699 0.738 _a
3.658
3.571
Cooperation with customers
CC2 CC3
CC4
0.536 0.824
0.693
0.287 0.679
0.480
0.482 0.694 0.725 _a 3.172
3.434
Eco-design ECO1 ECO2
ECO3
ECO4
0.765 0.852
0.677
0.687
0.585 0.726
0.458
0.472
0.560 0.749 0.835 _a 6.058
5.073
5.145
Table 21: Summary of validity and reliability measurement results after performing model fit (modified model)
Notes: _a a parameter fixed at 1.0 in the measurement model.; all critical ratios (t-values), unless otherwise stated, are significant at p<0.001
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Reliability
Cronbach’s alpha
The cronbach‘s alpha values of the adjusted constructs are still greater than the suggested value of 0.7
(Nunnally and Bernstein, 1994, pp. 264–265 cited in Iacobucci and Duhachek, 2003).
Factors Number of
Items
Mean SD Cronbach’s
alpha
Range of corrected item-
to-total correlations
Internal Environmental
Management
4 11.83 3.22 0.883 0.674-0.863
Green Purchasing 3 8.43 2.212 0.732 0.513-0.605
Cooperation with
Customers
3 7.76 2.32 0.713 0.453-0.616
Eco-Design 4 11.38 2.785 0.832 0.618-0.734
Table 22: Summary of cronbach‘s alpha and item-to-total correlations measurement results after performing model fit (modified
model)
Figure 9 depicts the path diagram of the first-order model and Figure 10 depicts the second-order factor
measurement model for GSCM Practice Implementation. Latent constructs are shown as an oval. Each
measured variable is associated with an error term which, for simplicity, are not shown in the exhibits.
Two headed connections are a sign of covariance between constructs and one headed connectors reveal
there to be a path from a construct to an indicator variable (a measured variable). Measured variables are
labeled corresponding to those in the questionnaire.
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Path Diagram of the Measurement Model (First-Order-Model)
IEM
GP
CC
ECO
IEM4
IEM1
IEM2
0.49
0.78
0.91
0.53
0.83
0.75
0.76
0.60
0.71
0.70
0.88
0.95
GP4
GP1
GP2
0.37
0.65
0.45 0.61
0.81
0.67
CC4
CC2
CC3
0.42
0.44
0.53 0.65
0.67
0.73
ECO1
ECO2
ECO3
ECO4
0.56
0.71
0.48
0.50
0.75
0.84
0.69
0.71
Figure 9: Path diagram of the first-order measurement model (modified model)
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Path Diagram of the Measurement Model (Second-Order-Model)
IEM
GP
CC
ECO
GSCM
0.82
0.99
0.79
0.74
IEM1
IEM2
IEM3
IEM4
0.77
0.89
0.53
0.50
0.88
0.95
0.72
0.71
GP4
GP1
GP2
0.35
0.65
0.46 0.60
0.81
0.68
CC4
CC2
CC3
0.43
0.51
0.47 0.65
0.71
0.68
ECO1
ECO2
ECO3
ECO4
0.58
0.68
0.50
0.50
0.76
0.82
0.70
0.71
Figure 10: Path diagram of the second-order measurement model (modified model)
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Scale Mediators, Moderator and Dependent Concepts
To assess the construct validity of the mediators, moderator and dependent concepts the
unidimensionality of all seven constructs was determined (Steenkamp and van Trijp, 1991). This is a
necessary step to ensure that the indicator variables of a construct measure the same thing. The most
prominent method for testing unidimensionality is cronbach‘s alpha. Assessing reliability in terms of
cronbach‘s alpha has already been done previously (Sub-Section 5.5.2) thus the following will focus on a
second method – confirmatory factor analysis - to determine whether the model fit indices indicate a good
fit to the data.
Confirmatory Factor Analysis in Structural Equation Modeling
Here, the measurement models will be assessed separately from the structural model. For each model the
model fit indices were determined by making use of the statistical software Amos. Table 22 summarizes
the results obtained.
From the table it can be concluded that six SRMR‘s are less than 0.06 and one is only slightly above 0.06
thus the majority of constructs satisfy the cutoff point suggested by Hu and Bentler (1999). The CFI‘s
range from 0.925 to 1.000 implying that all constructs satisfy the cutoff point suggested by Hu and
Bentler (1999) which is at a minimum of 0.90. In terms of the χ2 statistic, even though almost all χ2/df
ratios of the constructs satisfied the benchmark (2.0) suggested by Koufteros and Marcoulides (2006)
Medsker et al. (1994) states that any χ2/df ratios which are below 10 can be regarded as indicating a good
fit with the data. In terms of the RMSEA the majority of values do not satisfy the upper limit of 0.07
suggested by Steiger (2007). The value for RMSEA tends to improve as more items are added and is said
to artificially inflate if df and N are low (Kenny et al., 2011 cited in Filippov et al., 2012). Thus, Kenny et
al. (2011) (cited in Filippov et al., 2012) argue to refrain from computing the RMSEA for low df models.
It should here be noted that from the table it can be inferred that the construct Market Pressure with zero
degrees of freedom is just-identified. Identification is defined as the degree to which there is a satisfactory
number of equations enabling the solving for every coefficient (unknown) which has to be estimated. The
model is just-identified when there are zero degrees of freedom and the number of equations is equal to
the number of estimated coefficients. As structural equation models are always over-identified it is
probable that the construct Market Pressure does not have enough items. Thus, it is highly likely that
when performing the moderator analysis no results will be obtained. (Kenny, 2011) The analysis will be
performed in Chapter 6, Section 6.2.3.
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Model 𝛘𝟐 df p 𝛘𝟐/𝐝𝐟 CFI SRMR RMSEA
GSCM Practice
Implementation First-Order
75.683 59 0.071 1.283 0.957 0.074 0.068
GSCM Practice
Implementation Second-
Order
93.361 73 0.054 1.279 0.952 0.078 0.067
Employee Job Satisfaction
Scale
0.998 2 0.607 0.499 1.000 0.0278 0.000
Operational Efficiency
Scale
8.578 2 0.014 4.289 0.925 0.0503 0.230
Relational Efficiency Scale 26.843 9 0.001 2.983 0.935 0.0474 0.179
Market Pressure Scale 0.000 0 - - 1.000 0.000 0.491
Overall Business
Performance Scale
0.945 2 0.624 0.472 1.000 0.0139 0.000
Environmental Performance
Scale
6.645 5 0.248 1.329 0.984 0.0436 0.073
Economic Performance
Scale
21.022 14 0.101 1.502 0.968 0.0606 0.090
Table 23: Fit indices for the mediators, moderator and dependent concepts (modified model)
Figure 11 depicts the path diagrams of the measurement models for Employee Job Satisfaction,
Operational Efficiency, Relational Efficiency, Market Pressure and the three dependent concepts (Overall
Business Performance, Environmental Performance and Economic Performance). Latent constructs are
shown as an oval. Each measured variable is associated with an error term which, for simplicity, are not
shown in the exhibits. Two headed connections are a sign of covariance between constructs and one
headed connectors reveal there to be a path from a construct to an indicator variable (a measured
variable). Measured variables are labeled corresponding to those in the questionnaire.
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Path Diagrams of the Measurement Models
SAT
0.62
0.65
0.70
0.82
0.57
0.69
RE1
RE2
RE3
RE4
RE5
RE6
0.81
0.84
0.90
0.76
0.79
0.83
RE MP1
MP2
0.79
0.29 0.54
0.89
OBP1
OBP2
OBP3
OBP4
0.58
0.53
0.76
0.65
0.76
0.79
0.87
0.81
EP OBP
MP
0.43
0.42
0.56
0.81
0.48
ECP3
ECP4
ECP5
ECP6
ECP7
ECP
0.65
0.65
0.75
0.90
0.69
0.46
0.66
ECP8
ECP9
0.68
0.81
SAT1
SAT2
SAT3
SAT5
0.74
0.67
0.30
0.24
0.86
0.82
0.55
0.49
OE1
OE2
OE4
OE6
0.46
0.59
0.61
0.51
0.68
0.77
0.78
0.72
OE
EP1
EP2
EP3
EP4
EP6
0.47
0.45
0.58
0.58
0.41
0.67
0.76
0.76
0.64
0.69
Figure 11: Path diagrams of measurement models (modified model)
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6. HYPOTHESES TESTING AND DISCUSSIONS OF QUANTITATIVE DATA
Hereunder, the hypotheses developed in Chapter 3 will be tested by means of path analysis. More
specifically, this chapter is divided into three sections. First, the hypotheses will be tested by making use
of the original model without adjustments after which the hypotheses will be tested by utilizing the
modified model to determine the robustness of the results obtained. The robustness verification will be
performed in the last section of this chapter. The first two sections are divided into three subsections,
namely: an analysis of the direct effects, a mediation analysis and a moderation analysis. Each of the first
two sections will conclude with a summarizing table and a conceptual model of the hypotheses, their
unstandardized coefficient (b-value) and if a statistically significant relationship was found. It should here
be noted that due to the low response rate (10.71%) making generalizations from the sample to the
population is not advisable. Thus, the conclusions drawn in the following are made not taking into
account the low response rate.
6.1 Original Model
The results of the original structural model are summarized in Table 26 and Figure 12. This section is
divided into three subsections, namely: direct effects, mediation analysis and moderation analysis.
6.1.1 Direct Effects
In regards to the direct effects, hypotheses H1a to H4d, it can be noted that all hypotheses were supported
except H3a (b=0.291, t=1.771, p=0.077). No direct link between GSCM Practice Implementation and
Operational Efficiency could be found. However, the remaining paths from GSCM Practice
Implementation to the following showed positive significant results:
(1) Employee Job Satisfaction (b=0.493, t=2.671, p=0.008)
(2) Relational Efficiency (b=0.390, t=2.361, p=0.018)
As posited by hypotheses H3b, H3c and H3d, Operational Efficiency has a direct effect on all three
dependent concepts. Furthermore, the test results also revealed that an improved Operational Efficiency in
the supplying firm has a positive impact on the Relational Efficiency between the supplier and the buying
firm (H3e: b=0.818, t=4.347, p<0.001). As a last note it was found that there is a positive, significant
relationship between Relational Efficiency and Overall Business Performance (H4b: b=0.535, t=3.700,
p<0.001), Environmental Performance (H4c: b=0.458, t=3.003, p=0.003) and Economic Performance
(H4d: b=0.316, t=2.016, p=0.044).
Comparison to Results found by Lee et al. (2012)
When comparing the test results found in this study to the study performed by Lee et al. (2012) (Table 23)
the most anticipated finding for there to be a direct relationship between GSCM Practice Implementation
and Overall Business Performance was supported, however, weakly. Furthermore, the stronger indirect
effect between GSCM Practice Implementation and Overall Business Performance, which was expected,
could not be proven to exist when having evaluated the test results. Additionally, even though the
relationship between GSCM Practice Implementation and Employee Job Satisfaction is supported by both
studies this study did not find there to be a stronger effect (b=0.493, t=2.671, p=0.008 compared to
b=0.720, t=15.353, p<0.01). However, in contrast to the study performed by Lee et al. (2012) the
hypothesis stating there to be a relationship between Employee Job Satisfaction and Overall Business
Master Thesis 2013 Supply Chain Management-Taking an Environmental Perspective Michelle Engert 329909
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Performance was supported. The hypothesized effect of GSCM Practice Implementation on Operational
Performance could not be supported by this study (H3a: b=0.291, t=1.771, p=0.077).
Current Study Lee et al. (2012)
Path (from-to) Effects (Critical
Ratio)
Hypotheses
Test Results
Effects (Critical
Ratio)
Hypotheses
Test Results
H1 H1a:
GSCM ImplementationOverall
Business Performance (direct)
0.324 (1.989) Supported
p-value=0.047;
R2=0.11
0.084 (0.782) Not supported
H2 H2a: GSCM ImplementationEmployee
Job Satisfaction
0.493 (2.671) Supported
p-value=0.008;
R2=0.24
0.720 (15.353) Supported
p-value<0.01
H2b:
Employee Job SatisfactionOverall
Business Performance
0.459 (3.097)
Supported
p-value=0.002;
R2=0.21
0.161 (1.877) Not supported
H2c:
Employee Job
SatisfactionOperational
Efficiency
0.358 (2.281) Supported
p-value=0.023;
R2=0.13
0.024 (0.204) Not supported
H3 H3a:
GSCM
ImplementationOperational
Efficiency
0.291 (1.771) Not supported
p-value=0.077;
R2=0.08
0.444 (3.688) Supported
p-value<0.01
H3b:
Operational EfficiencyOverall
Business Performance
0.468 (2.979) Supported
p-value=0.003;
R2=0.22
0.423 (6.578) Supported
p-value<0.01
H3e:
Operational EfficiencyRelational
Efficiency
0.818 (4.347) Supported
p-value<0.001;
R2=0.67
0.447 (7.886) Supported
p-value<0.01
H4 H4a:
GSCM ImplementationRelational
Efficiency
0.390 (2.361) Supported
p-value=0.018;
R2=0.15
0.410 (6.858) Supported
p-value<0.01
H4b:
Relational EfficiencyOverall
Business Performance
0.535 (3.700) Supported
p-value<0.001;
R2=0.29
0.233 (3.022) Supported
p-value<0.01
H6 H6a: GSCM ImplementationOverall
Business Performance (indirect)
0.036 (0.813) Supported 0.455 (5.407) Supported
p-value<0.01
Table 24: Summary of hypotheses test results and comparison to results found by Lee et al. (2012)
6.1.2 Mediation Analysis
To examine the hypothesized mediating effects between GSCM Practice Implementation and the
dependent concepts: Overall Business Performance, Environmental Performance and Economic
Performance the widely known Baron and Kenny (1986) framework for mediation analysis has been
made use of. Furthermore, mediation tests by means of bootstrapping (number of bootstrap samples:
2000; bc confidence level: 95) have been performed to confirm or reject a relationship found by means of
the Baron and Kenny (1986) approach. To perform the analysis the statistical software Amos has been
made use of. Table 24 provides a summary of the results found.
From the previous analysis it was concluded that GSCM Practice Implementation is directly linked to all
three dependent concepts. The relationships were found to be significant. Furthermore, GSCM Practice
Implementation was found to be positively and significantly correlated with two mediators, namely:
Employee Job Satisfaction and Relational Efficiency. In turn, all three mediators (Employee Job
Satisfaction, Operational Efficiency and Relational Efficiency) were found to be positively and
significantly correlated with all three dependent concepts.
Master Thesis 2013 Supply Chain Management-Taking an Environmental Perspective Michelle Engert 329909
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In regards to H6a proposing the relationship between GSCM Practice Implementation and Overall
Business Performance to be mediated by Employee Job Satisfaction, Operational Efficiency and
Relational Efficiency it can be said that this hypothesis is supported. Having determined the direct effect
without the mediator and the effect with the mediator it could be concluded that there has been a drop in
strength from b=0.324 to b=0.036 and when including the mediators the path dropped out of significance
implying, according to the Baron and Kenny (1986) approach, that full mediation exists. It should here be
noted that according to Judd and Kenny (1981a, 1981b) full mediation exists if the effect of the
independent variable on the dependent variable is zero when the mediator is included. However, this is a
very rare case, thus, one can here also speak of full mediation. Having calculated the indirect effect by
means of bootstrapping it can be concluded that this analysis confirms there to be a mediating effect to
exist. The existence of this effect is quite intuitive considering the fact that the relationship between
GSCM Practice Implementation and Overall Business Performance was found to be very weak.
H6b, proposing the relationship between GSCM Practice Implementation and Environmental
Performance to be mediated by Operational Efficiency and Relational Efficiency is not supported.
According to the Baron and Kenny (1986) approach the path is partially mediated as there has been a drop
in strength when including the mediator and the path is still significant. However, when having a look at
the indirect effect a non-significant relationship was found implying there to be no mediation which
contradicts the results found when making use of the Baron and Kenny (1986) approach.
H6c, proposing the relationship between GSCM Practice Implementation and Economic Performance to
be mediated by Operational Efficiency and Relational Efficiency is also not supported. The path is
partially mediated as the path is still significant when including the mediator. However, the calculated
indirect effect reveals there to be a non-significant relationship which contradicts the results found when
making use of the Baron and Kenny (1986) approach.
Direct
without
Mediator
(p-value)
Direct with
Mediator
(p-value)
Indirect Hypotheses
Test Results
H6a: GSCM Practice ImplementationEmployee
Job Satisfaction, Operational Efficiency ,
Relational Efficiency Overall Business
Performance
0.324
(0.047)
0.036 (0.813) Two-tailed
significance
0.022mediation
Supported
Additional Analysis
GSCM Practice ImplementationEmployee
Job SatisfactionOverall Business
Performance
0.324
(0.047)
0.049 (0.748) Two-tailed
significance
0.209no
mediation
GSCM Practice ImplementationOperational
EfficiencyOverall Business Performance
0.324
(0.047)
0.053 (0.699) Two-tailed
significance
0.469no
mediation
GSCM Practice ImplementationRelational
EfficiencyOverall Business Performance
0.324
(0.047)
0.042 (0.766) Two-tailed
significance
0.073no
mediation
H6b: GSCM Practice Implementation Operational
Efficiency, Relational
EfficiencyEnvironmental Performance
0.590
(0.005)
0.481 (0.012) Two-tailed
significance
0.116no
mediation
Not Supported
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Additional Analysis
GSCM Practice Implementation Operational
Efficiency Environmental Performance
0.590
(0.005)
0.496 (0.010) Two-tailed
significance
0.040mediation
GSCM Practice ImplementationRelational
EfficiencyEnvironmental Performance
0.590
(0.005)
0.501 (0.012) Two-tailed
significance
0.253no
mediation
H6c: GSCM Practice Implementation Operational
Efficiency, Relational EfficiencyEconomic
Performance
0.818
(0.007)
0.828 (0.007) Two-tailed
significance
0.872no
mediation
Not Supported
Additional Analysis
GSCM Practice ImplementationOperational
EfficiencyEconomic Performance
0.818
(0.007)
0.772 (0.007) Two-tailed
significance
0.077no
mediation
GSCM Practice ImplementationRelational
EfficiencyEconomic Performance
0.818
(0.007)
0.859 (0.008) Two-tailed
significance
0.065no
mediation
Table 25: Summary of mediation analysis results (original model)
6.1.3 Moderation Analysis
Having made use of the statistical software SPSS the two items for the moderator Market Pressure MP1
and MP2 have been combined and the median was calculated (equals 6) in order to recode the resulting
values into different variables, namely 0 (MP_Low) and 1 (MP_High). Having made use of the statistical
software Amos, the regression weights tables for both groups (MP_High and MP_Low) were obtained
and with the help of the Stats Tool Package developed by Gaskin (2012c) Table 25 was obtained. From
the table it can be concluded that not one of the three hypotheses proved to be significant. There is no
significant difference between the values obtained for MP_High and MP_Low. However, it should be
noted that this can very likely be attributable to the rather low number of respondents and the fact that
only two items measure this construct. It can, thus, be concluded that there is potential for further
investigation and further refinement/ extension of the number of measurement items measuring the
moderator Market Pressure.
MP_High MP_Low
Estimate P Estimate P z-score
OBPGSCM 0.829 0.013 1.032 0.412 0.156
EPGSCM 0.567 0.020 2.603 0.212 0.971
ECPGSCM 0.904 0.011 2.064 0.245 0.641
Table 26: Summary of moderation analysis results (original model)
Notes: ** p-value < 0.01; * p-value < 0.05
Path (from-to) Mediator Moderator Direct Effects
(Critical Ratio)
Hypotheses Test Results
H1 H1a:
GSCM ImplementationOverall Business Performance (direct) 0.324 (1.989) Supported
p-value=0.047; R2=0.11
H1b:
GSCM ImplementationEnvironmental Performance (direct) 0.590 (2.801) Supported
p-value=0.005; R2=0.35
H1c:
GSCM ImplementationEconomic Performance (direct) 0.818 (2.707) Supported p-value=0.007; R2=0.67
H2 H2a: GSCM ImplementationEmployee Job Satisfaction 0.493 (2.671) Supported
p-value=0.008; R2=0.24
H2b:
Employee Job SatisfactionOverall Business Performance 0.459 (3.097)
Supported p-value=0.002; R2=0.21
H2c:
Employee Job SatisfactionOperational Efficiency 0.358 (2.281) Supported
p-value=0.023; R2=0.13
H3 H3a:
GSCM ImplementationOperational Efficiency 0.291 (1.771) Not supported
p-value=0.077; R2=0.08
H3b:
Operational EfficiencyOverall Business Performance 0.468 (2.979) Supported p-value=0.003; R2=0.22
H3c:
Operational EfficiencyEnvironmental Performance 0.377 (2.471) Supported
p-value=0.013; R2=0.16
H3d: Operational EfficiencyEconomic Performance 0.347 (2.026) Supported
p-value=0.043; R2=0.12
H3e:
Operational EfficiencyRelational Efficiency 0.818 (4.347) Supported p-value<0.001; R2=0.67
H4 H4a:
GSCM ImplementationRelational Efficiency 0.390 (2.361) Supported
p-value: 0.018; R2=0.15
H4b:
Relational EfficiencyOverall Business Performance 0.535 (3.700) Supported
p-value<0.001; R2=0.29
H4c:
Relational EfficiencyEnvironmental Performance 0.458 (3.003) Supported p-value=0.003; R2=0.21
H4d:
Relational EfficiencyEconomic Performance 0.316 (2.016) Supported
p-value=0.044; R2=0.10
H5 H5a: GSCM practice implementationOverall Business Performance High Market Pressure
Low Market Pressure
Not supported
H5b: GSCM practice implementationEnvironmental Performance High Market Pressure
Low Market Pressure
Not supported
H5c: GSCM practice implementationEconomic Performance High Market Pressure
Low Market Pressure
Not supported
H6 H6a: GSCM ImplementationOverall Business Performance Employee Job Satisfaction, Operational
Efficiency and Relational Efficiency
Supported
H6b: GSCM ImplementationEnvironmental Performance
Operational Efficiency and Relational Efficiency
Not Supported
H6c: GSCM ImplementationEconomic Performance
Operational Efficiency and Relational
Efficiency
Not Supported
Table 27: Results of path analysis and hypotheses tests (original model)
Conceptual Model (Original Model)
Independent Concept Mediators and Moderator Dependent Concepts
GSCM
Implementation
Overall Business Performance
Environmental Performance
Economic Performance
Employee Job
Satisfaction
Operational
Efficiency
Relational
Efficiency
Market
Pressure
H2a
0.493**
H4a
0.390*
H3a
0.291
H3e
0.818**
H2c
0.358*
H2b
0.459**
H4b, H4c, H4d
0.535*, 0.458**, 0.316**
H5a, H5b, H5c
Not supported
H1a, H1b, H1c
0.324*, 0.590**, 0.818**
H3b, H3c, H3d
0.468**, 0.377*, 0.347*
Figure 12: Hypothesized structural model results (original model)
Notes: ** p-value < 0.01; * p-value < 0.05
Master Thesis 2013 Supply Chain Management-Taking an Environmental Perspective Michelle Engert 329909
6.2 Modified Model
The results of the modified structural model are summarized in Table 29 and Figure 13. This section is
divided into three subsections, namely: direct effects, mediation analysis and moderation analysis.
6.2.1 Direct Effects
In regards to the direct effects, hypotheses H1a to H4d, it can be noted that all hypotheses were supported
except H2c (b=0.253, t=1.634, p=0.102) and H3a (b=0.291, t=1.771, p=0.077). No direct link between
Employee Job Satisfaction and Operational Efficiency as well as no direct link between GSCM Practice
Implementation and Operational Efficiency could be found. However, the remaining paths from GSCM
Practice Implementation to the following showed positive significant results:
(1) Employee Job Satisfaction (b=0.495, t=3.241, p=0.001)
Note: the strength of the relationship and the significance increased compared to the original
model with no adjustment.
(2) Relational Efficiency (b=0.395, t=2.733, p=0.006)
Note: the strength of the relationship and the significance increased compared to the original
model with no adjustment.
As for H2c it can be concluded that, as opposed to the results found when utilizing the original model,
increased Employee Job Satisfaction does not lead to an increase in Operational Efficiency. Furthermore,
as posited by hypotheses H3b, H3c and H3d, Operational Efficiency has a direct effect on all three
dependent concepts (H3b: b=0.367, t: 2.368, p=0.018; H3c: b=0.371, t=2.265, p=0.024; H3d: b=0.352,
t=2.240, p=0.025). Furthermore, the test results also revealed, as did those making use of the original
model, that an improved Operational Efficiency in the supplying firm has a positive impact on the
Relational Efficiency between the supplier and the buying firm (b=0.744, t=4.106, p<0.001). The effect
is, however, not as strong as it was when having made use of the unadjusted model.
6.2.2 Mediation Analysis
To examine the hypothesized mediating effects between GSCM Practice Implementation and the
dependent concepts: Overall Business Performance, Environmental Performance and Economic
Performance the widely known Baron and Kenny (1986) framework for mediation analysis has been
made use of. Furthermore, mediation tests by means of bootstrapping (number of bootstrap samples:
2000; bc confidence level: 95) have been performed to confirm or reject a relationship found by means of
the Baron and Kenny (1986) approach. To perform the analysis the statistical software Amos has been
made use of. Table 27 provides a summary of the results found.
From the previous analysis it was concluded that GSCM Practice Implementation is directly linked to all
three dependent concepts. The relationships were found to be significant. Furthermore, GSCM Practice
Implementation was found to be positively correlated with two mediators, namely: Employee Job
Satisfaction and Relational Efficiency. In turn, all three mediators (Employee Job Satisfaction,
Operational Efficiency and Relational Efficiency) were found to be positively correlated with all three
dependent concepts.
In regards to H6a proposing the relationship between GSCM Practice Implementation and Overall
Business Performance to be mediated by Employee Job Satisfaction, Operational Efficiency and
Relational Efficiency it can be said that this hypothesis is supported. Having determined the direct effect
without the mediator and the effect with the mediator it could be concluded that there has been a drop in
strength from b=0.333 to b=0.031 and when including the mediators the path dropped out of significance
Master Thesis 2013 Supply Chain Management-Taking an Environmental Perspective Michelle Engert 329909
83
implying, according to the Baron and Kenny (1986) approach, that full mediation exists. It should here be
noted that according to Judd and Kenny (1981a, 1981b) full mediation exists if the effect of the
independent variable on the dependent variable is zero when the mediator is included. However, this is a
very rare case, thus, one can here also speak of full mediation. Having calculated the indirect effect by
means of bootstrapping it can be concluded that this analysis confirms there to be a mediating effect to
exist. The existence of this effect is quite intuitive considering the fact that the relationship between
GSCM Practice Implementation and Overall Business Performance was found to be weak.
H6b, proposing the relationship between GSCM Practice Implementation and Environmental
Performance to be mediated by Operational Efficiency and Relational Efficiency is not supported.
According to the Baron and Kenny (1986) approach the path is partially mediated as there has been a drop
in strength when including the mediator and the path is still significant. However, when having a look at
the indirect effect a non-significant relationship was found implying there to be no mediation which
contradicts the results found when making use of the Baron and Kenny (1986) approach.
H6c, proposing the relationship between GSCM Practice Implementation and Economic Performance to
be mediated by Operational Efficiency and Relational Efficiency is also not supported. The path is
partially mediated as the path is still significant when including the mediator. However, the calculated
indirect effect reveals there to be a non-significant relationship which contradicts the results found when
making use of the Baron and Kenny (1986) approach.
Direct
without
Mediator
Direct with
Mediator
Indirect Hypotheses
Test Results
H6a: GSCM Practice
ImplementationEmployee Job
Satisfaction, Operational Efficiency ,
Relational Efficiency Overall
Business Performance
0.333 (0.025) 0.031 (0.841) Two-tailed
significance
0.006mediation
Supported
Additional Analysis
GSCM Practice
ImplementationEmployee Job
SatisfactionOverall Business
Performance
0.333 (0.025) 0.150 (0.350) Two-tailed
significance
0.015mediation
GSCM Practice
ImplementationOperational
EfficiencyOverall Business
Performance
0.333 (0.025) 0.246 (0.095) Two-tailed
significance
0.018mediation
GSCM Practice
ImplementationRelational
EfficiencyOverall Business
Performance
0.333 (0.025) 0.139 (0.322) Two-tailed
significance
0.001mediation
H6b: GSCM Practice Implementation
Operational Efficiency, Relational
EfficiencyEnvironmental
Performance
0.576 (0.001)
0.477 (0.004) Two-tailed
significance
0.108no
mediation
Not Supported
Additional Analysis
GSCM Practice Implementation
Operational Efficiency
Environmental Performance
0.576 (0.001)
0.508 (0.002) Two-tailed
significance
0.044mediation
GSCM Practice
ImplementationRelational
EfficiencyEnvironmental
Performance
0.576 (0.001)
0.476 (0.004) Two-tailed
significance
0.034mediation
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H6c: GSCM Practice Implementation
Operational Efficiency, Relational
EfficiencyEconomic Performance
0.845 (0.001) 0.821 (0.001) Two-tailed
significance
0.973no
mediation
Not Supported
Additional Analysis
GSCM Practice
ImplementationOperational
EfficiencyEconomic Performance
0.845 (0.001) 0.812 (0.001) Two-tailed
significance
0.125no
mediation
GSCM Practice
ImplementationRelational
EfficiencyEconomic Performance
0.845 (0.001) 0.847 (0.001) Two-tailed
significance
0.691no
mediation
Table 28: Summary of mediation analysis results (modified model)
6.2.3 Moderation Analysis
Having made use of the statistical software SPSS the two items for the moderator Market Pressure MP1
and MP2 have been combined and the median was calculated in order to recode the resulting values into
different variables, namely 0 (MP_Low) and 1 (MP_High). Having made use of the statistical software
Amos, the regression weights tables for both groups (MP_High and MP_Low) were obtained and with the
help of the Stats Tool Package developed by Gaskin (2012c) Table 28 was obtained. From the table it can
be concluded that not one of the three hypotheses proved to be significant. There is no significant
difference between the values obtained for MP_High and MP_Low. However, it should be noted that this
can very likely be attributable to the rather low number of respondents and the fact that only two items
measure this construct. It can be, thus, be concluded that there is potential for further investigation and
further refinement/ extension of the number of measurement items measuring the moderator Market
Pressure.
MP_High MP_Low
Estimate P Estimate P z-score
OBPGSCM 0.172 0.409 -0.095 0.809 -0.599
EPGSCM 0.265 0.121 0.598 0.082 0.867
ECPGSCM 0.695 0.001 1.080 0.019 0.761
Table 29: Summary of moderation analysis results (modified model)
Notes: ** p-value < 0.01; * p-value < 0.05
Path (from-to) Mediator Moderator Direct Effects
(Critical Ratio)
Hypotheses Test
Results
H1 H1a:
GSCM ImplementationOverall Business Performance (direct) 0.333 (2.238) Supported
p-value=0.025; R2=0.11
H1b:
GSCM ImplementationEnvironmental Performance (direct) 0.576 (3.414) Supported p-value=0.001; R2=0.33
H1c:
GSCM ImplementationEconomic Performance (direct) 0.845 (4.567) Supported
p-value=0.001; R2=0.71
H2 H2a: GSCM ImplementationEmployee Job Satisfaction 0.495 (3.241) Supported
p-value=0.001; R2=0.25
H2b:
Employee Job SatisfactionOverall Business Performance 0.460 (3.106) Supported
p-value=0.002; R2=0.21
H2c:
Employee Job SatisfactionOperational Efficiency 0.253 (1.634) Not Supported
p-value=0.102; R2=0.06
H3 H3a:
GSCM ImplementationOperational Efficiency 0.299 (1.921) Not supported
p-value=0.055; R2=0.00
H3b:
Operational EfficiencyOverall Business Performance 0.367 (2.368) Supported p-value=0.018; R2=0.13
H3c:
Operational EfficiencyEnvironmental Performance 0.371 (2.265) Supported
p-value=0.024; R2=0.14
H3d: Operational EfficiencyEconomic Performance 0.352 (2.240) Supported
p-value=0.025; R2=0.12
H3e:
Operational EfficiencyRelational Efficiency 0.744 (4.106) Supported p-value<0.001; R2=0.55
H4 H4a:
GSCM ImplementationRelational Efficiency 0.395 (2.735) Supported
p-value: 0.006; R2=0.16
H4b:
Relational EfficiencyOverall Business Performance 0.535 (3.700) Supported p-value<0.001; R2=0.29
H4c:
Relational EfficiencyEnvironmental Performance 0.419 (2.774) Supported
p-value=0.006; R2=0.18
H4d:
Relational EfficiencyEconomic Performance 0.313 (2.196) Supported
p-value=0.028; R2=0.10
H5 H5a: GSCM practice implementationOverall Business Performance High Market Pressure Low Market Pressure
Not supported
H5b: GSCM practice implementationEnvironmental Performance High Market Pressure
Low Market Pressure
Not supported
H5c: GSCM practice implementationEconomic Performance High Market Pressure
Low Market Pressure
Not supported
H6 H6a: GSCM ImplementationOverall Business Performance Employee Job Satisfaction, Operational Efficiency and Relational Efficiency
Supported
H6b: GSCM ImplementationEnvironmental Performance
Operational Efficiency and Relational
Efficiency
Not Supported
H6c: GSCM ImplementationEconomic Performance
Operational Efficiency and Relational
Efficiency
Not Supported
Table 30: Results of path analysis and hypotheses tests (modified model)
Conceptual Model (Modified Model)
Independent Concept Mediators and Moderator Dependent Concepts
GSCM
Implementation
Overall Business Performance
Environmental Performance
Economic Performance
Employee Job
Satisfaction
Operational
Efficiency
Relational
Efficiency
Market
Pressure
H2a
0.495**
H4a
0.395**
H3a
0.299
H3e
0.744**
H2c
0.253
H2b
0.460**
H4b, H4c, H4d
0.535**, 0.419**, 0.313*
H5a, H5b, H5c
Not supported
H1a, H1b, H1c
0.333*, 0.576**, 0.845**
H3b, H3c, H3d
0.367*, 0.371*, 0.352*
Figure 13: Hypothesized structural model results (modified model)
Notes: ** p-value < 0.01; * p-value < 0.05
Master Thesis 2013 Supply Chain Management-Taking an Environmental Perspective Michelle Engert 329909
6.3 Robustness of the Original Model
Robustness can be defined as a model‘s, test‘s or system‘s ability to operate without failure and
effectively perform even if the variables or assumptions are altered (Pluemper and Neumayer, 2012). To
determine robustness the following will compare the individual hypotheses tests of the original model and
the modified model to draw conclusions on the robustness of the original model.
When comparing Table 26 to Table 29 the most noticeable difference is that H2c, stating there to be a
positive relationship between Employee Job Satisfaction and Operational Efficiency, has changed from
being supported to not being supported. The p-value has experiences a dramatic increase from p=0.023 to
p=0.102 indicating that the hypothesis is after model adjustment strongly not supported. As for the
remaining hypotheses it can be noted that their hypotheses test result did not change. However, when
comparing the tables it can be inferred that the hypotheses stating there to be a positive relationship
between GSCM Practice Implementation and the three dependent variables are more strongly,
significantly supported when making use of the modified model. The same holds true for the relationship
between GSCM Practice Implementation and the mediators Employee Job Satisfaction and Relational
Efficiency. In terms of the mediator Operational Efficiency it can be said that there is still no support for
the existence of a positive relationship between GSCM Practice Implementation and Operational
Efficiency even though the p-value experiences a decrease from p=0.077 to p=0.055.
Concluding the hypotheses comparison it can be noted that due to the rather slight changes in the path
coefficients and their respective p-values it can be inferred that all hypotheses with the exception of H2c
can be considered to be rather robust when making use of the original model.
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88
7. SUMMARY AND IMPLICATIONS
The final chapter of this thesis will provide a summary of the most important findings. Furthermore, a
critical assessment of this study‘s limitations will be provided as well as recommendations for future
research. Last but not least this chapter, more specifically this thesis, will be rounded off with a
concluding summary.
7.1 Main Findings and Managerial Implications
This study which has been conducted from the supplier‘s point of view focusing on small- and medium-
sized suppliers in the automotive industry in Germany aimed at investigating whether it is reasonable to
assume that German enterprises are indeed operating in a more mature industry in terms of GSCM
Practice Implementation. More explicitly, this study‘s main intention was to determine if German
enterprises are less pressured by their buying firms and thus experience an improvement in Overall
Business Performance as well as Employee Job Satisfaction. Unfortunately, the analysis revealed that the
moderator Market Pressure ought to have been measured by more than two items and it was thus not
possible to draw conclusions in regards to the existence or non-existence of a moderating effect.
However, the most anticipated finding of there being a significant, direct relationship between GSCM
Practice Implementation and Overall Business Performance was supported. Furthermore, this study also
made a distinction between Environmental and Economic Performance and found supporting evidence for
the existence of a significant, direct relationship between GSCM Practice Implementation and
Environmental and Economic Performance.
This research makes three major managerial contributions to existing literature which will be elaborated
on in the following.
GSCM Practice Implementation, Employee Job Satisfaction and Overall Business Performance
Firstly, not only was a relationship found between GSCM Practice Implementation and Employee Job
Satisfaction but in contrast to the study performed by Lee et al. (2012) this study also managed to find a
relationship between Employee Job Satisfaction and Overall Business Performance. Even though the
indirect method for testing mediation does not provide supporting evidence for Employee Job Satisfaction
to mediate the relationship between GSCM Practice Implementation and Overall Business Performance
the Baron and Kenny (1986) approach did identify Employee Job Satisfaction to be a mediator. It can thus
be concluded that managers who implement GSCM practices achieve an increase in Employee Job
Satisfaction which positively impacts the firms‘ Operational Efficiency and Overall Business
Performance.
GSCM Practice Implementation and Business Performance (direct)
As a second point it is worthwhile to mention that in contrast to the study performed by Lee et al. (2012)
and supporting the studies performed by Chien and Shih (2007) as well as Zhu and Sarkis (2004) this
study managed to find supporting evidence for there to be a positive, significant relationship not only
between GSM Practice Implementation and Overall Business Performance but also between GSCM
Practice Implementation and Environmental and Economic Performance. In consideration of the rather
strong relationship between GSCM Practice Implementation and Environmental and Economic
Performance managers are advised to not underestimate cost savings and performance gains arising from
implementing green supply chain initiatives. The rather weak relationship between GSCM Practice
Implementation and Overall Business Performance can possibly be attributed to the rather broadly
Master Thesis 2013 Supply Chain Management-Taking an Environmental Perspective Michelle Engert 329909
89
defined measurement items and the fact that the relationship has been found to be mediated to a great
extent by Employee Job Satisfaction, Operational Efficiency and Relational Efficiency.
GSCM Practice Implementation, Relational Efficiency and Business Performance
Thirdly, this study has made one of the first attempts (to the researcher‘s knowledge) to tap into the
domain of Relational Efficiency and Business Performance. Relational Efficiency was found to be
impacted by Operational Efficiency and by the degree of GSCM Practice Implementation.
Furthermore, the study results reveal there to be a positive, significant relationship between Relational
Efficiency and Overall Business Performance, Environmental Performance and Economic Performance. It
can thus be concluded that the implementation of GSCM practices helps a supplying firm to improve its
Relational Efficiency with its buying firms. This ability of a supplying firm to build trust and credibility
in the relationship with the buying firm by means of collaboration and information sharing will eventually
have a positive effect on Business Performance. More specifically, the increased transparency and
openness in business processes has a strong impact on Overall Business Performance and Environmental
Performance and a weak but still significant impact on Economic Performance. This is intuitively
understandable as an increased collaboration between supply chain partners will inevitably facilitate the
optimization of entire supply chain activities and thus result in an overall improvement of the supplying
firm‘s Environmental Performance. This improvement incorporates a decrease in air emissions, a
reduction of solid wastes and for instance a decrease in the consumption of hazardous/harmful/toxic
materials.
The existence of a relationship between Relational Efficiency and Environmental and Economic
Performance provides new insights for managers who wish to increase their performance gains by means
of increased collaboration and trust with their supply chain partners. This study revealed that performance
gains are not only to be expected in regards to asset utilization and competitive position but also in terms
of decreases for waste discharge and a reduction in water usage as well as waste disposal.
Concluding this section, it can be said that this study provides enormous potential for future research
especially in regards to investigating whether a moderating effect exists between GSCM Practice
Implementation and Business Performance. To what degree does market pressure, when differentiating
between companies that experience more pressure and ones that experience less pressure, have an impact
on the Overall, Environmental and Economic Performance? However, even though conclusions on the
existence or non-existence of a moderating effect could not be drawn the results of this study suggest a
number of interesting insights. It was found that even though German enterprises are operating in a rather
mature environment in regards to green supply chain initiatives in comparison to companies located in
Korea there is still enormous potential for increasing operations‘/ supply chain managers‘ awareness of
differing Environmental Management Standards. Furthermore, it was found that GSCM Practice
Implementation is directly related to firm performance. Not only do firms experience a slight
improvement in their Overall Business Performance but the implementation of green practices also,
strongly, increases their Environmental and Economic Performance. It was also found that GSCM
Practice Implementation helps improve the Relational Efficiency with their buying firms, which leads to
enhanced business performance. Lastly, it ought to be mentioned that having achieved an improvement in
Employee Job Satisfaction, Operational Efficiency or Relational Efficiency the German supplying firms
would experience a stronger increase in Overall Business Performance than would Korean firms.
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7.2 Limitations and Future Research Directions
This study examined the relationship between GSCM Practice Implementation and Business Performance
taking a Resource Dependence and Institutional Theory perspective. In the following the findings of this
study will be critically evaluated in terms of limitations in the methodological approach. Additionally,
directions for future research will be outlined.
The first major limitation of this study is the low response rate. 63 responses were received from small-
and medium-sized German automobile suppliers which corresponds with a response rate of 10.71%
(=63/588). Thus, it can be concluded that when comparing the sample (N=588) to all responses (N=63) it
is probable that the total responses are not representative for the population implying non-response bias.
In consequence, making generalizations from the sample to the population is not possible/ advisable.
Thus, case study research (comparative case study) is encouraged to verify the findings. Even though
conclusions cannot and should not be drawn, the low response rate was not taken into consideration when
evaluating the test results. Furthermore, it should be noted that to achieve adequate power in structural
equation modeling Hair et al. (1995) (cited in Williams and Brown, 2012) recommend a minimum sample
size of one hundred. Even though maximum likelihood estimation (MLE) has been made use of which
has been found to present valid results for sample sizes as small as 50 observations it is not advisable to
use such a small sample size. According to Hair et al. (2006) (cited in Karim et al., 1989), optimally,
structural equation modeling is performed with a sample size of 100 to 400. 200 being the most
recommended sample size (Hair et al., 1998 cited in Goldman et al., 2007; Tabachnick and Fidell, 1996
cited in Goldman et al., 2007). Any sample exceeding 400 would result in the maximum likelihood
estimation (MLE) method becoming too sensitive (detecting almost any difference among the data)
resulting in poor model fit.
A second limitation identified relates to the validity of the measurements. Having made use of a single
source from which information was obtained in combination with the choice to make use of only one
single research method at the same moment in time has most likely lead to information bias as well as
common method variance. Collecting data at different moments in time (obtaining longitudinal data)
would be advisable to increase the validity of the measurements. Additionally, having multiple informants
in each supplying company respond to the questionnaire would be deemed beneficial. Furthermore, the
data have been collected from one country only, namely Germany. This choice facilitated data collection
and enabled controlling for diversity but the results are assumed to have low external validity. To make
the findings more generalizable it would be important to perform comparative studies in different
industries and in other countries. (Podsakoff et al., 2003)
Furthermore, it should be noted that the collected data is somewhat perceptual. To increase the credibility
of the survey questionnaire it would have been advisable to collect ―hard‖ data to enable making
comparisons and checking the validity of the ―soft‖ data collected by means of the scales utilized (Nahm
et al., 2003). This is especially the case when measuring Overall Business Performance, Environmental
and Economic Performance. Company documents would be a more valid measurement as opposed to
asking respondents to indicate how they perceive the organization to be performing. Furthermore, the
items measuring the dependent variables, more specifically the items measuring Overall Business
Performance, can be refined to more precisely measure the construct.
On a fourth and last note it should be mentioned that whereas using similar scale formats is advantageous
in the sense that it simplifies the task of answering the questionnaire according to Podsakoff et al. (2003)
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it is assumed that the covariation among the constructs may result from the consistency in the scale
properties and may not be associable with the content of the items. Thus, future researchers should also
take this into account when deciding on which scale formats to utilize.
7.3 Conclusions
This research, drawing on the Resource Dependence Theory as well as the Institutional Theory, has taken
an environmental perspective on supply chain management and has investigated the relationship between
green supply chain practices and organizational performance. The study‘s main intention was to
determine if the outcomes obtained differed from those found by Lee et al. (2012).
The study results reveal that organizations should not only focus on achieving Overall Business
Performance outcomes but should also recognize the potential that increasing Employee Job Satisfaction,
Operational Efficiency and Relational Efficiency brings with it when trying to improve an organizations
Environmental and Economic Performance. Furthermore, when conducting the study on German
suppliers it was found that improvements in all three mediators (Employee Job Satisfaction, Operational
Efficiency and Relational Efficiency) yielded stronger improvements in Overall Business Performance as
compared to the results found by Lee et al. (2012).
In conclusion, it remains questionable if the findings can be generalized in consideration of the low
response rate. Nevertheless, this thesis has managed to identify several possible improvements that can be
made to the methodological approach and which will undoubtedly enable future research on the topic to
yield more generalizable and accurate results. The main recommendation for future research is to conduct
the study on a larger sample and to continuously refine the survey instrument. As measuring GSCM
Practice Implementation is a rather new discipline the development of good measurement tools provides
enormous potential for further research.
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APPENDIX
Appendix 1 – List of Questionnaire Items and the respective Measurement Scales
Measurement Items - GSCM Practice Implementation
Factors Measurement Items
Internal Environmental
Management (IEM)
IEM1: senior managers‘ commitment on GSCM
IEM2: mid-level managers‘ support for GSCM
IEM3: cross-functional cooperation for environmental
improvements
IEM4: environmental compliance and auditing programs
IEM5: ISO 14001 certification_d
Reference: Zhu et al. (2008)
Green Purchasing (GP) GP1: eco labeling of products
GP2: cooperation with suppliers for environmental objectives
GP3: environmental audit for suppliers‘ internal management_d
GP4: suppliers‘ ISO 14000 certification
Reference: Chen (2005), Zhu et al. (2008)
Cooperation with Customers (CC) CC1: cooperation with customers for eco-design_d
CC2: cooperation with customers for cleaner production
CC3: cooperation with customers for clean packaging
CC4: cooperation with customers for developing environmental
database of products
Reference: Hsu and Hu (2008), Zhu et al. (2008)
Eco-Design (ECO) ECO1: design of products for reduced consumption of material/
energy
ECO2: design of products for reuse, recycle, recovery of material,
component parts
ECO3: design of products to avoid or reduce use of hazardous
products and/ or their manufacturing process
ECO4: design of products for disassembly
ECO5: design of products considering LCA_d
Reference: Matos and Hall (2007), Rusinko (2007), Zhu et al.
(2008)
Measured on a five-point scale: 1=not considering it, 2=planning to consider it, 3=considering it
currently, 4=initiating implementation, and 5=currently implementing
Measurement Items – Mediators
Factors Measurement Items
Employee Job Satisfaction (SAT) SAT1: most employees like their jobs in the present operations
SAT2: most employees think their supervisor treats them well
SAT3: most employees in our firm like their jobs more than many
employees of other firms
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SAT4: most employees in our firm do not intend to work for a
different company_d
SAT5: overall, our employees are quite satisfied with their jobs
Reference: Homburg and Stock (2004), Zhou et al. (2008)
Operational Efficiency (OE) OE1: cycle time has been reduced
OE2: overall, costs have been lowered
OE3: overall, products‘ quality has been improved_d
OE4: customer service has been improved
OE5: project duration has been reduced_d
OE6: our firm has delivered greater value to our customers
Reference: Rusinko (2007), Paulraj et al. (2008), Zhu et al. (2008),
Zacharia et al. (2009)
Relational Efficiency (RE) RE1: an increased respect for the skills and capabilities of
customers
RE2: an improved level of honesty
RE3: more open sharing of information with our customers
RE4: a more effective working relationship with our customers
RE5: an enhanced commitment to work with our customers in the
future
RE6: an overall more productive working relationship with our
customers
Reference: Zacharia et al. (2009)
Measured on a five-point scale: 1=strongly disagree, 2=disagree, 3=neutral, 4=agree, and 5=strongly
agree
Measurement Items – Moderator
Factors Measurement Items
Market Pressure (MP) MP1: export
MP2: sales to foreign customers
Reference: Zhu and Sarkis (2007)
Measured on a five-point scale: 1=not at all important, 2=not important, 3=not thinking about it,
4=important, and 5=extremely important
Measurement Items - Performance
Factors Measurement Items
Overall Business Performance
(OBP)
OBP1: better asset utilization
OBP2: stronger competitive position
OBP3: improved profitability
OBP4: overall improved organizational performance
Reference: Zhu et al. (2008), Zacharia et al. (2009), Matsuno and
Mentzer (2000)
Measured on a five-point scale: 1=strongly disagree, 2=disagree, 3=neutral, 4=agree, and 5=strongly
agree
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Environmental Performance (EP) EP1: reduction of air emissions
EP2: decrease of consumption for hazardous/ harmful/ toxic
materials
EP3: reduction of waste water
EP4: reduction of solid wastes
EP5: decrease of frequency for environmental accidents_d
EP6: overall improved environmental performance
Reference: Zhu et al. (2007), Zhu et al. (2008)
Economic Performance (ECP) ECP1: decrease of fee for waste discharge_d
ECP2: decrease of fee for waste treatment_d
ECP3: decrease of cost for materials purchasing
ECP4: decrease of cost for energy consumption
ECP5: decrease of fine for environmental accidents
ECP6: new market opportunities
ECP7: improved profit margin
ECP8: increased sales
ECP9: overall improved economic performance
Reference: Rao and Holt (2005), Zhu et al. (2007), Zhu et al.
(2008), Zhu and Sarkis (2007), Fuentes-Fuentes et al. (2004)
Measured on a five-point scale: 1=not at all, 2=a little bit, 3=to some degree, 4=relatively significant, and
5=significant
Notes: _d indicates the items that were deleted in the modified model
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Appendix 2 – Survey Questionnaire
Green Supply Chain Practices Research Survey
General Information
Thank you in advance for participating in this online questionnaire.
The purpose of this survey is to explore the effect of a firm‘s green supply chain management (GSCM)
efforts on the broader supply chain network.
Green Supply Chain Management (GSCM) practice implementation is defined as the adoption of
environmentally friendly supply chain management practices including internal environmental
management, green purchasing, cooperation with customers, and eco-design for developing corporate and
operational strategies which will enable the company to achieve environmental sustainability.
Instructions. Please answer all questions to the best of your knowledge. All information is strictly
confidential and will not be shared. The entire questionnaire will take approximately 20 minutes to
complete.
At the completion of the survey you will have the opportunity to enter your e-mail address and receive a
copy of the Executive Summary or Master Thesis subsequent to its completion.
Once again, thank you for your time.
Question 1:
Employee Job Satisfaction (Homburg and Stock, 2004 and Zhou et al., 2008)
Please indicate the extent to which you agree or disagree to have perceived the following during the past
year. (Five-point scale: 1=strongly disagree; 2=disagree; 3=neutral; 4=agree; and 5=strongly agree)
Most employees like their jobs in the present operations.
Most employees think their supervisor treats them well.
Most employees in our firm like their jobs more than many employees of other firms.
Most employees in our firm do not intend to work for a different company.
Overall, our employees are quite satisfied with their jobs.
Question 2:
Operational Efficiency (Rusinko, 2007; Paulraj et al., 2008; Zhu et al., 2008; and Zacharia et al.,
2009)
Please indicate the extent to which you agree or disagree to perceive that your plant has achieved each of
the following during the past year. (Five-point scale: 1=strongly disagree; 2=disagree; 3=neutral;
4=agree; and 5=strongly agree)
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Reduction in cycle time.
Overall, a reduction in costs.
Overall, an improvement in product quality.
Improvement in customer service.
Reduction in project duration.
Increase in value delivered to our customers.
Question 3:
Relational Efficiency (Zacharia et al., 2009)
Please indicate the extent to which you agree or disagree to perceive that your plant has achieved each of
the following during the past year. (Five-point scale: 1=strongly disagree; 2=disagree; 3=neutral;
4=agree; and 5=strongly agree)
Increase in respect for the skills and capabilities of customers.
Improvement in the level of honesty.
Increase in open sharing of information with our customers.
Improvement in the effective working relationship with our customers.
Enhanced commitment to work with our customers in the future.
Overall, an improvement in the productive working relationship with our customers.
Question 4:
Overall Business Performance (Zhu et al., 2008; Zacharia et al., 2009; and Matsuno and Mentzer,
2000)
Please indicate the extent to which you agree or disagree to perceive that your plant has achieved each of
the following during the past year. (Five-point scale: 1=strongly disagree; 2=disagree; 3=neutral;
4=agree; and 5=strongly agree)
A better asset utilization.
A stronger competitive position.
An improved profitability.
An overall improved organizational performance.
Question 5:
Environmental Performance (Zhu et al., 2007 and Zhu et al., 2008)
Please indicate the extent to which you agree or disagree to perceive that your plant has achieved each of
the following during the past year. (Five-point scale: 1=not at all; 2=a little bit; 3=to some degree;
4=relatively significant; and 5=significant)
Reduction of air emissions.
Decrease of consumption for hazardous/ harmful/ toxic materials.
Reduction of waste water.
Reduction of solid wastes.
Decrease in frequency for environmental accidents.
Improvement in the enterprise‘s overall environmental performance.
Question 6 and 7:
Economic Performance (Rao and Holt, 2005; Zhu et al., 2007; Zhu et al., 2008; Zhu and Sarkis,
2007; and Fuentes-Fuentes et al., 2004)
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Please indicate the extent to which you agree or disagree to perceive that your plant has achieved each of
the following during the past year. (Five-point scale: 1=not at all; 2=a little bit; 3=to some degree;
4=relatively significant; and 5=significant)
Decrease in fee for waste discharge.
Decrease in fee for waste treatment.
Decrease in cost for materials purchasing.
Decrease in cost for energy consumption.
Decrease in fine for environmental accidents.
Increase in new market opportunities.
Improvement in profit margin.
Increase in sales.
Improvement in the enterprise‘s overall economic performance.
Question 8:
Which of the following Environmental Management Systems (EMSs) and programs are you aware of?
(multiple answers are possible)
ISO 14000 series
Electronic product environmental assessment tool
European Eco-Management and Audit Scheme (EMAS)
EU eco-label award scheme
Environment, health and safety (EHS) programs
Life Cycle Analysis (LCA)
Total quality environmental management
None of the above
Question 9:
Which of the following Environmental Management Systems (EMSs) and programs has your company
already adopted? (multiple answers are possible)
ISO 14000 series
Electronic product environmental assessment tool
European Eco-Management and Audit Scheme (EMAS)
EU eco-label award scheme
Environment, health and safety (EHS) programs
Life Cycle Analysis (LCA)
Total quality environmental management
None of the above
Question 10:
Internal Environmental Management (Zhu et al., 2008)
Please indicate the extent to which you perceive that your plant is implementing each of the following.
(Five-point scale: 1=not considering it; 2=planning to consider it; 3=considering it currently; 4=initiating
implementation; and 5=currently implementing)
support for GSCM (green supply chain practices) from senior managers
support for GSCM (green supply chain practices) from mid-level managers
cross-functional cooperation for environmental improvements
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environmental compliance and auditing programs
ISO 14001 certification
Question 11:
Green Purchasing (Chen, 2005 and Zhu et al., 2008)
Please indicate the extent to which you perceive that your plant is implementing each of the following.
(Five-point scale: 1=not considering it; 2=planning to consider it; 3=considering it currently; 4=initiating
implementation; and 5=currently implementing)
eco labeling of products
cooperation with suppliers for environmental objectives
environmental audit for suppliers‘ internal management
suppliers‘ ISO 14000 certification
Question 12:
Cooperation with Customers (Hsu and Hu, 2008 and Zhu et al., 2008)
Please indicate the extent to which you perceive that your plant is implementing each of the following.
(Five-point scale: 1=not considering it; 2=planning to consider it; 3=considering it currently; 4=initiating
implementation; and 5=currently implementing)
cooperation with customers for eco-design
cooperation with customers for cleaner production
cooperation with customers for clean packaging
cooperation with customers for developing environmental database of products
Question 13:
Eco-Design (Matos and Hall, 2007; Rusinko, 2007 and Zhu et al., 2008)
Please indicate the extent to which you perceive that your plant is implementing each of the following.
(Five-point scale: 1=not considering it; 2=planning to consider it; 3=considering it currently; 4=initiating
implementation; and 5=currently implementing)
design of products for reduced consumption of material/ energy
design of products for reuse, recycle, recovery of material, component parts
design of products to avoid or reduce use of hazardous products and/ or their manufacturing
process
design of products for disassembly
design of products considering LCA
Question 14:
How important are the following factors to your company when deciding to implement green supply
chain practices. (Five-point scale: 1=not at all important; 2=not important; 3=not thinking about it;
4=important; and 5=extremely important)
Exporting products. (general export pressures)
Selling to foreign customers. (customer pressures)
Question 15:
Please indicate your job title.
Employee in charge
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Middle manager
Senior executive
Top executive
Question 16:
Please indicate your current job specification.
Supply chain
Logistics
Sales
Production
Manufacturing
Other
Question 17:
How many years of work experience do you have in the industry?
Less than 5
5-10
11-15
More than 15
Question 18:
How many full-time employees work at your firm?
Less than 50
50-100
101-200
201-300
301-400
401-500
More than 500
Question 19:
Please indicate how you would classify the industry of industries of your company‘s buying firms.
(multiple answers are possible)
Automobile
Electronics
Telecommunication
Retail
Question 20:
Please indicate how you would define your firm‘s primary business goal in the supply chain.
First-tier supplier to major firms
Second-tier supplier
Supplier to government
Other
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Question 21:
Please enter your e-mail address if you would like to receive a copy of the Executive Summary or the
Master Thesis subsequent to its completion.
Thank you for your participation.