Page 1
A Scale for Measuring Consumer Perceptions of Corporate SocialResponsibility Following the Sustainable Development Paradigm
Alejandro Alvarado-Herrera1 • Enrique Bigne2 • Joaquın Aldas-Manzano2 •
Rafael Curras-Perez2
Received: 13 October 2014 / Accepted: 7 April 2015
� Springer Science+Business Media Dordrecht 2015
Abstract The aim of this research is to develop and
validate a measurement scale for consumer’s perceptions
of corporate social responsibility (CSRConsPerScale) us-
ing the three-dimensional social, environmental and eco-
nomic conceptual approach as a theoretical basis. Based on
the stages of measurement scale creation and validation
suggested by DeVellis (Scale development: theory and
applications, 1991) and supported by Churchill Jr.’s (J
Mark Res 16(1):64–73, 1979) suggestions, five different
empirical studies are developed expressly and applied to
consumers of tourist services. This research involves 1147
real tourists from 24 countries in two different cultural and
geographical contexts. A three-dimensional 18-item scale
is proposed for measuring consumer perceptions of cor-
porate social, environmental and economic responsibilities.
This paper presents the complete development of the scale,
as well as the implications and limitations of the main
findings and the managerial implications.
Keywords Consumer perceptions � Corporate social
responsibility � Scale development � Structural equation
modelling � Sustainable development
Abbreviations
CSR Corporate social responsibility
SD Sustainable development
Introduction
Corporate social responsibility (i.e. CSR) is a topic of
growing academic and management interest (Maon et al.
2010; Peloza and Shang 2011), particularly regarding its
impact on consumer behaviour variables. This is because
consumers tend to employ a company’s CSR image in
purchase and consumption decision making (Du et al. 2011;
Choi and Ng 2011; Trudel and Cotte 2009; Vlachos et al.
2009). Although this statement does not hold for all types of
products or in all segments (Auger et al. 2010; Peloza and
Shang 2011), some internationally recognised companies,
like General Motors, Unilever, Ikea and Avon, seek to po-
sition themselves as socially responsible brands by be-
coming strategically linked to a variety of social causes
including among others sustainable development (i.e. SD),
the fight against the climate change and cancer. Magazines
such as Business Week or Fortune report on firms’ CSR
activities or publish surveys, including Fortune’s ‘‘Amer-
ica’s Most Admired Corporations’’, which include some
CSR-related items (Luo and Bhattacharya 2006).
One of the main limitations of studies on the impact of
CSR on consumer behaviour is the way the construct is
measured. The lack of a unified scale for measuring CSR
makes it difficult to compare findings between studies, and
& Rafael Curras-Perez
[email protected]
Alejandro Alvarado-Herrera
[email protected]
Enrique Bigne
[email protected]
Joaquın Aldas-Manzano
[email protected]
1 Sustainable Development Division, University of Quintana
Roo, Av. Andres Quintana Roo (11 Avenida) s/n esquina 110,
77600 Cozumel, Quintana Roo, Mexico
2 Department of Marketing, Faculty of Economics, University
of Valencia, Av. Tarongers s/n. Ed. Dptal. Oriental,
46022 Valencia, Spain
123
J Bus Ethics
DOI 10.1007/s10551-015-2654-9
Page 2
the vagueness of the concept often leads to contradictory
results (Coles et al. 2013). Thus, reliable instruments are
needed to measure consumer perceptions of a firm’s CSR
(Auger et al. 2010; Green and Peloza 2011; Vlachos et al.
2009).
There have been valuable efforts to develop CSR scales
focused on managers (Aupperle 1984; Chow and Chen
2011), stakeholders (Perez et al. 2013) and consumers
(Oberseder et al. 2013). These have primarily used the
most successful theoretical approaches to the CSR con-
struct from consumer behaviour researchers: (i) Carroll’s
Pyramid model (1979, 1991), which includes economic,
legal, ethical and discretional dimensions and (ii) the cor-
porate associations notion suggested by Brown and Dacin
(1997), which discriminates between economic and non-
economic aspects, associating the latter with CSR in a one-
dimensional manner.
Both theoretical approaches have significant limitations.
Prior research into CSR perception based on Carroll’s
Pyramid suggests that it does not fit correctly to consumer
perceptions, as they do not manage to discriminate the four
dimensions proposed by the model (Garcıa de los Salmones
et al. 2005; Alvarado and Shlesinger 2008). In some of the
studies, depending on the cultural context, the economic
dimension of CSR perception even disappears (Maignan
2001; Maignan and Ferrell 2003). The Corporate Asso-
ciations approach cannot be used to discriminate any CSR
dimension because it treats CSR as a holistic perception in
the consumer’s mind. Therefore, some researchers suggest
using different theoretical frameworks for conceptualising
CSR from the consumer perception point of view to miti-
gate the limitations identified above (Maignan 2001;
Maignan and Ferrell 2003).
A few recent papers have progressed in this regard
(Oberseder et al. 2013). Nevertheless, the use of the SD
paradigm (which is capable of meeting the needs of the
present without compromising the ability of future gen-
erations to meet their own needs) (WCED 1987) has been
largely neglected despite the fact that it offers a useful
perspective for conceptualising CSR (Choi and Ng 2011;
Chow and Chen 2011; van Marrewijk 2003). Thus, the
main objective of this research is to develop and validate a
measurement scale to serve as a framework for measuring
customer perceptions of CSR activities (CSRConsPerS-
cale) using the SD three-dimensional (economic develop-
ment, social equity and environmental protection)
conceptual approach as a theoretical basis. This develop-
ment rests on the stages of measurement scale creation and
validation suggested by DeVellis (1991) and considers the
methodological aspects recommended by Churchill Jr.
(1979).
This article presents five empirical studies performed to
develop the scale. The studies were applied to tourism
services consumers in two countries (i.e. Spain and Mex-
ico) and for two activities: hotels and natural parks. Mexico
and Spain are among the top 15 world tourism destinations.
Both are highly dependent on international tourism with
different resources and type of tourist products. According
to the latest available data from World Tourism Organi-
zation, Spain was the third largest tourism destination in
2014 with 65 million and Mexico fifteenth in 2013 with
24.2 international tourist arrivals (UNWTO 2015).
An initial qualitative study based on a review of the
literature and the work of a panel of experts was conducted
to generate and then purge the items. An initial quantitative
study of university students in Spain was then conducted to
purge the scale for the first time. Next, we conducted a
mixed-method study (concept mapping, multidimensional
scaling and cluster analysis) with a focus group comprising
consumers of tourism services. The scale was refined and
validated by a second quantitative study among consumers
of hospitality services in Spain. Finally, to replicate and
generalise the scale, a third quantitative study was con-
ducted among natural parks tourists in Mexico. This article
presents and discusses the results of the above studies,
which demonstrate that the CSRConsPerScale is a reliable,
useful, valid and parsimonious instrument to measure
consumer perceptions of CSR in terms of sustainability
perspective. This study also reflects the professional and
academic implications of the CSRConsPerScale and the
main caveats for its extension.
The contributions of this paper to the existing literature
are twofold. First, it attempts to provide a multidimensional
scale for measuring consumer perceptions about CSR
firms’ initiatives. Second, the scale’s dimensions and items
are derived from the SD three-dimensional conceptual
approach: economic, social and environmental dimensions.
Thus, this work adopts a managerial perspective of CSR, as
the scale enables measurement of the consumer’s per-
spective on a firm’s particular strategy (e.g. on environ-
mental matters or in relation to its commitment to the
community). The scale also allows measurement of a
general CSR perspective on the firm because it can be used
to approximate global perception of a firm’s socially re-
sponsible nature (perceived CSR as a second-order
construct).
Theoretical Background
Sustainable Development as a Conceptual
Framework for CSR
The literature provides a wide variety of conceptualisations
of CSR (Garriga and Mele 2004; Peloza and Shang 2011).
Some of these conceptualisations define the businessperson
A. Alvarado-Herrera et al.
123
Page 3
(Bowen 1953; Davis 1960) as the subject of social re-
sponsibility, whereas others place responsibility on the
organisation as a whole (Carroll 1979; Sethi 1975). Some
conceptions situate CSR as a subversive doctrine (Fried-
man 1962), whereas others present it as the reflection of a
new social contract between firms and society (Bowen
1953; van Marrewijk 2003). Others consider CSR a reac-
tion to the social pressures that firms face (Carroll 1979;
Sethi 1975). Some works posit CSR as voluntary (Jones
1980; van Marrewijk 2003) and others as mandatory
(Bowen 1953; Frederick 1960). In other works, the study of
CSR focuses on the dimensions or areas for which the firm
is responsible (Carroll 1979) or underlines the public to
which the firm must answer (Jones 1980; Maignan et al.
2005).
In summary, there are at least two ideas shared by most
conceptualisations of CSR in academia. First is the as-
sumption that the firm has responsibilities beyond max-
imising profits (Carroll 1979; Davis 1960). The second idea
is linked to the first and maintains that the firm is not only
accountable to its owners, but also to other stakeholders
(Frederick 1960; Jones 1980; van Marrewijk 2003).
For some researchers, CSR differs from theoretical ap-
proaches such as Carroll’s Pyramid (1979, 1991) and
Corporate Associations (Brown and Dacin 1997); the use
of another framework might solve some of their main
limitations (Maignan 2001; Maignan and Ferrell 2003). As
indicated, the SD paradigm is a theoretical framework
particularly suitable for studying CSR. However, the aca-
demic community has largely neglected it (Choi and Ng
2011; Chow and Chen 2011; van Marrewijk 2003), prob-
ably because it can be difficult to implement at organisa-
tional level (Garriga and Mele 2004).
The term sustainable development was conceived for a
macrolevel that ‘‘calls for a convergence between the three
pillars of economic development, social equity, and envi-
ronmental protection’’ (Drexhage and Murphy 2010, p. 2).
In other words, it is a hypernorm that offers universal
principles but demands attention at organisational level to
convert the traditional ‘‘baseline’’ of economic profitability
into the ‘‘triple bottom line’’ (Garriga and Mele 2004) and
develop CSR strategies and actions that are more tangible
and easy to assess for consumers (Oberseder et al. 2014).
This is because CSR reflects the highest expectations of
citizens, consumers and investors concerning economic
growth, social cohesion and environmental protection
(Eberhard-Harribey 2006).
Thus, a useful definition of CSR for this paper is ‘‘a
firm’s commitment to maximise long-term economic, soci-
etal and environmental well-being through business prac-
tices, policies and resources’’ (Du et al. 2011, p. 1). The
definition is appropriate because it allows identification of
CSR dimensions directly from the SD model and its
sustainable-centred rationality translates to management
and operative objectives (Kakabadse and Rozuel 2006).
This definition grants the operationalisation of consumer
perception of CSR business practices, policies and re-
sources related to economic, societal and environmental
dimensions. In this same vein, it supports the idea that CSR
is a multidimensional reflective construct whose three di-
mensions—economic development (ECO), social equity
(SOC) and environmental protection (ENV)—correspond
to SD dimensions (van Marrewijk 2003).
Measurement of Consumer Perceptions of CSR
The idea that the firm has more than economic and tech-
nical responsibilities is based on the assumption that the
firm is also accountable to other groups with interests
different from those of shareholders (Jones 1980; van
Marrewijk 2003). However, the scarce literature on CSR
scales from the consumer perspective is due to the or-
ganisational behavioural approach that has focused on firm
managers as stakeholders (Quazi and O’Brien 2000; Turker
2009a). Approaches to CSR from the perspective of other
stakeholders (i.e. employees or consumers) have increased
over the years (Turker 2009b), leading to a myriad of focal
points. However, a gap in measurements from the customer
perspective remains to be filled (Oberseder et al. 2013,
2014) and is therefore the focus of this paper.
The early works in the 1970s tended to analyse criteria
for the demographic and psychographic segmentation of
the socially responsible consumer (Anderson Jr. and Cun-
ningham 1972; Kinnear et al. 1974). Since then, works
focusing on the CSR-consumer binomial have mainly
concentrated on understanding how CSR perceptions in-
fluence the cognitive, affective and behavioural responses
of consumers to the firm. For example, CSR perceptions
have been shown to have a positive impact on various types
of responses, such as brand reputation (Brammer and
Millington 2005), firm credibility (Lafferty 2007), con-
sumer–company identification (Marın and Ruiz 2007; Sen
and Bhattacharya 2001), the consumer’s purchase intention
(Trudel and Cotte 2009) and attitude towards the firm
(Brown and Dacin 1997; Du et al. 2011; Sen and Bhat-
tacharya 2001).
However, the literature review on this topic revealed a
lack of a homogeneous conceptualisation of CSR from the
consumer behaviour perspective (Green and Peloza 2011)
and, in particular, a lack of solid measurement instruments
for corroborating the reliability and validity of scales used
to measure consumer perceptions of CSR. Most studies
operationalise CSR perceptions in a unidimensional man-
ner based on the notion of corporate associations proposed
by Brown and Dacin (1997). These authors distinguished
two types of associations perceived by consumers in
A Scale for Measuring Consumer Perceptions of CSR Following the SD Paradigm
123
Page 4
relation to the firm (i.e. corporate associations): corporate
ability (CA) associations, which refer to the firm’s expe-
rience in producing and delivering products and services
(mainly technical and economic); and Corporate Social
Responsibility (CSR associations, which are ‘‘the reflection
of a firm’s status and activities with regard to its perceived
social obligations’’ (p. 68) that correspond to non-eco-
nomic issues. This approach facilitates the operationalisa-
tion of consumer perceptions of CSR and is therefore
useful in causal studies seeking to understand its relation-
ship with other attitudinal or behavioural variables. The
notion of CSR associations, however, is too general an
approach (and could even be considered a naıve approach)
to the CSR construct, as it does not permit discrimination
between different dimensions of CSR, thereby losing the
richness of the concept and distancing itself from content
validity.
In this context, a few works have assumed the multidi-
mensional nature of the CSR construct from the consumer
behaviour perspective or have carried out methodological
processes for creating and validating scales to measure the
construct for this group of stakeholders. Tables 1 and 2
summarise the conceptual and technical characteristics of
the six scales identified from the literature to measure
consumer perceptions of CSR from a multidimensional
perspective in the moment this stage was carried out, all
with a quantitative nature.
As can be seen, a group of works analyse whether
consumers perceptually discriminate economic, legal,
ethical and philanthropic responsibilities based on Carroll’s
(1979, 1991) conceptualisation, whereas the works of
Maignan (2001), Maignan and Ferrell (2003), David et al.
(2005), Garcıa de los Salmones et al. (2005) and Alvarado
and Shlesinger (2008) have repeatedly shown that the
conception of CSR in Carroll’s (1979, 1991) four dimen-
sions does not adequately reflect consumers’ minds. The
general conclusion is that economic responsibility does not
appear to form a part of the CSR construct for consumers,
underlining the idea that CSR is not about making a profit
for these stakeholders.
Furthermore, some studies based on the theoretical no-
tions of SD suggest that consumers are able to discriminate
the three dimensions of the CSR construct (Bigne et al.
2005; Singh et al. 2007); therefore, its use is justified in
accordance with the literature. This finding is particularly
true in the case of tourism (the sector chosen as the study
context) because the industry offers three advantages: (i) it
enables the inclusion of a heterogeneous group of inter-
viewees comprising individuals of different nationalities;
(ii) the industry’s main agents (e.g. hotels, airlines) are
active in CSR activities (Sheldon and Park 2011); and (iii)
SD and the triple bottom line is the development paradigm
adopted by the World Tourism Organization (2004).
Scale Development: CSRConsPerScale
The methodological process for developing the
CSRConsPerScale follows DeVellis’ (1991) proposal.
Furthermore, the chosen procedure was adapted following
the recommendations from Churchill Jr. (1979, 1999) and
Malhotra and Birks (2007), including a mixed-method
study. The following sections present each of the five
empirical studies and their main results (see Table 3).
Study 1: Scale Generation and Initial Purification
Item Generation
Following Cadogan et al. (1999), the six scales identified in
the literature measuring the same construct were analysed to
generate potential items for the new scale (see Table 1). A
total of 73 items were initially identified. First, we eliminated
the unnecessary items following Shimp and Sharma’s (1987)
key elimination criteria: (i) double argument, (ii) connotations
conditioning the respondent’s answer, (iii) ambiguity, (iv)
implicit assumptions and (v) relation to more than one SD
dimension. Of the 73 items, five were deleted and 68 were
retained for the next methodological phase.
Expert Review
A panel of experts scrutinised the list of generated items to
establish the scale’s content validity (DeVellis 1991).
Following Ouellet (2007), the panel comprised six ex-
perts—three PhD and three advanced PhD students with
the following profile: (i) university education at the post-
graduate level in business, (ii) in-depth marketing knowl-
edge, (iii) well-versed in the subject matter of CSR and (iv)
experience applying the scientific method.
The experts’ opinions addressed item elimination fo-
cused on redundancy, uncorrelation, content ambiguity
(Hardesty and Bearden 2004) and scale representativeness
of the construct (Zaichkowsky 1985). The expert review
resulted in a list of 25 items, nine corresponding to the
dimension SOC, seven to ENV and nine to ECO. The re-
fined list was used to develop a scale for testing in the pilot
questionnaire in the next stage.
Initial Determination of the Measurement Format
At this stage, we employed a metric using the Likert scale
with no neutral point and six response points. Avoiding a
neutral option eliminates the ‘‘easy way out’’ (Churchill Jr.
1999, p. 343) by preventing respondents from consciously
seeking a non-definition (Cox III 1980) and forcing them to
make a choice. General scales with a neutral point are less
reliable than those without (Churchill Jr. and Peter 1984).
A. Alvarado-Herrera et al.
123
Page 5
Table 1 Conceptual characteristics of measurement scales for consumer perception of CSR and its dimensions
Research and scale name Method Conception Dimension(s) of the scale and what it/they
attempt(s) to measure
Reference framework for
the dimension(s)
Maignan (2001), Maignan
and Ferrell (2003)
Survey Reflective Economic Importance a consumer attributes to the
economic dimension of CSR
Carroll’s Model (1979 and
1999)
Legal Importance a consumer attributes to the legal
dimension of CSR
Corporate social
responsibilities
Ethical Importance a consumer attributes to the
ethical dimension of CSR
Philanthropic Importance a consumer attributes to
the discretional dimension of CSR
Garcıa de los Salmones
et al. (2005)
Survey Reflective Economic Users’ opinion of what the firm does
about its social responsibility in the economic
arena
Carroll’s Model (1979 and
1999)
CSRa dimensions Ethical–legal Users’ opinion of what the firm does
about its social responsibility in the ethical–legal
arena
Philanthropic Users’ opinion of what the firm does
about its social responsibility in the discretional
field
David et al. (2005) Survey Reflective Moral-Ethical Personal importance attributed to the
moral and ethical aspects of CSR activities and the
firm’s perceived performance
Adapted from Carroll’s
Model (1979 and 1999)
Personal importance (and
perceived performance)
of CSR action
Discretional Personal importance attributed to the
discretionary aspects of CSR activities and the
firm’s perceived performance
Discretional Personal importance attributed to the
relational aspects of CSR activities and the firm’s
perceived performance
Bigne et al. (2005) Survey Reflective Social Consumer perception of socially responsible
firms in relation to certain social practices
Sustainable development
Elements perceived by
consumers as integral to
CSR
Economic Consumer perception of socially
responsible firms in relation to certain economic
practices
Environmental Consumer perception of socially
responsible firms in relation to certain
environmental practices
Singh et al. (2007) Survey Reflective Commercial Consumer perception of socially
responsible firms in relation to their creation of
value in commercial terms
Carroll’s Model (1979 and
1999)
Corporate social
responsibility Scale
Ethical Users’ opinion of what the firm does about
its social responsibility in the ethical arena
Social Consumer perception of socially responsible
firms in relation to certain social practices
Alvarado and Shlesinger
(2008)
Survey Reflective Economic Users’ opinion of what the firm does
about its social responsibility in the economic
arena
Carroll’s Model (1979 and
1999)
CSR dimensions Ethical–legal Users’ opinion of what the firm does
about its social responsibility in the ethical–legal
arena
Philanthropic Users’ opinion of what the firm does
about its social responsibility in the discretional
field
a Although Garcıa de los Salmones et al. (2005) tried to obtain the four dimensions established by Carroll (1979 and 1999) using Maignan’s
items (2001), their CFA indicated that the legal and ethical dimensions were in fact a single factor that they called the ethical–legal dimension. In
addition, a second-order CFA indicated that, according to their results, the economic dimension was not perceived by consumers as a component
of CSR
A Scale for Measuring Consumer Perceptions of CSR Following the SD Paradigm
123
Page 6
Table
2T
ech
nic
alch
arac
teri
stic
so
fsc
ales
for
mea
suri
ng
con
sum
erp
erce
pti
on
of
CS
R
Res
earc
hD
imen
sio
nT
yp
eo
fsc
ale:
#
item
s,#
po
ints
per
item
Rel
iab
ilit
yS
tati
stic
al
tech
niq
ue
and
go
od
nes
so
ffi
t
Val
idit
yS
amp
le
size
Po
pu
lati
on
Sec
tor
Co
un
try
(ies
)
Mai
gn
an(2
00
1)
and
Mai
gn
anan
d
Fer
rell
(20
03)a
Economic
Lik
ert:
4it
ems,
3p
oin
ts
a 1=
.81
EF
A;
no
tsp
ecifi
edN
ot
spec
ified
40
8C
on
sum
ers
No
tsp
ecifi
edF
ran
ce,
Ger
man
y
and
US
Aa 2
=.9
5
a 3=
.86
Legal
Lik
ert:
4it
ems,
3p
oin
ts
a 1=
.92
a 2=
.91
a 3=
.90
Ethical
Lik
ert:
4it
ems,
3p
oin
ts
a 1=
.91
a 2=
.96
a 3=
.92
Philanthropic
Lik
ert:
4it
ems,
3p
oin
ts
a 1=
.82
a 2=
.95
a 3=
.93
Gar
cıa
de
los
Sal
mo
nes
etal
.
(20
05)b
Economic
Lik
ert:
3it
ems,
7p
oin
ts
a=
.74
CF
A;
NF
I=
.90
;
NN
FI=
.89
;
GF
I=
.94
;
AG
FI=
.90
;
RM
SE
A=
.08
Co
nv
erg
ent
and
dis
crim
inan
t
68
9C
on
sum
ers
Ser
vic
es(M
ob
ile
tele
phony)
Sp
ain
IFC=
.77
Ethical–legal
Lik
ert:
4it
ems,
7p
oin
ts
a=
.75
IFC=
.76
Philanthropic
Lik
ert:
4it
ems,
7p
oin
ts
a=
.73
IFC=
.73
Dav
idet
al.
(20
05)c
Moral-Ethics
Lik
ert:
5it
ems;
10
po
ints
a=
.84
EF
A;
no
tsp
ecifi
edN
ot
spec
ified
17
6D
egre
est
ud
ents
fam
ilia
rw
ith
CS
R
Th
ree
fro
mth
e
con
sum
erg
oo
ds
sect
or
and
on
e
fast
foo
dre
stau
ran
t
US
A
a 1=
.78
a 2=
.81
a 3=
.76
a 4=
.82
Discretional
Lik
ert:
4it
ems;
10
po
ints
a=
.86
a 1=
.86
a 2=
.83
a 3=
.77
a 4=
.88
Relational
Lik
ert:
2it
ems;
10
po
ints
r=
.48
r 1=
.35
r 2=
.50
r 3=
.40
r 4=
.22
A. Alvarado-Herrera et al.
123
Page 7
Table
2co
nti
nu
ed
Res
earc
hD
imen
sio
nT
yp
eo
fsc
ale:
#
item
s,#
po
ints
per
item
Rel
iab
ilit
yS
tati
stic
al
tech
niq
ue
and
go
od
nes
so
ffi
t
Val
idit
yS
amp
le
size
Po
pu
lati
on
Sec
tor
Co
un
try
(ies
)
Big
ne
etal
.
(20
05)d
Social
Lik
ert:
6it
ems;
10
po
ints
a=
No
t
spec
ified
;
EF
A;
Ex
pl.
var
ian
ce=
60
%;
KM
O=
.81
No
tsp
ecifi
ed4
18
Stu
den
ts
Co
nsu
mer
s
Go
od
s(S
ho
esan
d
deo
dora
nt)
Arg
enti
na,
Chil
e,
Sp
ain
and
Po
rtu
gal
Economic
Lik
ert:
2it
ems;
10
po
ints
Environmental
Lik
ert:
4it
ems;
10
po
ints
Sin
gh
etal
.
(20
07)e
Commercial
Lik
ert:
4it
ems,
10
po
ints
a 1=
.79
CF
A;[
Sp
ain
]
NF
I=
.86
NN
FI=
.88
CF
I=
.90
IFI=
.90
RM
SE
A=
.06
Co
nv
erg
ent
and
dis
crim
inan
t
14
8[S
pai
n]
14
4[U
K]
Con
sum
ers
Go
od
s.D
airy
pro
duct
s
(Dan
on
e),
soft
dri
nks
(Co
caC
ola
),
cere
als
(Kel
logg’s
)
and
tooth
pas
te
(Co
lgat
e)
Sp
ain
and
UK
IFC=
.80
a 2=
.78
IFC=
.80
Social
Lik
ert:
4it
ems,
10
po
ints
a=
.77
;
IFC=
.76
a 2=
.78
IFC=
.81
Environmental
Lik
ert:
4it
ems,
10
po
ints
a=
.77
[UK
]
NF
I=
.85
NN
FI=
.86
CF
I=
.88
IFI=
.88
;
RM
SE
A=
.07
IFC=
.77
a 2=
.84
IFC=
.83
Alv
arad
o
and
Sh
lesi
ng
er
(20
08)
Economic
Lik
ert:
3it
ems,
7p
oin
ts
a=
.70
CF
A;
NN
FI=
.93
CF
I=
.95
IFI=
.95
MF
I=
.91
RM
SE
A=
.04
Co
nv
erg
ent
and
dis
crim
inan
t
35
8S
tud
ents
con
sum
ers
Ser
vic
es(M
ob
ile
tele
ph
on
y)
Sp
ain
IFC=
.76
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Lik
ert:
4it
ems,
7p
oin
ts
a=
.63
IFC=
.68
Philanthropic
Lik
ert:
4it
ems,
7p
oin
ts
a=
.69
IFC=
.69
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ents
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A Scale for Measuring Consumer Perceptions of CSR Following the SD Paradigm
123
Page 8
Study 2: Preliminary Measure Assessment
Sample and Procedure
In the following stage, we tested for scale reliability to
detect poor item performance. The questionnaire was
pretested in a pilot study on 17 members from the uni-
versity community, resulting in minor changes to some
items. As this was the early stage of scale development, we
decided to use a convenience sample of university students
from a variety of disciplines at two Spanish universities,
who had used tourism services recently. Interviewees were
chosen in two stages: First, 50 % of quotas were estab-
lished for gender and university, and second, interviewees
were randomly selected at their schools. The instrument
was administered to 204 individuals; 19 respondents were
eliminated because they failed to answer items or had a
tendency to answer yes or no to everything (Churchill Jr.
1979). The final 185 respondents included a balanced
number of women (50.3 %) and men (49.7 %) with an
average age of 22.4 years. All respondents were Spanish.
Data Analysis and Results
We ran confirmatory factor analysis (CFA) to detect items
that threatened convergent validity because of low stan-
dardised loadings or high Lagrange Multipliers (Cadogan
et al. 1999; Fornell and Larcker 1981). As a result, 11 items
(Soc6, Soc7, Soc8, Soc9, Env7, Eco1, Eco2, Eco3, Eco7,
Eco8 and Eco9) were identified as candidates for
elimination. Table 4 shows the results of each CFA and the
provisional decisions adopted.
The provisional consecutive exclusion of each item
identified as a candidate for elimination not only grants a
better statistical fit to the model, but also has theoretical
justification (Bagozzi 1981). The provisional purging of the
scale was detained to determine Cronbach’s a coefficients
for each factor using the retained items and calculate the
corresponding CR and AVE (see Table 5).
As observed, even with the elimination of the above-
mentioned items, the new values of Cronbach’s a and
composite reliability support scale reliability. However, the
AVE results show some deficiencies in the ECO and SOC
dimensions, suggesting the need for a new qualitative
phase to improve the scale.
Study 3: Scale Refinement and Validation (Mixed-
Method Study)
According to previous results, it was decided to carry out
the mixed-method study based on concept mapping (Tro-
chim 1989), which generates concept maps using multidi-
mensional scaling (i.e. MDS) and cluster analysis derived
from focus group results. This technique has been applied
to consumers (Joiner 1998), brands (John et al. 2006) and
travel agencies in the tourism setting (Bigne et al. 2002).
Table 3 Methodological process for scale development
Study Aim Approach Country/sample’s size Research method(s) and technique(s) Main expected
outcome(s)
One Generation and
initial
purification
Qualitative Spain and Mexico/N = 6
experts on CSR
Literature review and panel of experts Specification of
construct domain
Generation of sample/
pool of dimensions
and items
Evaluation of content
validity
Determination of the
format for
measurement
Two Preliminary
measure
assessment
Quantitative Spain/N = 185 university
students users of tourism
services
Survey and confirmatory factor analysis Initial reliability and
validity assessment
Three Refinement and
validation
Mixed Spain/N = 14 national and
international tourism
services’ users
Concept mapping; multidimensional
scaling and cluster analysis of focus
group results
Enhanced items and
dimensions
Four Additional
testing of the
scale
Quantitative Spain/N = 462 national and
international tourists on visit
Survey and confirmatory factor analysis Refined and validated
scale
Five Final replication
and
generalisation
Quantitative Mexico/N = 440 national and
international tourists on visit
Survey and confirmatory factor analysis Validated and
generalsed
CSRConsPerScale
A. Alvarado-Herrera et al.
123
Page 9
Sample and Procedure
The focus group comprised 14 consumers of tourism ser-
vices. After the participants sorted the items individually,
generated groups were shown to the participants. They
reached a consensus by merging the different groups or
reassigning items to different groups (see Trochim 1989 for
details of the methodological process).
Data Analysis and Results
The ALSCAL algorithm was used to construct the concept
map obtained from the MDS analysis because it is the most
appropriate algorithm for the type of data. The resulting
concept map, shown in Fig. 1, provides a very good fit:
Stress1 = .0156 (Kruskal 1964); S-Stress1 = .0062
(Takane et al. 1977) and RSQ = .9994 (Schiffman et al.
1981). The cluster analysis was hierarchical, and the so-
lution was determined following Ward’s method.
As expected, 24 of the 25 items considered in the pre-
liminary questionnaire and group dynamics showed strong
tendencies to group in their corresponding dimensions
anticipated by the theory and expert review. The exception
was item Eco9 (sponsorship of sporting events), adding
further evidence of its erratic behaviour. Garcıa de los
Salmones et al. (2005) first proposed that the item belonged
to the SOC dimensions, but the empirical results of their
study did not support that proposal. Therefore, item Eco9
was eliminated from the scale, and the dimensions SOC,
ENV and ECO were integrated for further empirical testing
with items Soc1–Soc9, Env1–Env7 and Eco1–Eco8,
respectively.
Drafting Improvements and Determination of the New
Measurement Format
When the participants reached a consensus on the items,
groups and composition, they were asked to propose
improvements to the items to eliminate ambiguities and
reaffirm the belonging of each to its resulting dimension.
The suggested improvements were studied carefully and
incorporated in the final drafting. The main suggestion
was to use a 7-point Likert scale, as some focus group
participants believed that consumers should not neces-
sarily have to agree or disagree with the statements
contained in the items, making a neutral response point
more desirable.
Table 4 CFAs for the preliminary analysis of the initial purging of the proposed scale
AFC Item SL S-B0 ad hoc goodness-of-fit indicators FA D Expected
in S-B with
elimination
of the item
Decision taken
NFI NNFI CFI IFI RMSEA
1 Eco1 .315 586.68*** (272 df) .607 .709 .736 .742 .080 Soc -22.543*** Provisional elimination
2 Eco7 .519 534.43*** (249 df) .625 .725 .752 .757 .079 Env -21.34*** Provisional elimination
3 Soc7 .425 476.27*** (227 df) .647 .747 .773 .778 .078 Eco -13.49*** Provisional elimination
4 Eco2 .532 420.99*** (206 df) .668 .768 .793 .798 .076 Soc -9.282*** Provisional elimination
5 Soc8 .244 377.90*** (186 df) .678 .775 .801 .806 .075 NA NA Provisional elimination
6 Soc9 .336 324.40*** (167 df) .706 .804 .828 .832 .072 Eco -4.061* Provisional elimination
7 Eco9 .376 249.51*** (149 df) .751 .861 .879 .882 .061 Env -5.132* Provisional elimination
8 Soc6 .370 206.58*** (132 df) .779 .890 .905 .907 .056 NA NA Provisional elimination
9 Eco3 .472 161.93** (116 df) .812 .926 .937 .939 .045 NA NA Provisional elimination
10 Eco8 .454 135.29* (101 df) .831 .940 .950 .951 .043 NA NA Provisional elimination
11 Env7 .516 123.05** (87 df) .834 .932 .943 .945 .048 NA NA Provisional elimination
12 Soc1 .688 94.42 (74 df) .859 .957 .965 .966 .039 Eco -5.61* End of provisional
purging process
CFA consecutive number of CFA, SL standardised loading, S-B0 S-B with the item loading to the factor it should theoretically load to, FA
additional factor to which the item could load according to the Lagrange Multipliers test, NA not applicable (used when the elimination criterion
was that SL\ .60)
* p\ .05; ** p\ .01; *** p\ .001
Table 5 Reliabilities by dimension after preliminary optimisation of
the scale (Study 2)
Dimension Cronbach’s a CR AVE
Social equity .725 .729 .352
Environmental protection .857 .858 .507
Economic development .710 .726 .479
CR composite reliability, AVE average variance extracted
A Scale for Measuring Consumer Perceptions of CSR Following the SD Paradigm
123
Page 10
Study 4: Testing the Refined Scale (Tourists
in Spain)
Sample and Procedure
The next methodological stage was conducted to refine and
validate the scale derived from the previous stage. We car-
ried out a new empirical study focused on the updated items
derived from the non-representative sample used in the
previous stage (Study 3). Due to the scale’s advanced de-
velopmental stage and because it was a second approach for
validation, we decided to work with a representative sample
of tourism consumers visiting the Spanish Mediterranean. A
random sampling plan was developed using three Spanish
urban tourism destinations ranked in the top 10 most visited
(Alicante, Barcelona and Valencia) as sampling points. The
sample size of 480 interviewees with a confidence level of
95 % (z = 1.96) and error less than ±5 % (e\ .046) was
considered appropriate. Of the 480 questionnaires, 18 were
discarded because of missing data or because they had been
answered unthinkingly, deriving a final sample of 462 tour-
ists without any significant impact on the anticipated confi-
dence levels or estimation error. The final sample comprised
59.3 % of men and 43.7 of women: 32 % were in the age
range of 18–30, 28.8 % in the range of 31–40 and 39.2 %
over 40. Of the respondents, 49.8 % were Spanish, 50.2 %
were foreign tourists and 77.3 % were employed. The av-
erage duration of stay was 3.5 days, and 60.4 % travelled by
plane to the tourist destination.
Assessment of the Items and Determination of Reliability
Based on data from the 462 valid questionnaires, the op-
eration of each item on the scale was assessed with an
initial determination of its reliability (DeVellis 1991).
Table 6 shows the results of Pearson’s correlation coeffi-
cients, average and standard deviation of the items for each
CSR dimension and Cronbach’s a coefficient calculated
from all the items initially considered in each factor.
As shown, average values of the items remained
relatively close to the other means for the indicators of the
group to which they belonged, and all the relations were
significant at a level of p\ .01 in relation to the other
items belonging to each group. Simple reliabilities (Cron-
bach’s a) for each dimension exceeded the acceptable
value of .80 for consolidated scales (Malhotra and Birks
2007; Nunnally and Bernstein 1994); therefore, it was
considered appropriate to continue with the analysis.
To determine the composed reliability indices and
variances extracted and to analyse the purging of the scale,
the same procedure followed in the first quantitative study
was adopted. Several first-order CFAs were run, and the
items that significantly affected scale fit were eliminated.
To avoid conditions incompatible with the convergent va-
lidity of the scale, the CFA results led to the definitive
elimination of items Soc2 and Soc5 because their stan-
dardised loads were below .60 (kSoc2 = .567 and
kSoc5 = .534) (Cadogan et al. 1999; Fornell and Larcker
1981). This was important because incompatibility would
Indicator Calculated value Critical value exceeded Fit Stress1 .0156 .025 Excellent S-Stress1 .0062 .025 Excellent R2 .9994 .600 Very good
Fig. 1 Concept mapping of Corporate Social Responsibility dimensions (Study 3)
A. Alvarado-Herrera et al.
123
Page 11
affect scale operation. Table 7 shows Cronbach’s a for
each factor using the remaining items and the corre-
sponding CR and AVE, and also presents the results for the
corresponding second-order CFA, where the reflective
concept perceived CSR was considered in the hypothesised
terms.
As shown, elimination of the aforementioned items
barely affected the value adopted by Cronbach’s a for the
social dimension and in all cases supported instrument
reliability by exceeding the minimum expected value of .80
for consolidated scales (Malhotra and Birks 2007; Nun-
nally and Bernstein 1994). Moreover, all the CR values
exceeded the .70 threshold and supported the reliability of
the measurement instrument. The AVE results exceeded
the critical value of .50 established for this conservative
criterion (Fornell and Larcker 1981).
Scale Length and Determination of Validity
The aim of this stage of scale development was twofold.
First, we sought to reduce scale length to an optimum point
and, second, to determine instrument validity. In all cases,
a balance between the length of the scale making it easy to
administer, scale reliability (DeVellis 1991) and validity
indicators at appropriate levels guided our goals. Conse-
quently, we assessed the validity of the scale in terms of
content, convergence, discriminant and nomological
validity.
Table 6 Correlations, mean, standard deviation and Cronbach’s a for each dimension (Study 4)
Soc1 Soc2 Soc3 Soc4 Soc5 Soc6 Soc7 Soc8 Soc9
Social equity dimension (a = .923)
Soc1 4.83 (1.27)
Soc2 .431** 5.45 (1.00)
Soc3 .801** .405** 4.97 (1.28)
Soc4 .518** .624** .568** 5.39 (1.14)
Soc5 .279** .609** .270** .605** 5.56 (1.07)
Soc6 .678** .465** .736** .613** .442** 5.21 (1.20)
Soc7 .714** .467** .706** .615** .412** .828** 5.07 (1.24)
Soc8 .659** .462** .630** .623** .461** .730** .812** 5.10 (1.21)
Soc9 .429** .483** .453** .556** .522** .580** .595** .652** 5.42 (1.11)
Env1 Env2 Env3 Env4 Env5 Env6 Env7
Environmental protection dimension (a = .946)
Env1 5.25 (1.07)
Env2 .427** 5.39 (1.08)
Env3 .435** .451** 5.40 (1.11)
Env4 .552** .415** .429** 5.47 (1.03)
Env5 .590** .418** .443** .599** 5.41 (1.04)
Env6 .734** .468** .432** .498** .601** 5.52 (1.09)
Env7 .353** .237** .387** .456** .470** .358** 5.44 (1.09)
Eco1 Eco2 Eco3 Eco4 Eco5 Eco6 Eco7 Eco8
Economic development dimension (a = .959)
Eco1 5.52 (1.08)
Eco2 .766** 5.58 (1.06)
Eco3 .706** .779** 5.59 (1.04)
Eco4 .711** .721** .750** 5.60 (1.07)
Eco5 .700** .737** .753** .789** 5.58 (1.07)
Eco6 .701** .681** .719** .753** .798** 5.56 (1.09)
Eco7 .740** .726** .738** .764** .780** .831** 5.59 (1.08)
Eco8 .685** .782** .747** .711** .752** .756** .820** 5.62 (1.06)
The diagonal shows the mean and standard deviation for each variable
** Significant correlation for p\ .01
A Scale for Measuring Consumer Perceptions of CSR Following the SD Paradigm
123
Page 12
Content validity refers to the degree to which a mea-
sure adequately reflects the different aspects of the phe-
nomenon being studied (Malhotra and Birks 2007). This
type of validity is fundamentally subjective (Malhotra and
Birks 2007) and cannot be guaranteed a priori because
construct consistency with the conceptual framework
from which it stems is given by the theory, appropriate
literature review and expert opinion (Churchill Jr. 1999).
As already noted, the methodological process chosen for
developing the scale included a stage for ensuring content
validity, which is considered to have been achieved in
light of the literature review and the results of Studies 1,
2 and 3.
Convergent validity of the CSRConsPerScale was de-
termined using goodness-of-fit criteria for the measurement
model, significance and direction of factor loading for the
items and the means of standardised loads on each factor.
Table 7 shows that goodness-of-fit indicators for the
CSRConsPerScale were adequate (NFI = .89; NNFI =
.92; CFI = .93; IFI = .93; RMSEA = .06).
Table 7 The first- and second-order CFA results and psychometric properties of CSRConsPerScale (Study 4)
Scale Factor k (2� CFA) t value Item Reliability Convergent validity
a CR AVE k (std.) t value ks (mean)
Perceived CSR .874 (mean) .907 .766
Social equity .856*** 13.06 Soc1 .926 .929 .652 .78# # .803
Soc3 .79*** 29.69
Soc4 .71*** 11.42
Soc6 .88*** 22.32
Soc7 .91*** 22.54
Soc8 .87*** 17.75
Soc9 .67*** 8.48
Environmental protection .955*** 13.79 Env1 .946 .947 .718 .79# # .847
Env2 .88*** 27.34
Env3 .83*** 23.26
Env4 .86*** 18.42
Env5 .87*** 19.32
Env6 .86*** 19.21
Env7 .85*** 18.60
Economic development .809*** 13.66 Eco1 .959 .959 .747 .82# # .864
Eco2 .85*** 33.32
Eco3 .86*** 28.22
Eco4 .86*** 27.91
Eco5 .88*** 26.49
Eco6 .87*** 27.03
Eco7 .90*** 26.06
Eco8 .87*** 25.97
Goodness-of-fit indicators Discriminant validity. AVE, Corr2 and confidence intervals
Social Environmental Economic
S-B v2 (206 df) = 495.67** Social .652 .471*** .375***
NFI = .89
NNFI = .92 Environmental [.508–.864] .718 .333***
CFI = .93 Economic [.452–.772] [.427–.727] .747
IFI = .93
RMSEA = .06 The diagonal shows the values of the variance extracted indexes, below the diagonal the confidence intervals for
each pair of factors and above the diagonal the squares of the inter-factor correlation coefficients
k Standardised load
*** p\ .001# Not estimated because it was used to identify the model
A. Alvarado-Herrera et al.
123
Page 13
Table 7 also shows that the factor loadings for all the
items were significant and positive in relation to their
factors (Churchill Jr. 1979), thereby indicating the con-
vergent validity of the model. Similarly, the means for the
standardised loads on each factor were high, significant and
exceeded the cut-off points of .70 and .50 (Fornell and
Larcker 1981), providing good indications of convergent
validity. In short, joint interpretation of the above criteria
makes it possible to state that the ongoing scale has con-
vergent validity.
Discriminant validity was tested using the difference test
and the confidence interval test for the correlation among
constructs (Anderson and Gerbing 1988) and the Fornell
and Larcker (1981) criterion, which compares AVE with
the squared correlation between constructs. Table 7 shows
that no evidence of problems with discriminant validity
arose from the results.
Nomological validity is shown if the scale correlates in the
theoretically anticipated form with the measures of different
but theoretically related concepts (Malhotra and Birks 2007).
To determine the nomological validity of our scale, six general
items were included in the questionnaire, two for the SOC
dimension (G_Soc1 and G_Soc2), two for ENV (G_Env1 and
G_Env2) and two for ECO (G_Eco1 and G_Eco2).
Table 8 shows the correlation coefficients between the
mean values of the responses in each considered dimension
and the contrast items. As can be seen, in all cases, the
correlations were strong, positive and significant (p\ .01)
thereby establishing the nomological validity of the scale
being developed according to the criterion (Shimp and
Sharma 1987).
Figure 2 shows the results of the second-order CFA for
Study 4.
Study 5: Replication and Generalisation (Tourists
in Mexico)
To refine and purge the CSRConsPerScale for addressing
generalisation, we conducted a third quantitative study in a
different country. Replication in geographical, sociocul-
tural and tourism service environments different from those
used for the previous quantitative studies (Studies 3 and 4)
will grant potential generalisation.
Sample and Procedure
A representative sample of tourists visiting the Mexican
Caribbean was chosen for the sample. A random sampling
plan was developed using three natural parks equipped
with appropriate infrastructures and tourist services, and
adopting three sampling points on the Yucatan Peninsula
(X’cacel-Xcacelito, Chankanaab and Faro Celerain-Punta
Sur). The sample size of 440 showed an estimation error of
less than ±4.5 % (e\ .047) with p = q = .50. The final
sample was 53.6 % of women and 46.4 % of men: 56.1 %
were in the age range of 16–35, 26.8 % were in the range
of 36–45 and 17 % were over 45. Americans comprised
64.2 % and Mexicans 20 %; 64.3 % were employed and
40.5 % came by cruise to the destination.
Data Analysis and Results
The operation of each item in the scale was evaluated, and
simple reliabilities were determined for each of the three
factors. Table 9 shows the results for Pearson’s correlation
coefficients, averages and standard deviations of the items
for each CSR dimension and Cronbach’s a coefficients cal-
culated from all the items initially considered in each factor.
Four new first-order CFA analyses were run for a
definitive purging of the scale, which led to the elimination
of items Soc9, Env3, Eco1 and Eco5: the first two because
of convergent validity problems (kSoc9 = .559, kEn-
v3 = .567) and the other two because of discriminant va-
lidity problems (Fornell and Larcker 1981). Then we ran a
new second-order CFA (Fig. 3). The results (Table 10)
permitted reasonable recognition (in general terms and
with the same tests and criteria followed in Studies 2 and 4)
of the convergent and discriminant validity of the
CSRConsPerScale in the context of Study 5. The above
analysis supported the scale’s external validity and its
usefulness as a valid parsimonious instrument in the terms
discussed in the following section.
Table 8 Correlation of
measures of the perceived CSR
dimensions with validation
items
Dimension Mean Validation item Mean Correlation coefficient
Pearson Spearman
Social equity 5.14 G_Soc1 5.38 .600** .575**
G_Soc2 5.39 .628** .577**
Environmental protection 5.41 G_Env1 5.40 .699** .660**
G_Env2 5.47 .707** .642**
Economic development 5.58 G_Eco1 5.44 .705** .635**
G_Eco2 5.47 .676** .609**
** p\ .01
A Scale for Measuring Consumer Perceptions of CSR Following the SD Paradigm
123
Page 14
Discussion and Conclusions
Theoretical Discussion
The main contribution of this research is the development
of the CSRConsPerScale, a valid measurement scale for
consumer perceptions of CSR based on three dimensions
proposed by the SD approach: economic development,
social equity and environmental protection responsibilities
(Choi and Ng 2011; Chow and Chen 2011; van Marrewijk
2003). Based on the methodology suggested by DeVellis
(1991), a process of 13 stages over five empirical studies
.856***
.955***
.809***
.784#
.794***
.714***
.881***
.911***
.866***
.674***
.787#
.876***
.826***
.863***
.866***
.862***
.848***
.823#
.851***
.856***
.860***
.880***
.872***
.898***
.871***
.621***
.608***
.700***
.473***
.413***
.500***
.617***
.482***
.563***
.506***
.501***
.508***
.530***
.568***
.525***
.517***
.510***
.476***
.489***
.440***
.491***
.739***
.518***
.297**
.588***
SOC
PerceivedCSR
ECO
ENV
Soc7
Soc9
Soc3
Soc4
Soc1
Soc6
Soc8
Env2
Env5
Env1
Env3
Env4
Env6
Env7
Eco1
Eco2
Eco3
Eco4
Eco5
Eco6
Eco7
Eco8
ESoc1
ESoc3
ESoc4
ESoc6
ESoc7
ESoc8
EEnv1
EEnv2
EEnv3
EEnv4
EEnv5
EEnv6
EEnv7
EEco1
EEco2
EEco3
EEco4
EEco5
EEco6
EEco7
EEco8
ESoc9 DSoc
DEnv
DEco
Fig. 2 The second-order CFA for Study 4. **p\ .01; ***p\ .001.
The details and psychometric properties of the model are shown in
Table 7. # = Not estimated because it was fixed at 1 to identify the
model. Goodness of fit indicators: NFI = .89; NNFI = .92;
CFI = .93; IFI = .93; RMSEA = .06, for a confidence interval at
90 % [.049; .061]; S-B chi (206df) = 495.669, p\ .001
A. Alvarado-Herrera et al.
123
Page 15
was followed to create the new scale and to debug and test
its reliability and validity through a confirmatory approach.
The final version of the CSRConsPerScale comprises 18
items: six for the ECO, six for the SOC and six for the
ENV dimension. Table 11 presents the wording and con-
tent of each item in the final version of the
CSRConsPerScale scale.
This study has two main theoretical conclusions. First,
the dependent factors considered in the second-order are
reflective of the CSR model (SOC, ENV and ECO) and
have discriminant validity according to the criteria used.
This proves that consumer perception of CSR is a multi-
dimensional construct, rather than the one-dimensional
factor postulated by the corporate associations approach
(Brown and Dacin 1997). This result, in line with Carroll’s
(1979, 1991), confirms that CSR is a complex construct
and that even in terms of consumer perceptions, its
complexity is reflected in the discrimination of economic,
social and environmental dimensions. This finding is im-
portant because no study in the literature has corroborated
[using confirmatory techniques (CFA)] consumer percep-
tions of the multidimensionality of CSR from a SD
perspective.
Secondly, this work supports the triple bottom line of
SD as a theoretical approach (widely accepted by practi-
tioners) that matches consumer perceptions of CSR even in
different cultural contexts. This finding helps overcome the
doubts expressed in previous studies about the extent to
which the framework established by Carroll (1979, 1991)
and its dimensions appropriately reflect the perceptions of
this group of stakeholders (e.g. Alvarado and Shlesinger
2008; Garcıa de los Salmones et al. 2005; Maignan 2001;
Maignan and Ferrell 2003). The definition of CSR pro-
posed by Carroll (1979, 1991) appears to fit better with the
Table 9 Correlations, means, standard deviation and Cronbach’s a for each dimension (Study 5)
Soc1 Soc3 Soc4 Soc6 Soc7 Soc8 Soc9
Social equity dimension (a = .835)
Soc1 3.67 (1.03)
Soc3 .521** 3.26 (1.12)
Soc4 .457** .434** 3.76 (1.03)
Soc6 .550** .443** .453** 3.70 (1.10)
Soc7 .425** .440** .429** .449** 3.69 (1.07)
Soc8 .356** .428** .340** .453** .421** 3.07 (1.01)
Soc9 .371** .309** .273** .351** .388** .527** 3.38 (1.02)
Env1 Env2 Env3 Env4 Env5 Env6 Env7
Environmental protection dimension (a = .872)
Env1 4.20 (.94)
Env2 .599** 3.94 (1.00)
Env3 .443** .471** 3.38 (1.02)
Env4 .585** .536** .313** 4.23 (.89)
Env5 .464** .456** .361** .504** 3.88 (.96)
Env6 .476** .501** .355** .557** .609** 3.99 (.95)
Env7 .487** .541** .413** .500** .626** .629** 3.87 (.99)
Eco1 Eco2 Eco3 Eco4 Eco5 Eco6 Eco7 Eco8
Economic development dimension (a = .880)
Eco1 3.37 (.92)
Eco2 .499** 3.59 (.93)
Eco3 .470** .545** 3.68 (1.01)
Eco4 .403** .438** .577** 3.51 (.99)
Eco5 .431** .297** .477** .462** 3.73 (1.06)
Eco6 .368** .492** .414** .561** .466** 3.45 (.93)
Eco7 .383** .478** .539** .623** .408** .565** 3.55 (.97)
Eco8 .470** .541** .545** .521** .408** .473** .596** 3.61 (.98)
The diagonal shows the mean and standard deviation for each variable
** Significant correlation for p\ .01
A Scale for Measuring Consumer Perceptions of CSR Following the SD Paradigm
123
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measurement of consumer expectations about the socially
responsible nature of the firm but not necessarily with the
measurement of perceptions of what the firm does in CSR.
In fact, in relation to whether the economic dimension
belongs to the CSR construct, Carroll (1999) notes that it
cannot always be perceived as such, because many indi-
viduals think that the economic component of CSR is what
the firm does for itself, whereas the other dimensions are
what the firm does for others. Furthermore, Carroll (1999)
adds that even when an individual does not perceive the
economic dimension as forming part of CSR, ‘‘financial
viability is something that firms do for society as well,
although we do not see it like that’’ (p. 284). Nevertheless,
it is illogical to exclude an essential part of the definition of
a concept when studying its indicators (Diamantopoulos
and Winklhofer 2001). Therefore, as financial viability is
indissociable from CSR according to the main dimensional
frameworks of CSR (i.e. Carroll’s Pyramid and SD), there
.696***
.862***
.825***
.700#
.670***
.660***
.714***
.645***
.595***
.704#
.726***
.718***
.719***
.767***
.767***
.666#
.732***
.763***
.674***
.790***
.729***
.714***
.742***
.751***
.700***
.764***
.804***
.710***
.687***
.696***
.695***
.641***
.642***
.746***
.682***
.647***
.739***
.613***
.684***
.718***
.489***
.566***
SOC
PerceivedCSR
ECO
ENV
Soc7
Soc3
Soc4
Soc1
Soc6
Soc8
Env2
Env5
Env1
Env4
Env6
Env7
Eco2
Eco3
Eco4
Eco6
Eco7
Eco8
ESoc1
ESoc3
ESoc4
ESoc6
ESoc7
ESoc8
EEnv1
EEnv2
EEnv4
EEnv5
EEnv6
EEnv7
EEco2
EEco3
EEco4
EEco6
EEco7
EEco8
DSoc
DEnv
DEco
Fig. 3 CSRConsPerScale after external validation and final purging:
the second-order CFA for Study 5. ***p\ .001. The details and
psychometric properties of the model are shown in Table 10. # = Not
estimated because it was fixed at 1 to identify the model. Goodness of
fit indicators: NFI = .89; NNFI = .93; CFI = .94; IFI = .94;
RMSEA = .051, for a confidence interval of 90 % [.042; .059];
S-B(132df) = 280.119, p\ .001
A. Alvarado-Herrera et al.
123
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is no logical or theoretical justification for eliminating it, as
to do so would destroy the content validity of the construct
itself. The above suggests that, at least in the area of the
behaviour of tourism services consumers, the SD paradigm
has greater explanatory ability for consumer perceptions of
CSR than Carroll’s Model (1979, 1991).
Managerial Implications
The main managerial implication of this study is that it
provides practitioners with a reliable, valid instrument for
measuring their customers’ perceptions of CSR, enabling
correct discrimination between economic, social and
environmental initiatives, that is, the CSRConsPerScale
could become a powerful instrument for monitoring the
effectiveness of CSR programmes in general or itemised
according to SD dimensions. This procedure would enable
a more effective combination of CSR with other classical
relational variables, such as perceived value, satisfaction
and loyalty, achieving measures that are more consistent
with the returns on a CSR programme, at least from the
consumer behaviour perspective.
Moreover, the CSRConsPerScale could be used by other
entities (e.g. NGOs, public authorities and social commu-
nication media) to determine real consumer perceptions of
a firm’s CSR performance.
Table 10 Results of the first- and second-order CFA and psychometric properties of CSRConsPerScale (Study 5)
Scale Factor k(28 CFA)
t value Item Reliability Convergent validity
a CR AVE k (Std.) t value ks (mean)
Perceived CSR .798 (mean) .842 .529
Social equity .696*** 10.77 Soc1 .825 .826 .442 .70# # .664
Soc3 .67*** 12.38
Soc4 .66*** 10.51
Soc6 .71*** 12.25
Soc7 .65*** 10.77
Soc8 .60*** 10.59
Environmental protection .872*** 10.58 Env1 .875 .875 .539 .70# # .734
Env2 .73*** 14.21
Env4 .72*** 13.54
Env5 .72*** 13.42
Env6 .77*** 13.12
Env7 .77*** 13.87
Economic development .825*** 10.44 Eco2 .870 .870 .529 .67# # .726
Eco3 .73*** 12.59
Eco4 .76*** 12.00
Eco6 .67*** 14.05
Eco7 .79*** 11.90
Eco8 .73*** 14.21
Goodness-of-fit indicators Discriminant validity. AVE, Corr2 and confidence intervals
Social Environmental Economic
S-B v2 (132 df) = 280.12*** Social .442 .368*** .329***
NFI = .89 Environmental [.517–.697] .539 .517***
NNFI = .93 Economic [.476–.672] [.651–.787] .529
CFI = .94
IFI = .94
RMSEA = .05 The diagonal shows the values of the variance extracted indexes, below the diagonal the confidence intervals for
each pair of factors and above the diagonal the squares of the inter-factor correlation coefficients
k Standardised load
*** p\ .001# Not estimated because it was used to identify the model
A Scale for Measuring Consumer Perceptions of CSR Following the SD Paradigm
123
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Limitations and Future Research
First, despite the effort to generalise the scale by applying it
to a different cultural context (Mexico) from the one in which
it was developed (Spain), this work does not by any means
exhaust the possibilities for generalising the scale. The
scale’s predictive validity needs corroborating with new
studies relating the CSR construct (measured with the
CSRConsPerScale) with other variables established in the
literature. For example, the relations between the CSR con-
struct and variables including consumer–company identifi-
cation (Lichtenstein et al. 2004; Sen and Bhattacharya 2001),
consumer satisfaction (Luo and Bhattacharya 2006), brand
loyalty (Garcıa de los Salmones et al. 2005) or consumer
interest and information about CSR initiatives (Oberseder
et al. 2011), which have significant relationships with con-
sumer CSR perception, should be evaluated.
Second, the content of the proposed scale items assumes
that the consumer must have a certain degree of knowledge
of the firm’s CSR initiatives to prevent erratic, unthinking
responses or reactions that are marked by social desirability.
However, there is usually low awareness of a company’s
CSR activities among its external stakeholders, especially
consumers (Pomering and Dolnicar 2009; Du et al. 2010).
This phenomenon in the creation of scales is not new. The
limitation of the consumer’s lack of information when ap-
plying a scale is also relevant to the application of well-
consolidated scales, such as SERVQUAL (Parasuraman
et al. 1988) or the customer-based corporate reputation of a
service firm scale (Walsh and Beatty 2007). This is also true
for other scales for measuring consumer perceptions about
the firm or its processes. Information asymmetry leads to
some items or dimensions about which consumers have less
knowledge, leaving them with less information upon which
to base their judgements—judgements that are typically
made considering heuristics or basic decision rules. The
halo effect (Nisbett and Wilson 1977) may come into play
in these situations: a consumer may use the evaluation of a
particular opinion (e.g. their knowledge of the firm’s sup-
port of social causes) to evaluate the entire socially re-
sponsible nature of the firm (e.g. the environmental or
economic CSR dimensions).
Managers who use the scale should consider this phe-
nomenon and try to mitigate it by, for example, providing
consumers with prior information on the firm’s CSR ac-
tivities. This approach has been used extensively in CSR
research (Berens et al. 2007; Sen and Bhattacharya 2001),
and its aim is to elicit in consumers’ minds or bring to their
memory the firm’s CSR activities, so they have the nec-
essary elements to make an evaluation. Alternatively, re-
searchers might check CSR awareness and adopt it as a
classification variable that could lead to cluster identifica-
tion in a sample population.
In this vein, the CSRConsPerScale appears more suit-
able for service firms (where personal contact between
consumer and firm is more frequent) than to firms that sell
Table 11 Items in the validated and purged CSRConsPerScale scale
In my opinion, regarding society, [Hotel chain/Park name] is really…… Trying to sponsor educational programmes (Soc1)
… Trying to sponsor public health programmes (Soc3)
… Trying to be highly committed to well-defined ethical principles (Soc4)
… Trying to sponsor cultural programmes (Soc6)
… Trying to make financial donations to social causes (Soc7)
… Trying to help to improve quality of life in the local community (Soc8)
In my opinion, regarding the environment, [Hotel chain/Park name] is really…… Trying to sponsor pro-environmental programmes (Env1)
… Trying to allocate resources to offer services compatible with the environment (Env2)
… Trying to carry out programmes to reduce pollution (Env4)
… Trying to protect the environment (Env5)
… Trying to recycle its waste materials properly (Env6)
… Trying to use only the necessary natural resources (Env7)
In my opinion, regarding the economy, [Hotel chain/Park name] is really…… Trying to maximise profits in order to guarantee its continuity (Eco2)
… Trying to build solid relations with its customers to assure its long-term economic success (Eco3)
… Trying to continuously improve the quality of the services that they offer (Eco4)
… Trying to have a competitive pricing policy (Eco6)
… Trying to always improve its financial performance (Eco7)
… Trying to do its best to be more productive (Eco8)
A. Alvarado-Herrera et al.
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goods. It could also be more applicable to long-term cus-
tomers than new ones. The services chosen in this research
are high involvement and considerably expensive. In short,
the scale must be applied to more industries with different
product categories to find out its degree of adaptability and
if, as we believe, the SD approach is valid beyond the
tourism sector as a theoretical approach to studying CSR
from the perspective of consumer perception.
Acknowledgment The authors acknowledge the financial support
of the research project of the Generalitat Valenciana (GV/2013-055).
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