Triple bottom line and sustainable performance measurement in industrial companies.
Hourneaux, Flavio, Jr. ; Gabriel, Marcelo Luiz da Silva ; Gallardo-Vazquez, Dolores Amalia 等
Triple bottom line and sustainable performance measurement in industrial companies.
1. Introduction
Sustainability, despite its inherent difficult to be properly
defined (Lele, 1991; Glavic and Lukman, 2007), has become a major issue
when seen from an organisational perspective. As previously pointed out
by several authors (e.g. Atkinson et al., 1997; Neely et al., 2002;
Epstein and Roy, 2003), since sustainability has had its role increased
in several aspects of management, one issue has arisen: how to better
understand the way sustainability has been taken into account in terms
of performance measurement by the firms? In order to find an answer to
this question, numerous studies have dealt with how companies could turn
firm's sustainability performance into a systematic and effective
way (Veleva and Ellenbecker, 2001; Warhust, 2002; Azapagic, 2004; Singh
et al., 2012; Krajnc and Glavic, 2005; Searcy, 2009).
Once it has become clear the need for a paradigm shift towards a
sustainable performance measurement, a new way to define
organisation's sustainable performance has advanced, the triple
bottom line (TBL) approach (Elkington, 1998; Harris etal., 2001; Pava,
2007; Norman and McDonald, 2004; Colbert and Kurucz, 2007). The TBL adds
both social and environmental dimensions to the traditional economic
results to measure a firm's performance from a sustainable
perspective.
Accordingly, many studies that aim to study sustainability and
performance in organisations use TBL as their conceptual basis,
mentioning Elkington's proposal as their conceptual reference (e.g.
Cinelli et al., 2014; Deng, 2015; Ekins and Vanner, 2007; Krajnc and
Glavic, 2005; Padua and Jabbour, 2015).
Given the importance of the theme and the need for differentiation
for unequal realities, several scholars have tried to shed some light on
how to integrate sustainability measurement in organisations from
different sectors. Thus, studies depict sectors such as minerals
(Azapagic, 2004); textiles (Zamcope et al., 2012); agricultural
(Guttenstein et al., 2010); oil and gas (Infante et al., 2013; Hourneaux
et al, 2017); and steel (Singh et al., 2007).
In this fashion, this paper aims to propose a minimum set of
indicators to be measured by industrial companies to represent their
performance according to the TBL approach. To do so, the instrument for
data collection was threefold: for the economic dimension, we used 20
BSCs typical indicators, according to Henri (2009); 9 and 22 indicators
from Global Reporting Initiative (GRI) (2008) for environmental and
social dimensions, respectively. The empirical research had a sample
that summed up 149 companies in Brazil.
The paper is structured as follows. Section 2 enfolds the main
concepts of sustainability, sustainable performance measurement and
indicators, followed by the study hypotheses. In the subsequent part, we
describe the research methodology. In the sequence, we show the main
results and analyses that were carried out and the paper ends with the
conclusions and recommendations.
2. Theoretical background
2.1 Sustainability and the triple bottom line approach
Possibly the most known definition related to this theme is the
Brundtland Commission's, that states that sustainable development
"meets the needs of the present without compromising the ability of
future generations to meet their own needs" (World Commission on
Environment and Development, 1987). Despite its importance, there have
been some difficulty and controversy in defining what sustainability is
(Lele, 1991; Doppelt, 2008), especially on how to translate it into
business frameworks and practices.
Possibly, due to its complexity, organisational sustainability is
most known as represented by the "TBL". According to Elkington
(1998), the TBL approach could lead an organisation to perform economic
prosperity, environmental quality and social justice simultaneously.
McDonough and Braungart (2002) emphasise that many executives are
getting to know these three concepts, including TBL issues as a way to
add value to their products or services. Later, Lacy et al. (2010) and
Berns et al. (2009) reinforce the importance of TBL as the main proxy to
represent and measure sustainability in organisations.
In the search for a consensus, among countless definitions and
terminologies, the three-pillar approach called the TBL has been a
widely accepted perspective for sustainability not only by scholars but
also by society and organisations (Lacy et al., 2010), although the TBL
has not been exempt from criticism and contention (Norman and McDonald,
2004; Macdonald and Norman, 2007).
Despite some researchers' resistance to this concept, to whom
the concept is impossible to be put into operation (Norman and McDonald,
2004; MacDonald and Norman, 2007; Hubbard, 2009; Smith and Sharicz,
2011), the TBL has gradually been accepted among organisations
(Elkington, 1998). Some studies reinforce this movement (Ho and Taylor,
2007; Hubbard, 2009).
2.2 Sustainability performance through indicators
In some sense, performance measurement has been noticed as a
fundamental key to the managerial control process in any business (Olson
and Slater, 2002). One point of departure for measuring
organisation's--whether sustainability-oriented or not--performance
is the use of indicators. As seen before, they can be split into
economic, social and environmental, according to the TBL approach.
2.2.1 Economic indicators: the balanced scorecard. The balanced
scorecard (BSC) was created by Kaplan and Norton, in the early 1990s.
The BSC is defined as a way to integrate strategy and action, through a
communication process, including objectives, goals, initiatives and
indicators, both financial and non-financial (Kaplan and Norton, 1996).
Kaplan and Norton (1996) created the BSC as a new management system that
"emphasises that financial and non-financial measures must be part
of the information system for employees at all levels of the
organisation" (p. 8).
BSC consists of four perspectives, setting the interrelationships
among performance indicators that could lead to a complete view of a
company's activities (Kaplan and Norton, 1996). As per Kaplan and
Norton (1996, p. 150), "[a] good Balanced Scorecard should have a
mix of outcome measures and performance drivers. Outcome measures
without performance drivers do not communicate how the outcomes are to
be achieved". Simons (2000) also stresses that a well-designed BSC
should allow a balance between short and long-term objectives and
outcome (lagging) and process (leading) measures, besides establishing
both objective and subjective measures for firm's performance.
Some authors explored BSC through statistical analysis, assessing
the validity and reliability of the model (Bouliane, 2006; Henri, 2009).
In one of these studies, Henri (2009), investigating 383 top management
teams of Canadian manufacturing firms, establishes a set of 20
indicators that would be representative of a typical BSC composition.
Table I presents these indicators, according to Henri's (2009)
proposal, used as a proxy for representing economic indicators in this
study.
2.2.2 Social and environmental indicators: Global Reporting
Initiative. The Global Reporting Initiative (GRI) Reporting Framework is
intended to perform as an accepted framework for reporting on an
organisation's economic, environmental and social performance (GRI,
2008). The GRI is a network with experts and representatives from
various sectors of society present in over 40 countries around the
world, and it has been determining the guidelines to sustainability
reporting with the participation of several important stakeholders (GRI,
2008).
Table II presents the social and environmental aspects defined by
the GRI guidelines. These aspects are "the general types of
information that are related to a specific indicator category, e.g.,
energy use, child labour, customers" (GRI, 2008) and will be used
as a proxy for the data gathering in this research.
3. Study hypotheses
This study aims to describe how TBL approach has had been taking
into account regarding the firm's performance measurement. Figure 1
presents the research's conceptual model and the hypotheses.
Two hypotheses refer to the relationship among the different types
of indicators, commonly presented as the three dimensions of the TBL.
These hypotheses are:
H1. There is a positive association between the degree of use of
environmental indicators and social indicators in industrial firms.
H2. There is a positive association between the degree of use of
environmental and social indicators and the use of economic indicators
in industrial firms.
A third hypothesis refer to an overall analysis of the TBL and
challenges the common understanding that the three dimensions would be
equal. This hypothesis is:
H3. Economic, environmental and social indicators have different
degrees of use in industrial firms.
4. Methodological aspects
This sections aims to define and describe the main methodological
aspects considered in the empirical research. Besides the content of
this section, a detailed explanation on the statistical procedures was
given also in Section 5.
4.1 Research definitions
The study is both descriptive and quantitative, using a survey-type
research approach, conducted with managers of industrial companies.
Despite the non-probabilistic sampling, this can be considered as a
homogeneous group, with at least one common characteristic, as belonging
to the same industry, as recommended by Flynn et al. (1990).
The research universe was the set of companies associated with the
Centre of Industries of Sao Paulo State (CIESP). To each company, an
invitation letter was sent by the board of social responsibility from
CIESP with instructions to access the electronic questionnaire.
In order to reach the purposes of the study, the instrument for
data gathering was threefold: for economic dimension, 20 BSCs
indicators, according to Henri (2009); 9 and 22 indicators from GRI
(2008) environmental and social dimensions, respectively, and questions
regarding companies' characteristics, as shown before in Tables I
and II. To each of these indicators, the respondent should identify its
degree of use, respecting a seven-point scale, with "1" being
"not at all" and "7" as "at a great
extent", with verbal anchors at the extremes.
4.2 Statistics
In this study, the chosen indicators were used as observed
variables of latent variables (constructs) and were treated as a scale.
Moreover, the relationship between constructs were hypothesised and
defined. The multivariate technique used was partial least
squares-structural equation modelling (PLS-SEM or PLS path modelling), a
second-generation technique primarily used to develop theories in
exploratory research (Hair, Gabriel, and Patel, 2014; Hair, Hult, Ringle
and Sarstedt, 2014).
From Shook et al. (2004) initial analysis of SEM usage in strategy
research to Robins's editorial (2012) in a special issue of Long
Range Planning devoted to the use of PLS-SEM, this technique is growing
in importance and relevance in strategy research. An SEM model is
composed of two main components: the measurement model (or outer model)
and the structural model (or inner model). The measurement model is used
to show the relationships between the constructs and the indicators, and
the structural model displays the relationships between the constructs
(Hair, Gabriel and Patel, 2014).
In any SEM approach, the measurement model is validated using
confirmatory factor analysis (CFA). CFA is useful to test a hypothesis
based on past evidence and/or theory and requires a strong knowledge of
observed measures that define the latent variable. Conversely from
exploratory factor analysis (EFA), CFA provides a greater emphasis on
theory testing and also offers a robust set of analytic procedures, not
available on EFA (Brown, 2006). Since CFA is focussed only on the link
between the factors and their measured variables, in the context of a
SEM represents the measurement model (Byrne, 2009).
PLS-SEM was used for model measurement, and the constructs were
hypothesised as reflective. Reflective models are the most used
measurement model in social sciences and have its roots in classical
test theory. This measurement model is useful when the hypothesis of
causality is generated from the construct to the indicators. The
structural model was assessed in their key results: significance and
relevance of relationships, predictive accuracy, effect size and
predictive relevance. Data were analysed using SmartPLS 2.0 (M3) (Ringle
et al., 2005).
5. Results
5.1 Sample characteristics
Brazil has the largest economy in Latin America. It is also known
for representing the first letter of the five countries from the BRICS
acronym. Sao Paulo State is one of the 27 Brazilian federative units and
responsible for more than 31 per cent of Brazilian GDP. It is also known
as the best infrastructure, the largest labour force and the most
powerful technological and industrial park. Its industrial sector is the
largest employer in the country, with more than 2.5m people.
The survey gathered 149 companies. We can highlight their main
characteristics as: the predominance of transformational industrial
companies (87.2 per cent); mostly of them are micro, small and medium
companies, with annual revenues less than USD60m (73.2 per cent) and a
number of employees less than 99 (59.1 per cent). Of these companies,
mostly, only 11.4 per cent are negotiated in the open market. They
mostly have domestic (79.9 per cent) and private capital (99.3 per
cent).
On variance based structural equation modelling, as PLS-SEM used in
this study, normality is not a required assumption as in
co-variance-based structural equation modelling (e.g. using software
like LISREL, AMOS, EQS, MPLUS, LAVAAN, and others). Hair, Gabriel, and
Patel (2014)/Hair, Hult, Ringle and Sarstedt (2014) considered
worthwhile to evaluate the data distribution. Following this suggestion,
data were tested using theory-driven methods (Razali and Wah, 2011),
namely, Shapiro-Wilk test (SK) for univariate normality and
Mardia's skewness and kurtosis, Henze-Zirkler and Doornik-Hansen
for multivariate normality. The results for univariate normality are
presented in Table III.
The results for multivariate normality are presented in Table IV.
The null hypothesis of all normality tests performed is not
supported, which support the statement of non-parametric data, and it is
suitable for PLS-SEM.
5.2 Assessment of measurement model
The estimation of a measurement model implies in the definition of
relationships between the indicators (observed variables) and the
construct (the latent variable). To assess a certain measurement model,
several criteria of reliability and validity must be evaluated. The
complete assessment of a measurement model includes the composite
reliability to evaluate internal consistency, individual indicator
reliability and average variance extracted (AVE) to check convergent
validity, Fornell-Larcker criteria and cross-loadings to assess
discriminant validity (Hair, Hult, Ringle and Sarstedt, 2014).
Composite reliability (pc) is measured from 0 to 1, and higher
values are equal to higher levels of reliability. As a rule of thumb,
values between 0.7 and 0.9 are considered satisfactory. Indicator
reliability and AVE are common measures of convergent validity.
Indicator reliability is measured by its outer loading, and the expected
measure is above 0.7. AVE should be above 0.50. These values are shown
in Table V.
Finally, discriminant validity is assessed by three measures:
Fornell-Larcker criteria cross-loadings and disattenuated correlation.
Fornell-Larcker criteria compare the squared root of the AVE of each
construct to the correlations with other latent variables (or
constructs), and the value of AVE should be greater. Also, an
indicator's outer loading on the associated construct should be
greater than any of its loadings in other constructs (cross-loaded), and
the disattenuated correlation approach is an estimate of what is the
true correlation between two constructs if they were perfectly measured.
Disattenuated correlation between two constructs close to 1 indicates
the lack of discriminant validity (Hair, Gabriel, and Patel, 2014; Hair,
Hult, Ringle and Sarstedt, 2014).
All indicators present outer loading above 0.7 and cross-loading
confirmed discriminant validity. All parameters fitted or exceeded the
minimum threshold. Table VI shows the squared root AVE (italics)
compared to the latent variable correlations, according to
Fornell-Larcker criteria.
The next step was to identify disattenuated correlations, which was
calculated for each pair of constructs, as shown in Table VII.
All parameters fitted or exceeded the minimum threshold suggested
by the literature, what validates the proposed scale. Thus, the results
suggest that it is possible to consider a firm's sustainable
performance through a set of 24 indicators, six for the economic
dimension, nine for the environmental and nine for social performance,
as presented in Table VIII.
5.3 Assessment of structural model
In SEM, the structural model is used to confirm the relationships
hypothesised between the constructs. Several results are used to confirm
or reject the hypothesis of a certain relationship, and the most common
are the size and significance of path coefficients, the coefficients of
determination ([R.sup.2]), predictive relevance ([Q.sup.2]) and effect
sizes ([f.sup.2]). The structural model is presented in Figure 2.
Both the size and significance of a structural model in PLS-SEM are
assessed by bootstrapping that generates an empirical t-value. Table IX
presents the results of bootstrapping for each indicator.
The results for the significance testing results of structural
model path coefficients are presented in Table X.
The path coefficients in a PLS-SEM can be interpreted as the
hypothesised relationships between the constructs and must be
interpreted relatively to one another. In this study, two of the
relationships are significant at a level of 1 per cent, and the effect
of GRI ENV on GRI_SOC is higher than the effect of GRI_ENV on BSC_FULL
and the smallest effect occurs on GRI_SOC related to BSC_FULL.
To assess the predictive relevance ([Q.sup.2]) in PLS-SEM, the
common procedure is blindfolding. Values of [Q.sup.2] higher than 0
suggest that the model has predictive relevance for certain endogenous
constructs. The coefficient of determination [R.sup.2] (the most
commonly used measure to evaluate the structural model) is also a
measure of the predictive accuracy of a certain model. The value of
[R.sup.2] ranges from 0 to 1 and values of 0.75,0.50 and 0.25 can be
described as substantial, moderate or weak (Hair, Gabriel, and Patel,
2014; Hair, Hult, Ringle and Sarstedt, 2014). Table XI presents the
values of [Q.sup.2] and [R.sup.2] for the hypothesised model.
The final assessment of a PLS-SEM structural is the effect size
([f.sup.2]). Effect size is useful to analyse the relevance of
constructs in explaining how much a predictor construct contributes to
the [R.sup.2] value of a target construct in the structural model.
Results from 0.02, 0.15 and 0.35 can be interpreted as small, medium and
large effect sizes (Hair, Gabriel, and Patel, 2014; Hair, Hult, Ringle
and Sarstedt, 2014). Effect sizes are presented in Table XII.
5.4 Hypotheses results
The results pointed out that: H1 was confirmed; H2 was not
confirmed and H3 was confirmed.
6. Discussion and conclusions
6.1 General remarks
As our results show, a set of indicators that covers the main
aspects of sustainability performance can be useful for industrial
companies' management, according to the TBL approach. Within the
economic dimension, on-time delivery, number of customer complaints and
survey of customer satisfaction are typical indicators related to the
firm's value proposition and emphasise the importance of the client
as a major stakeholder for companies in the industrial sector
(Karkkainen et al., 2001; Hourneaux, Siqueira, Telles and Correa, 2014).
On the other hand, materials efficiency variance, rate of material scrap
loss and labour efficiency variance are economic indicators directly
related to the efficiency of the industrial process--crucial for
industrial companies--and may have a high impact on firm's economic
performance.
In the environmental dimension, the indicators materials, energy
and water are the ones that have the highest priority on the measurement
of production costs (Hourneaux Jr, Hrdlicka, Gomes and Kruglianskas,
2014). Other indicators such as emissions, effluents and waste,
environmental aspects of products and services, environmental
compliance, and general environmental issues are also typical in
industrial process and should be measured, as well. Transporting also
has important impacts on industrial companies (Gonzalez-Benito and
Gonzalez-Benito, 2006). Finally, biodiversity has been considered as a
relevant issue for companies in an ecosystem like Brazil, one of the
richest in the world (Ramalho et al, 2016). It is important to state
that it may lose its importance in other industrial contexts.
In the social dimension, the indicators labour/management
relations, occupational health and safety, training and education,
non-discrimination, freedom of association and collective bargaining,
child labour, forced and compulsory labour, and security practices
emphasise the importance of the employees as another major stakeholder
for industrial companies (Shields and Young, 1992; Galeazzo and Klassen,
2015; Maia et al, 2018). Therefore, the social dimension can be seen as
critical and complex for sustainability performance. Compliance, the
other indicator is broader and can address the attempts to fit the
regulations and possible ethical conflicts, sometimes with grave and
unintended consequences to the companies (De Cremer and Lemmich, 2015).
Regarding the study's hypotheses, the results pointed out that
there are positive associations between the degree of use of
environmental indicators and social indicators for H1. These findings
emphasise that companies that have social and environmental orientation
can achieve some synergy in these two aspects of sustainability. As
mentioned before, the multidimensionality of sustainability and its
intrinsic overlapping within measures underpins these relationships
between environmental and social dimensions.
For H2, we conclude that economic, environmental and social
indicators have different degrees of use in firms. Despite this logical
deduction, companies can be misled to try to achieve the so-called
balanced among the three sustainability dimensions, as we can recall
some ideas like the three-legged stool as a representative figure for
the TBL approach.
On the other hand, in H3, a positive association between the degree
of use of environmental and social indicators and the use of economic
indicators was not confirmed. This result suggests that companies can
follow environmental and social performance regardless of their economic
performance and vice versa. Again, the idea of a TBL approach as
balanced as understood by common sense can be trick or misunderstood.
6.2 Academic implications
In brief, performance measurement is multidimensional and complex
(Bourne et al., 2000; Chenhall and Langfield-Smith, 2007; Richard et
al., 2009). As a logical consequence, sustainability performance should
present different dimensionalities and levels for its measurement (Van
Marrewijk and Werre, 2003). Trying to find new and better ways to deal
with these issues have been seen as of increasing importance (Searcy,
2012).
Although our suggestion--or any other framework, actually--could
not be considered as a complete or ideal solution to measure a
firm's sustainable performance, it can be seen as another path to
recognise the importance of sustainability for companies'
management.
Thus, this study aims to propose and validate a framework for
measuring a firm's performance from TBL perspective. The proposed
model is not expected to be considered as the only possible approach to
support the assessment of TBL in organisations. Furthermore, the
so-called balance on the TBL dimensions is rarely discussed, and it
seems to be something highly important to be done.
We also emphasise the need for more clarification on the
"balance" of the TBL approach to avoid misconceptions or
misunderstandings among scholars.
6.3 Practical implications
This research indicates that the use of the TBL performance
indicators can be done in different ways and degrees. It is also
important to emphasise that several other factors can also influence the
sustainable performance assessment, such as: industry, company size,
local regulation, stakeholders' efforts, competitive scenario,
company lifecycle, amongst many others that could be used as moderators
and/or mediators in the proposed model, generating a broader
comprehension of TBL in practice and its impact on managerial aspects of
every company, given an unique nature of every business.
This framework is supposed to work as a minimum set of indicators
that could provide managers, policymakers and researchers subsidies to
identify gaps and opportunities to enhance the overall performance of a
certain organisation on regard of sustainability. This minimum set of
indicators is intended to be used by industrial companies as a reliable
instrument to sustainable performance assessment of the current stage of
the TBL deployment and provide alternative approaches to address
specific issues related to the environmental, social and economic
sustainability.
6.4 Limitations and further research
This study has its limitations, mainly related to the
non-probabilistic sample and to the specific context in which it was
done, Brazilian industrial companies. Additionally, those indicators
used as proxies are generic indicators employed as a way to make it
possible for all the firms to participate in the research, instead of
specific ones that could lead to missing data. Future research works
could also investigate the fitness of the model for companies, and also
take into consideration variables that could moderate or mediate the
sustainable performance assessment.
As a sequence to this work, besides the possibility of counting on
a larger sample and replicating this instrument in other circumstances,
we suggest an investigation on the reasons for the use of this or that
set of indicators over others, and on what basis it occurs, in order to
enhance the quality and robustness of these indicators, as suggested by
Singh et al. (2012).
DOI 10.1108/REGE-04-2018-0065
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Received 29 April 2018
Revised 26 June 2018
Accepted 26 June 2018
Corresponding author
Flavio Hourneaux Jr can be contacted at: flaviohjr@usp.br
Flavio Hourneaux Jr
Department of Business Administration, School of Economics,
Business Administration and Accounting--University of Sao Paulo, Sao
Paulo, Brazil
Marcelo Luiz da Silva Gabriel
Head of Market Research and Business Intelligence, Central de
Inteligencia Automotiva--CINAU, Sao Paulo, Brazil, and
Dolores Amalia Gallardo-Vazquez
Departamento de Economia Financiera y Contabilidad, Universidad de
Extremadura--Campus Badajoz, Badajoz, Spain
Caption: Figure 1.
Conceptual model and hypotheses
Caption: Figure 2.
Structural model
Table I.
Economic indicators
used in the survey
Perspective Indicators Code (a)
Finance (1) Operational income OperIncF
(2) Sales growth SalesGrowF
(3) Return-on-investment (ROI) ROIF
(4) Return-on-equity (ROE) ROEF
(5) Net cash flows CashFlowF
(6) Cost per unit produced CostUnitF
Customer (1) Market share MShareC
(2) Customer response time RespTimeC
(3) On-time delivery OnTimeDelC
(4) Number of customer complaints NComplC
(5) Number of warranty claims NWaClaimC
(6) Survey of customer satisfaction SurveySatC
Internal processes (1) Materials efficiency variance MatEffVarP
(2) Manufacturing lead time ManTimeP
(3) Rate of material scrap loss MatLossP
(4) Labour efficiency variance LabEffVarP
Learning and (1) Number of new patents NNewPatL
development (2) Number of new product launches NNewProdL
(3) Time-to-market for new products TimeNewPrL
(4) Employee satisfaction EmplSatL
Note: Codes created for the purposes of this research
Source: Based on Henri (2009)
Table II.
Social and
environmental
indicators used in
the survey
TBL dimension Indicator Code (a)
Environmental Materials GRI ENV A
indicators Energy GRI ENV B
Water GRI_ENV_C
Biodiversity GRI_ENV_D
Emissions, effluents and waste GRI_ENV_E
Environmental aspects of products and GRI_ENV_F
services
Environmental compliance GRI_ENV_G
Transporting GRI_ENV_H
General environmental issues GRI_ENV_I
Social Employment GRI SOC A
indicators Labour/management relations GRI SOC B
Occupational health and safety GRI SOC C
Training and education GRI SOC D
Diversity and equal opportunity GRI SOC E
Investment and procurement practices GRI SOC F
Non-discrimination GRI SOC G
Freedom of association and collective GRI SOC H
bargaining
Child labour GRI SOC I
Forced and compulsory labour GRI SOCJ
Security practices GRI SOC K
Indigenous rights GRI SOC L
Community GRI SOC M
Corruption GRI SOC N
Public policy GRI SOC O
Anti-competitive behaviour GRI SOC P
Compliance GRI SOC Q
Customer health and safety GRI SOC R
Product and service labelling GRI SOC S
Marketing communications GRI SOC T
Customer privacy GRI SOC U
Compliance of products and services GRI SOC V
Note: (a) Codes created for the purposes of this research
Source: Created by the authors, based on GRI (2008)
Table III.
Univariate
normality test
Shapiro-
Wilk test
TBL dimension Indicator Statistic
Economic OperIncF 0.750
indicators SalesGrowF 0.720
ROIF 0.868
ROEF 0.923
CashFlowF 0.779
CostUnitF 0.815
MShareC 0.893
RespTimeC 0.861
OnTimeDelC 0.733
NComplC 0.782
NWaClaimC 0.831
SurveySatC 0.846
MatEffVarP 0.895
ManTimeP 0.819
MatLossP 0.872
LabEffVarP 0.893
NNewPatL 0.855
NNewProdL 0.930
TimeNewPrL 0.919
EmplSatL 0.874
Environmental Materials 0.920
indicators Energy 0.884
Water 0.872
Biodiversity 0.872
Emissions, effluents and waste 0.881
Environmental aspects of products and 0.896
services
Environmental compliance 0.855
Transporting 0.914
General environmental issues 0.906
Social Employment 0.904
indicators Labour/management relations 0.920
Occupational health and safety 0.859
Training and education 0.893
Diversity and equal opportunity 0.933
Investment and procurement practices 0.921
Non-discrimination 0.885
Freedom of association and collective 0.906
bargaining
Child labour 0.810
Forced and compulsory labour 0.812
Security practices 0.840
Indigenous rights 0.768
Community 0.900
Corruption 0.857
Public policy 0.885
Anti-competitive behaviour 0.868
Compliance 0.878
Customer health and safety 0.864
Product and service labelling 0.885
Marketing communications 0.903
Customer privacy 0.804
Compliance of products and services 0.869
Shapiro-
Wilk test
TBL dimension Indicator df
Economic OperIncF 149
indicators SalesGrowF 149
ROIF 149
ROEF 149
CashFlowF 149
CostUnitF 149
MShareC 149
RespTimeC 149
OnTimeDelC 149
NComplC 149
NWaClaimC 149
SurveySatC 149
MatEffVarP 149
ManTimeP 149
MatLossP 149
LabEffVarP 149
NNewPatL 149
NNewProdL 149
TimeNewPrL 149
EmplSatL 149
Environmental Materials 149
indicators Energy 149
Water 149
Biodiversity 149
Emissions, effluents and waste 149
Environmental aspects of products and 149
services
Environmental compliance 149
Transporting 149
General environmental issues 149
Social Employment 149
indicators Labour/management relations 149
Occupational health and safety 149
Training and education 149
Diversity and equal opportunity 149
Investment and procurement practices 149
Non-discrimination 149
Freedom of association and collective 149
bargaining
Child labour 149
Forced and compulsory labour 149
Security practices 149
Indigenous rights 149
Community 149
Corruption 149
Public policy 149
Anti-competitive behaviour 149
Compliance 149
Customer health and safety 149
Product and service labelling 149
Marketing communications 149
Customer privacy 149
Compliance of products and services 149
Shapiro-
Wilk test
TBL dimension Indicator Sig.
Economic OperIncF 0.000
indicators SalesGrowF 0.000
ROIF 0.000
ROEF 0.000
CashFlowF 0.000
CostUnitF 0.000
MShareC 0.000
RespTimeC 0.000
OnTimeDelC 0.000
NComplC 0.000
NWaClaimC 0.000
SurveySatC 0.000
MatEffVarP 0.000
ManTimeP 0.000
MatLossP 0.000
LabEffVarP 0.000
NNewPatL 0.000
NNewProdL 0.000
TimeNewPrL 0.000
EmplSatL 0.000
Environmental Materials 0.000
indicators Energy 0.000
Water 0.000
Biodiversity 0.000
Emissions, effluents and waste 0.000
Environmental aspects of products and 0.000
services
Environmental compliance 0.000
Transporting 0.000
General environmental issues 0.000
Social Employment 0.000
indicators Labour/management relations 0.000
Occupational health and safety 0.000
Training and education 0.000
Diversity and equal opportunity 0.000
Investment and procurement practices 0.000
Non-discrimination 0.000
Freedom of association and collective 0.000
bargaining
Child labour 0.000
Forced and compulsory labour 0.000
Security practices 0.000
Indigenous rights 0.000
Community 0.000
Corruption 0.000
Public policy 0.000
Anti-competitive behaviour 0.000
Compliance 0.000
Customer health and safety 0.000
Product and service labelling 0.000
Marketing communications 0.000
Customer privacy 0.000
Compliance of products and services 0.000
Source: Created by the authors
Table IV.
Multivariate
normality test
Test Statistics [chi square] df Sig.
Mardia
mSkewness 1,304.38 33,069.84 23,426 1 0.000 0.000
mKurtosis 3,012.02 657.991
Henze-Zirkler
1.000388 2.34e+07 1 0.000
Doornik-Hansen 523.317 0.000
Source: Created by the authors
Table V.
AVE and composite
reliability for each
construct
AVE [[rho].sub.c]
BSC_FULL 0.5698 0.88796
GRI ENV 0.6440 0.9418
GRI_SOC 0.6026 0.9577
Reference values > 0.50 > 0.708
[R.sup.2] Cronbach's [alpha]
BSC_FULL 0.282 0.853
GRI ENV 0.930
GRI_SOC 0.555 0.915
Reference values Weak = 0.25 > 0.708
Moderate = 0.50
Substantial = 0.75
Source: Created by the authors
Table VI.
Correlations among
constructs
BSC_FULL GRI_ENV GRI_SOC
BSC_FULL 0.7725
GRI_ENV 0.5310 0.8025
GRI_SOC 0.4550 0.6921 0.7763
Source: Created by the authors
Table VII.
Disattenuated
correlations among
constructs
Original Disattenuated Discriminant
correlation correlation validity
BSC_FULL-GRI_ENV 0.8879 0.5866 Supported
BSC_FULL-GRI_SOC 0.4550 0.4934 Supported
GRI_ENV-GRI_SOC 0.6921 0.7287 Supported
Note: Reference values < 0.90
Source: created by the authors
Table VIII.
Triple bottom line
performance
measurement and
representative
indicators for each
dimension
Economic Dimension Environmental dimension
On-time delivery Materials
Number of customer complaints Energy
Survey of customer satisfaction Water
Materials efficiency variance Biodiversity
Rate of material scrap loss Emissions, effluents and waste
Labour efficiency variance Environmental aspects of
products and services
Environmental compliance
Transporting
General environmental issues
Economic Dimension Social dimension
On-time delivery Labour/management relations
Number of customer complaints Occupational health and safety
Survey of customer satisfaction Training and education
Materials efficiency variance Non-discrimination
Rate of material scrap loss Freedom of association and
collective bargaining
Labour efficiency variance Child labour
Forced and compulsory labour
Security practices
Compliance
Source: Created by the authors
Table IX.
Bootstrapping results
for each indicator
Latent Indicator Outer t-value Sig. level p-value
variable weight
Economic BSCF1 0.678 7.587 *** 0.000
BSCF2 0.715 8.493 *** 0.000
BSCF3 0.855 36.384 *** 0.000
BSCF4 0.813 25.948 *** 0.000
BSCF5 0.690 7.386 *** 0.000
BSCF6 0.753 13.029 *** 0.000
Environmental GRI_ENV_A 0.731 14.745 *** 0.000
GRI_ENV_B 0.744 16.042 *** 0.000
GRI_ENV_C 0.832 24.624 *** 0.000
GRI_ENV_D 0.830 26.534 *** 0.000
GRI_ENV_E 0.887 46.394 *** 0.000
GRI_ENV_F 0.828 19.445 *** 0.000
GRI_ENV_G 0.705 12.365 *** 0.000
GRI_ENV_H 0.764 16.525 *** 0.000
GRI_ENV_I 0.885 38.134 *** 0.000
Social GRI_SOC_B 0.766 20.352 *** 0.000
GRI_SOC_C 0.777 26.504 *** 0.000
GRI_SOC_D 0.744 19.918 *** 0.000
GRI_SOC_G 0.799 22.637 *** 0.000
GRI_SOC_H 0.825 26.083 *** 0.000
GRI_SOC_I 0.787 19.057 *** 0.000
GRI_SOC_J 0.793 20.541 *** 0.000
GRI_SOC_K 0.710 14.397 *** 0.000
GRI_SOC_Q 0.742 16.007 *** 0.000
Note: ***p < 0.001
Source: Created by the authors
Table X.
Significance testing
results of structural
model path
coefficients
Path coefficients t-values
GRI ENV [right arrow] BSC FULL 0.415 3.863
GRI ENV [right arrow] GRI SOC 0.692 15.183
GRI SOC [right arrow] BSC FULL 0.168 1.556
Significance level Hypothesis
GRI ENV [right arrow] BSC FULL p > 0.01 Confirmed
GRI ENV [right arrow] GRI SOC p > 0.01 Not confirmed
GRI SOC [right arrow] BSC FULL p > 0.10 Confirmed
Source: Created by the authors
Table XI.
Results of [R.sup.2] and [Q.sup.2]
values
[R.sup.2] [Q.sup.2]
BSC FULL 0.282 0.1619
GRI SOC 0.555 0.2724
Source: created by the authors
Table XII.
Results of [f.sup.2]
[f.sup.2]
BSC FULL 0.379
GRI SOC 0.497
GRI ENV 0.562
Source: Created by the authors
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