Knowledge and the Climate Change Issue: An Exploratory Studyof Cluster and Extra-Cluster Effects
Jeremy Galbreath • David Charles •
Des Klass
Received: 11 February 2013 / Accepted: 16 September 2013
� Springer Science+Business Media Dordrecht 2013
Abstract Climate change, while potentially impacting
many industries, appears to have considerable significance
to the wine industry. Yet little is known about how firms
acquire knowledge and gain an understanding of climate
change and its impacts. This study, exploratory in nature
and studying firms from the wine-producing region of
Tasmania, is one of the first in the management literature to
use cluster theory to examine the climate change issue.
Firms are predicted to exchange knowledge about climate
change more readily with other firms internal to the sub-
cluster than with those external to the sub-cluster. The
hypothesis does not find support. The study also proposes
that the different characteristics of knowledge can either
increase or decrease their flows in and around clusters.
Specifically, ‘‘public’’ knowledge about climate change is
predicted to flow more freely than ‘‘private’’ knowledge
about climate change. The hypothesis does not find sup-
port. Finally, firms are expected to acquire knowledge
about climate change from sources other than cluster-
entrenched firms, and in particular peak national industry
bodies. The hypothesis finds partial support. A discussion
of the findings is presented along with future research
directions.
Keywords Australia � Climate change � Clusters �Knowledge � Knowledge exchange � Wine
Introduction
Climate change is leading to business volatility, risk, and
disruption (Hoffman and Forbes 2011). As such, it is
considered ‘‘one of the greatest economic and political
challenges facing the world economy this century’’ (Knight
2011, p. 817). NASA climate scientist Professor Jim
Hansen goes so far as to claim it is a ‘‘great moral issue’’
(cited in Carrell 2012). Therefore, firms need to acquire
knowledge about climate change, as it has the potential to
impact their strategies and operations (Winn et al. 2011).
This seems to be especially the case for wine producers
(Galbreath 2011a, 2012; Nicholas and Durham 2012).
Wine production is an industry very sensitive to climatic
changes; for example, as little as a 1 �C increase in average
temperature can dramatically affect which varieties can best
be ripened where (Keller 2010). Indicative of these tem-
perature effects, a major global study has found that in the
world’s top wine-producing regions, temperatures have risen
in the last 55 years by an average of 1.26 �C, and are
expected to rise by an average of 2.04 �C by 2050 (Jones
et al. 2005). Thus, the survival of many wine-growing
regions could be under threat due to climate change.
Given that wine producers have historically faced
shifting and changing climatic conditions from one vintage
to the next—due to the fact that they are weather-driven
enterprises—and given that wine production takes place
mainly in narrow geographic clusters (Porter and Bond
2008), there would seem to be an advantage for producers
to be freely exchanging knowledge about climate change
within specific clusters. More specifically, are wine
J. Galbreath (&) � D. Klass
Curtin Graduate School of Business, Curtin University of
Technology, 78 Murray Street, Perth, WA 6000, Australia
e-mail: [email protected]
D. Klass
e-mail: [email protected]
D. Charles
European Policies Research Centre, School of Government and
Public Policy, University of Strathclyde, 40 George Street,
Glasgow G1 1QE, UK
e-mail: [email protected]
123
J Bus Ethics
DOI 10.1007/s10551-013-1901-1
producers freely engaging in knowledge exchanges about
climate change and are these exchanges influenced by their
location in a particular cluster?
Considering this question, this study seeks to explore
some fundamental aspects that have remained largely
unexplored in the cluster literature. For example, while it is
known that firms are attempting to respond to climate
change (e.g., Dawkins and Fraas 2011; Eberlein and Mat-
ten 2009; Galbreath 2011a, 2012; Le Menestrel et al.
2002), there is little research demonstrating how firms
might acquire sufficient knowledge and understanding
about the issue. Following cluster theory (Porter 1998,
2000), this study hypothesizes that given the potential
magnitude and impact of climate change on wine produc-
tion, producers in wine clusters readily exchange knowl-
edge about climate change because of geographic
proximity. However, the paper relies on a rarely studied
dimension of clusters; namely, sub-cluster effects. As sub-
clusters develop unique identities within a regional cluster,
firms are expected to exchange knowledge about climate
change more freely within the sub-cluster than with firms
in other sub-clusters in the region (Fig. 1).
A second aspect, and one that follows the work of
Tallman et al. (2004), concerns what type of knowledge
about climate change is exchanged between firms in wine
clusters. For example, in their study of 32 firms in the
aerospace cluster in Rome, Sammarra, and Biggiero (2008)
find that knowledge exchange includes technological,
market, and managerial knowledge. This finding chal-
lenges the usual emphasis on the exchanges of technical
knowledge (Munari et al. 2011). No study, however, has
explored the types of knowledge exchanged relating to
climate change. Advancing understanding of this aspect is
important because knowledge is not unidimensional nor are
firms expected to be limited in the types of knowledge they
exchange (Sammarra and Biggiero 2008).
The final aspect relates to so-called ‘‘extra-cluster’’
knowledge (Giuliani and Bell 2005). Too often the cluster
literature focuses analysis exclusively on inter-firm
knowledge exchange, but other scholars argue that firms
acquire knowledge from various sources beyond firms
within the cluster (Amin and Cohendet 2004; Malmberg
2003). In their study of 28 firms in a regional Chilean wine
cluster, Giuliani and Bell (2005) find that at least some
firms in the cluster not only engage in inter-firm cluster
knowledge exchanges, but acquire technical knowledge
from universities, suppliers, consultants, and business
associations. In the present study, a hypothesis is developed
that posits that wine firms in the regional cluster of interest
gain their most valuable knowledge about climate change
from peak national industry bodies.
The paper makes three contributions to the literature.
First, firms are expected to respond to climate change when
they are sufficiently informed and knowledgeable about the
Regional wine cluster (meso level)
Sub-cluster 1 knowledge exchange
(sub-meso level)
Sub-cluster 2 knowledge exchange
(sub-meso level)
Sub-cluster 4 knowledge exchange
(sub-meso level)
Sub-cluster 3 knowledge exchange
(sub-meso level)
internalexchange
externalexchange
internalexchange
internalexchange
externalexchange
internalexchange
externalexchange
externalexchange
The expectation is that wine sub-clusterswill develop a unique sense of identity that sees firms exchanging knowledge about climate change more readily within the sub-cluster as opposed to outside the sub-cluster
Fig. 1 Conceptualization of
knowledge exchange about
climate change in regional wine
lusters
J. Galbreath et al.
123
issue (Galbreath 2009). While research does demonstrate
that firms are making decisions to respond to climate
change, no studies have examined how they gain knowl-
edge to influence such decisions. Thus, the interest of this
study is not in the types of responses firms implement to
respond to climate change, but rather in the mechanisms or
means by which firms acquire knowledge about climate
change. Namely, this study examines inter-firm knowledge
exchanges. However, while regional clusters and underly-
ing cluster theory are taken into account, due to the nature
of the wine industry, the concept of ‘‘sub-clusters’’ is
explored. A sub-cluster is defined as a unique spatial
location within a regional wine-producing cluster. This
focuses attention on finer spatial elements of clusters,
determining if knowledge exchanges about climate change
more readily occur at the sub-cluster level (Fig. 1). This
level of analysis enables the influence of geography to be
further explored.
Second, studies on the types of knowledge exchanged in
clusters are underrepresented in the literature. This study
advances research in this area by exploring several ‘‘pub-
lic’’ and ‘‘private’’ knowledge types, determining if firms
exchange knowledge about climate change mainly through
‘‘public’’ knowledge types. Lastly, firm-level knowledge
exchange is prominent in cluster research. However,
knowledge can also be acquired from sources that are
external to firms in the cluster. This study examines several
sources of external knowledge to determine the main
source of knowledge within the cluster, thus advancing
research on extra-cluster sources of knowledge.
The paper proceeds as follows. First, background to the
research is presented, including a review of relevant
existing studies. Next, a set of research hypotheses are put
forth. This is followed by a description of the research
methods, after which the results are presented. The paper
concludes with a discussion and presentation of findings,
future research directions, and limitations.
Background
Climate Change and Wine
Wine grapes can be successfully grown in only a very
narrow geographical range. Suitable locations must have
particular climates, which are highly sensitive to changes
in climatic conditions (Keller 2010; Webb et al. 2010). For
example, as little as a 1 �C increase in average temperature
can dramatically affect where different varieties can best be
ripened and can potentially affects yield, quality and,
ultimately, economic sustainability (Jones et al. 2005;
Keller 2010). In extreme cases, entire vintages can be lost
if temperatures are too high (Fenner 2009). Hence, grape
growing and wine production are largely weather- and
climate-driven enterprises. Further, long-term changes in
climate can profoundly affect production viability, quality,
and wine styles, due to changes in winter-hardening
potential, frost occurrence, growth season lengths, and heat
accumulation (Webb et al. 2007). In addition, growing
premium qualities of specific grape varieties requires even
narrower ranges of climatic conditions, meaning that
variety-specific locations may be particularly vulnerable to
variations arising from climate change, such as more
extreme heat days, less rainfall, and increases in humidity.
In the wine industry, the evidence tends to suggest that
climate change is having an effect on the world’s main
production centers.
In a ground-breaking study of global temperature
changes, Jones et al. (2005) modeled climatic conditions in
27 of the most important wine regions in the world.
Studying cool, intermediate, warm, and hot climate
regions, the authors find that in 17 out of 27 regions
(63 %), growing season temperature averages rose between
1950 and 1999. Further, in 15 out of 27 regions (56 %),
dormant season temperature averages rose during the same
period. The majority of the rises were in US and European
wine regions, although, averaged across all regions, tem-
perature warming was 1.26 �C. Further, the researchers
calculate that temperatures are expected to rise by an
average of 2.04 �C by 2050 in the wine regions under
study. The evidence therefore suggests that climate change
poses a threat to many wine-producing regions in the
world. Further, recent evidence suggests that wine pro-
ducers are well aware of their reliance on climatic condi-
tions and eco-system services, and may act as stewards of
the natural environment, not only to ensure their own
sustainability, but to protect and care for the regions within
which they operate (Galbreath 2012). Therefore, what
mechanisms might facilitate how firms gain know-how and
information about climate change? One mechanism, and
the focus of this study, is cluster effects.
Cluster Theory
Cluster theory has become prominent in the exploration of
regional and national economies, economic growth and
development, and innovation (Martin and Sunley 2003;
Maskell 2001; Porter 1998, 2000; Rogers 1995). Growing
out of Marshall’s (1890) seminal work on industrial dis-
tricts, clusters are generally conceptualized as ‘‘a geo-
graphically proximate group of interconnected companies
and associated institutions in a particular field, linked by
commonalities and complementarities’’ (Porter 2000,
p. 16). Firms based in clusters often enjoy success rates
greater than non-clustered or isolated firms (Porter 1998).
Cluster theory suggests that success rates are mainly due to
Knowledge and the Climate Change Issue
123
interdependencies and a geographic proximity that expe-
dites the exchange of information and knowledge.
Researchers exploring cluster theory have devoted con-
siderable attention to studying the dynamics of well-known
clusters, such as technology firms in Silicon Valley and
Route 128 in the US (Saxenian 1994), wireless systems in
Scandinavia (Dahl and Pedersen 2004), textile and clothing
in Italy (Lazerson 1990), and motor sport in the UK (Henry
and Pinch 2001).
Most research on clusters pays special attention to
knowledge spillovers. Generally, a knowledge spillover is a
flow of knowledge between firms, which theory posits occurs
more frequently, and with greater affect, between firms that
are close to one another (Tallman et al. 2004). Knowledge
exchanges are critical because it is thought that these are a
key underlying mechanism that drives competitive advan-
tage, and economic growth and performance, in regional
clusters (Maskell 2001; Tallman et al. 2004). More specifi-
cally, a concentration of many firms working on a similar set
of problems often produces a widely shared understanding of
an industry and its workings, challenges, and opportunities.
A number of studies have documented the role of knowledge
exchanges in clusters, and their methodologies have inclu-
ded the study of patent data, and the use of surveys and
interviews (e.g., Dahl and Pedersen 2004; Saxenian 1994).
Other studies have sought a more in-depth analysis of
knowledge and clusters, by employing concepts such as
‘‘knowledge in the air’’. Yet, too often such studies poorly
identify the kinds of knowledge exchanged and why these
matter (Hervas-Oliver and Albors-Garrigos 2009; Huber
2012; Ibrahim et al. 2009). In their work, Tallman et al. (2004)
posit that there are essentially two types of knowledge char-
acteristics present in knowledge spillovers in clusters: com-
ponent knowledge (usually technical) and architectural
knowledge (usually organizational). Component knowledge
tends to be more explicit and ‘‘public’’, and is subject to
discovery and therefore more easily transferred. Architectural
knowledge relates more to organizational systems and tends
to be tacit and private, idiosyncratic knowledge in that it is
unique to a given firm and is more subject to mobility barriers.
From a cluster perspective, it is the mixture of the types
of knowledge that makes proximity important. While
explicit or public knowledge may be easily communicated,
such as through ICT because it can be written down, tacit
knowledge needs to be exchanged face-to-face, often
through the movement of skilled staff between firms. In
addition, informal groupings of practitioners within an
industry may exchange knowledge through communities of
practice which are based on face-to-face communication
and knowledge exchange (Brown and Duguid 2000). This
study seeks to examine both knowledge types, and to
understand the extent to which the exchange of each type
differs.
Hypotheses
Climate change impacts wine production more directly
than it does many other business sectors (Galbreath 2011a).
Understanding the impacts of climate change, therefore,
may be a key to the long-term survival and sustainability of
wine clusters. Given, climate change’s documented dis-
ruption of wine production (Webb et al. 2010), wine firms
in Australia could be expected to be exchanging knowledge
about climate change to stay informed about how climatic
conditions will impact production.
Research has documented the changing conditions in
some of Australia’s regional wine clusters due to climate
change (Galbreath 2011a; Webb et al. 2010). Of particular
importance to this study is the fact that Australia has fur-
ther delineated its regional wine clusters into distinctive
‘‘sub-clusters’’ specific to a given regional wine-producing
cluster. This has implications for knowledge exchanges
about climate change in the Australian wine industry.
Within the literature, while the geographic delineation of
clusters and the relations between different spatial scales
remains controversial (Martin and Sunley 2003), there is
generally agreement among scholars that clusters are ‘‘geo-
graphically proximate’’ (Porter 2000, p. 16)—although
‘‘proximity’’ is open to interpretation. In the context of this
study, a sub-cluster is a unique spatial location within a
regional wine-producing cluster (Fig. 1). For example, in
California, the largest regional wine-producing cluster in the
United States, there are 107 identified sub-clusters, with
Napa Valley and Sonoma Valley among the most well-
known.1 This finer spatial distinction is critical to the wine
industry as ‘‘place’’ or, as explained by the French, terroir,
describes the unique local geography of a vine’s entire nat-
ural environment: the combination of climate, topology,
geology and soil, all of which bear on the local environ-
ment’s growth and the characteristics of its grapes and wine
(Cross et al. 2011; Seguin and de Cortazar 2005).2
Of importance is the fact that a wine’s unique origin
conveys a message to buyers and consumers, and has sig-
nificant implications for branding, reputation, and price
(Cross et al. 2011). Given this place-based identity, which
appears to be increasingly linked to the sub-cluster rather
than the region (e.g. Napa Valley rather than California),
there is the possibility that inter-firm knowledge exchanges
within sub-clusters occur more naturally and frequently than
knowledge exchanges with firms in other sub-clusters within
a region. There are a few main reasons for this possibility.
1 Information on California’s sub-clusters available at http://www.
iwineinstitute.com/CALAVABYNAME.ASP.2 As a good example of sub-cluster climate effects, the Overberg,
Stellenbosch, and Paarl wine sub-clusters in South Africa experience
up to a 6 �C difference in temperature, even though there is as little as
a 40 km distance between them (Deloire et al. 2009).
J. Galbreath et al.
123
First, as wine sub-clusters increasingly compete on their
unique brand and reputation, one way this can be achieved
is through demonstration of its environmental management
credentials (including credentials related to climate
change). Building environmental credentials is predicated
on the acquisition of knowledge (Haugh and Talwar 2010).
Hence, as sub-clusters seek to differentiate themselves from
other sub-clusters (e.g., through strong environmental
management credentials), they would be expected to more
readily exchange knowledge about climate change within
their sub-cluster than with other sub-clusters. Second, there
is recognition that the exchange of knowledge is dependent
upon the location of expertise. The decision to seek new
knowledge from another is affected by awareness of that
source as a valuable reserve of relevant knowledge (Borg-
atti and Cross 2003). As individuals are likely to engage in
knowledge exchanges with others whose areas of expertise
are known to them, knowledge exchange is dependent upon
individuals’ knowing ‘‘who knows what’’ (Moreland et al.
1996). Evidence suggests that knowing ‘‘who knows what’’
is bound by geographic proximity (Uzzi 1996, 1999);
therefore, given their close proximity, the expectation is
that knowledge exchanges about climate change between
firms within a sub-cluster occur more readily than with firms
in other sub-clusters in the region. It is also expected that the
relevance of knowledge exchanged about the consequences
of climate change is higher within sub-clusters, where the
climatic and soil conditions are more homogenous than is
the case between different sub-clusters.
Clear distinctions of ‘‘place’’ appear to be emerging in the
Australian wine industry, in particular among sub-clusters
(Costley 2012; Schmitt 2013), and these distinctions could
impact the extent to which knowledge about climate change
is exchanged within a regional cluster. While the arguments
put forth do not discount the possibility of flows of knowl-
edge between sub-clusters, the expectation is that they will be
more evident within them. Hence:
Hypothesis 1 Knowledge exchange about climate change
is more widespread within wine sub-clusters than between
them.
Following Hypothesis 1, there are two aspects that
require further examination: the type of knowledge
exchanged and extra-cluster knowledge sources. Tallman
et al. (2004) argue that clusters thrive because of flows of
knowledge between firms in the cluster, which is exem-
plified in Maskell’s (2001) knowledge-based theory of the
geographical cluster. Because knowledge is argued to be
more freely shared in the cluster it is ‘‘part and parcel of the
social community—a public good for all members’’
(Tallman et al. 2004, p. 261). However, not all knowledge
has the same characteristics and therefore may be more or
less exchanged in clusters.
The resource-based view (RBV) of the firm suggests
that private knowledge, or knowledge that is idiosyncratic
to a given firm, is knowledge that is generally protected
and thus less readily transferred or exchanged (Barney
1991; Galbreath 2005). Examples include knowledge about
organizational processes, long-term strategies, and mana-
gerial routines (Teece et al. 1997). Such knowledge tends
to be tacit, is path-dependent, and specific to the firm.
Therefore, private knowledge is generally more difficult to
transfer (Tallman et al. 2004). This is because as firms seek
to build and establish competitive advantage, they might
protect private knowledge through legal property rights
(Galbreath 2005), or otherwise may be reluctant to share
within the cluster knowledge that they perceive to give
them a special or unique advantage.
Alternatively, cluster theory posits that explicit knowl-
edge, or knowledge that is generally technical in nature or
common across an industry, is freely exchanged between
firms (Munari et al. 2011). This is because explicit
knowledge is knowledge that is related to identifiable parts
of an organizational system, and tends to be more precisely
defined, documented, and communicated (Tallman et al.
2004). Examples include engineering knowledge based
upon specific scientific principles. In the case of wine,
explicit knowledge would include knowledge about
growing grapes or making wine. Explicit knowledge is
generally subject to discovery, relatively transparent, and
relatively mobile among firms who are informed and will
understand it once presented to them (Jenkins and Tallman
2010; Tallman et al. 2004).
Evidence suggests that, globally, technical and industry
knowledge (‘‘public’’ knowledge) in the wine industry
appears to be readily exchanged between firms (Giuliani
2007). In the case of the Australian wine industry, the
setting of this study, public knowledge is spread throughout
regional wine clusters (Aylward 2007a, b). National wine
peak bodies, for example, promote and educate members
about the technical and industry aspects of climate change.
On the other hand, little evidence demonstrates that private
knowledge is as freely flowing in or around wine clusters.
This might be due to the fact that any private knowledge
about climate change would be highly embedded within the
and subject to causal ambiguity.
Based on the above:
Hypothesis 2 ‘‘Public’’ knowledge about climate change
is more readily exchanged than ‘‘private’’ knowledge about
climate change in wine clusters.
Finally, according to Camagni (1991), Bell and Albu
(1999), and Giuliani and Bell (2005), in addition to inter-
firm knowledge exchanges, a cluster also has the capacity
to take advantage of so-called ‘‘extra-cluster’’ knowledge.
For example, in their study of a Chilean wine cluster,
Knowledge and the Climate Change Issue
123
Giuliani and Bell (2005) find that firms in the cluster
acquire technical knowledge from external sources,
including consultants, suppliers, and universities. While
some of these may be based within the cluster, many will
be located elsewhere, in major cities for example. In the
case of Australia, there is reason to believe the various
regional wine clusters would likely be acquiring knowl-
edge about climate change from extra-cluster sources.
More specially, Australia has a number of trade journals
that are read by the wine-producing community, including
Australian Journal of Grape and Wine Research, Australia
and New Zealand Grapegrower and Winemaker, Wine &
Viticulture Journal, and Winestate. In the past few years,
several articles on climate change have featured in these
journals (e.g., Galbreath 2011b; Hall and Jones 2010;
Webb et al. 2007). On the other hand, consultants, sup-
pliers to the industry, and universities would all be
expected to be sources of knowledge about climate change
that could be used by firms within regional wine clusters
(Giuliani and Bell 2005). However, given the structure of
Australia’s wine industry, one source would be expected to
be particularly useful to learn about climate change.
In Australia, peak bodies such as federations, regulators,
research agencies, and other intermediaries play a signifi-
cant role in the wine industry. All wine producers pay
levies to fund research and development, which includes
research and development related to climate change and the
natural environment. Industry knowledge is then dissemi-
nated by these various peak national industry bodies to
wine producers. Furthermore, EntWine, which is part of the
Winemakers’ Federation of Australia (a peak national
body), recently initiated and oversees the certification
process for the industry’s environmental management
system. EntWine offers training on environmental man-
agement and includes accountability for greenhouse gas
(GHG) emissions, while ensuring that technologies and
processes are in place to reduce GHG emissions prior to
awarding certification. Given the substantial influence of
peak national industry bodies on the wine industry in
Australia, the expectation is that they are the leading source
of extra-cluster knowledge about climate change. Hence:
Hypothesis 3 Considering extra-cluster sources of
knowledge, knowledge about climate change from peak
national industry bodies is the leading source.
Methods
Context
Australia is made up of several regional wine clusters
(Aylward 2007a, b). More specifically, most Australian
wine is produced in the regional clusters of New South
Wales, South Australia, Tasmania, Victoria, and Western
Australia. As an initial exploratory study of wine clusters,
Tasmania was chosen for this research project. Although
small by the rest of the country’s standards (producing just
over 7,000 tonnes of grapes in 2012—less than 1 % of
Australia’s overall crush), Tasmania enjoys a national and
international reputation as a producer of some of Austra-
lia’s leading premium wines, its Pinot Noir and sparkling
wines in particular winning high praise and trophies from
wine judges and critics alike. Further, after years of over-
production of wine and the effects of the global financial
crisis on the Australia wine industry, Tasmania has
emerged as one of the strongest wine regions in the country
and has clear competitive advantages and potential for
significant growth. Prices for Tasmanian grown wine
grapes are the highest in Australia and demand for its
grapes exceeds supply (100 % of wine produced is in the
super-premium and ultra-premium categories). At a time
when the Australian mainland wine industry is struggling
to cope with grape surpluses, brought about by loss of
market share in export and domestic markets, mainly for
generally lower-priced wines, the Tasmanian wine sector
remains buoyant.
Sample and Data Collection
The entire population of Tasmanian wine firms was
sourced from the Winetitles database, a directory of Aus-
tralian and New Zealand wine firms (Winetitles 2010). In
all, 97 firms were included. To collect data, a purpose-
designed questionnaire was created. The questionnaire was
discussed with a local wine trade organization in Tasmania,
who shared it with the technical committee to assess the
validity of its content. A few changes were suggested, most
of which were minor word changes. The questionnaire was
then mailed to all firms in an initial mailing, and a reminder
letter was sent 2 weeks later. Thereafter, a second reminder
letter was sent to non-respondents, along with an additional
questionnaire. Out of the 97 firms surveyed, 38 replied,
resulting in a response rate of nearly 40 %, which is out-
standing relative to most wine industry studies (Atkin et al.
2012; Sellitto 2006), and well above the typical response
rate (5–10 %) of direct mail surveys. To supplement the
main data, demographic information about each company
was collected from the Winetitles database. These demo-
graphics are presented in Table 1.
To test for non-response bias, early versus late respon-
dents were compared for the key demographic variables
used in the study. Chi square tests revealed no significant
differences between type of business (v2 = 2.46,
p = 0.48); business structure (v2 = 1.70, p = 0.43); type
of ownership (v2 = 3.16, p = 0.21); number of employees
J. Galbreath et al.
123
(v2 = 4.44, p = 0.22); and annual revenue (v2 = 2.06,
p = 0.56). Hence, non-response bias was not likely to be a
problem. Further, because the main variables of interest
were collected from a single source, a test for common
method bias was conducted. A Harman’s ex post single
factor test (Podsakoff and Organ 1986) revealed the
absence of a single general factor accounting for most of
the observed covariance in the variables. Hence, common
method bias did not appear to be a problem in this sample.
Measurement of Variables
In the context of this study, knowledge is defined as ‘‘that
which is known’’ (Grant 1996, p. 110). Knowledge can be
held by individuals or firms, and can be found in books,
journals, blueprints, manual, and the like (Grant 1996;
Inkpen and Dinur 1998; Liebeskind 1996). To measure
knowledge exchange about climate change, this study
relied on the procedure of Sammarra and Biggiero (2008).
Following their work, knowledge exchange about climate
change was conceptualized as a two-way flow, in which
knowledge can be exchanged from one firm in a sub-cluster
to another firm in that sub-cluster (or to firms in other sub-
clusters) and vice versa (Sammarra and Biggiero 2008).
However, the procedure differs from that of a typical net-
work analysis study: it entails an assessment from agent
(firm) to location (sub-cluster) rather than from agent to
agent. Hence, rather than create a roster listing all 97 firms,
a roster of the seven identified sub-clusters within Tas-
mania was listed.3
Respondents were then asked to consider the climate
change issue and the extent to which they had exchanged
any knowledge they possessed about climate change with
firms within their sub-cluster and with firms in other sub-
clusters. A four-point Likert scale was used to register
responses, which could range from ‘‘no knowledge
exchange’’ about climate change to ‘‘very high knowledge
exchange’’ about climate change with firms within their
sub-clusters and firms in other sub-clusters, but not with
any specific firm.4 These responses were mapped onto a
knowledge matrix, recording knowledge exchanges with
firms in other sub-clusters. The values of the cells in the
matrix range from cell ij = 0, indicating that a firm in sub-
cluster i exchanged no knowledge about climate change
with firms in sub-cluster j, to 3, indicating that a firm in
sub-cluster i exchanged a very high amount of knowledge
about climate change with firms in sub-cluster j.
As to the type of knowledge exchanged about climate
change, first, a categorization of knowledge types based on
a literature review was developed. Literature from inter-
national business, management, marketing, strategy, and
technology and innovation was consulted. The types of
knowledge identified were technical, industry, market,
organizational, marketing, and strategy knowledge, each of
which has been used in previous research (e.g., Boschma
and Ter Wal 2007; Kesidou et al. 2009; Sammarra and
Biggiero 2008). Next, each knowledge type was contex-
tualized for the issue of climate change (see Appendix 1).
For example, technical knowledge relates to insights on
technologies and technical enhancements for adapting to
climate change; industry knowledge relates to know-how
gained from peak national industry bodies or peers on
addressing sector requirements or government policies on
3 The seven sub-clusters include Coal River Valley, Derwent Valley,
East Coast, Huon/Channel, North West, Pipers River, and Tamar
Valley. This designation was determined by several factors, including
historical evolution of the region, categorizations by Wine Tasmania,
the industry association that oversees the affairs of Tasmanian wine
producers, and government classifications. Such sub-cluster designa-
tions are consistent with other wine-producing regions around the
world, including regions in Chile (Giuliani and Bell 2005), South
Africa (Deloire et al. 2009), and the United States (Cross et al. 2011).4 The reason for choosing a four-point scale was twofold. First, the
scale was used to get a sense of the intensity level of exchanges,
which follows the work of Giuliani and Bell (2005). Second, the
present study serves as the foundation for a larger national study;
therefore, scales were able to be assessed for validity and reliability
for future research efforts.
Table 1 Demographics
Sub-cluster
Coal River Valley 7
Derwent Valley 3
East Coast 6
Huon/Channel 4
North West 3
Pipers River 4
Tamar Valley 11
Type of business
Grape grower 11
Wine producer 2
Vertically-integrated 25
Ownership
Domestic 36
Foreign 2
Number of employees
Less than 5 29
5–9 3
10–19 3
30 or more 3
Annual revenue
Less than AUD$1M 31
AUD$1M–AUD$5M 5
AUD$6M–AUD$10M 1
More than AUD$10M 1
Knowledge and the Climate Change Issue
123
climate change; organizational knowledge relates to the
coordination and supervision of organizational resources
and processes to effectively and efficiently address climate
change impacts; and marketing knowledge relates to how
an individual firm addresses customer preferences, mar-
keting and branding, and new product development are
influenced by climate change.
Once knowledge types were contextualized, the list was
sent to four experts in the field of knowledge exchange and
clusters who reside in the United Kingdom and the United
States. After consultation, the four experts came to general
agreement upon the types of knowledge. Suggestions were
made to reword some of the examples for greater clarity
and content validity, and these were incorporated into the
final questionnaire. The respondents were asked to consider
any knowledge exchanges about climate change they had
made with other firms within Tasmania, assessing those
exchanges for each of the knowledge types (on a four-point
Likert scale as described above). Finally, after reviewing
the literature (e.g., Aylward 2007a, b; Giuliani 2004; Gi-
uliani and Bell 2005), a list of six key extra-clusters
sources of knowledge were identified; namely, peak
national industry bodies, institutions of higher education,
suppliers, consultants, trade journals, and wine firms
operating outside of the regional Tasmania wine cluster.
Respondents were asked to indicate if they had acquired
knowledge about climate change from each source, where
1 = yes and no = 0.
Results
Means, standard deviations, and correlations are presented
in Table 2. To examine Hypothesis 1, first, the proportion
of firms was calculated, by sub-cluster, reporting any level
of knowledge exchange to the total number of sub-clusters
in the sample (n = 7).5 The averaged proportion of
knowledge exchange across the sample is 0.31.6 The
intensity of knowledge exchange appears to be mixed.
More specifically, respondents were asked to rate the
intensity of knowledge exchanges about climate change
from 0 (‘‘no exchange’’) to 3 (‘‘very high exchange’’).
Taking into account knowledge exchanges across all sub-
clusters, for those not exchanging any knowledge (0), the
averaged proportion is 0.69. For very little exchange (1),
the averaged proportion is 0.15. For moderate exchange
(2), the averaged proportion is 0.11. For very high
exchange (3), the averaged proportion is 0.05. The results
suggest that, when examined across all sub-clusters, less
than half of the firms in the sample reported that they are
exchanging knowledge about climate change.
To test Hypothesis 1, that knowledge about climate
change is more widespread within sub-clusters than
between them, each responding firm was classified by its
corresponding sub-cluster, including their knowledge
exchange ratings. The proportion of exchange across each
sub-cluster was then calculated, using this value to create a
matrix for analysis in organizational risk analyzer (ORA),
Carnegie Mellon’s social network analysis software. Fig-
ure 2 demonstrates the results of the network analysis. As
can be seen, the network analysis graphically reveals
knowledge exchanges of firms in each sub-cluster (i.e., firm
to sub-cluster), and whether these exchanges are internal or
external to the sub-cluster.
To statistically compare differences, any level of
exchange by each firm within and between sub-clusters was
counted as a 1, 0 otherwise (i.e., a firm was assigned a 1 if
they had indicated any level of knowledge exchange based
on the Likert scale described above). The mean exchange
of firms within the sub-cluster (intra-exchange) was
examined relative to the mean of exchange with firms in
the other sub-clusters (inter-exchange). One-way analysis
of variance (ANOVA) tests were conducted to detect sta-
tistical differences. In all cases no statistically significant
differences were found (Coal River Valley, F = 0.741,
Table 2 Descriptives and correlations
Variable Mean SD 1 2 3 4
1. Sub-cluster
knowledge
exchange
0.64 0.77 1.00
2. Public
knowledge
exchange
0.82 0.71 0.55** 1.00
3. Private
knowledge
exchange
0.75 0.76 0.21 0.60** 1.00
4. Extra-cluster
knowledge
sources**
0.34 0.30 0.44** 0.54** 0.50** 1.00
** p = 0.01
5 To calculate proportions, a 36 9 7 matrix was created that
contained each individual firm and the seven sub-clusters. For any
given firm, if there was evidence of any level of exchange, either
within the sub-cluster or to other sub-clusters, this was counted as a 1.
Counts were then divided by the total number of firms within the sub-
cluster, which provided a proportion of exchanges. This process was
repeated for each sub-cluster to derive an average proportion of the
sub-cluster exchanges, which was then used to calculate an overall
averaged proportion for the whole sample. The process was repeated
again for each level of intensity of knowledge exchange.6 Individually, only two sub-clusters demonstrate knowledge
exchange proportions above 0.50 (Derwent Valley and East Coast).
That is, more than half of the firms in these two sub-clusters are
exchanging knowledge about climate change. As can be seen in
Appendix 2, Tasmania is a relatively isolated regional wine-produc-
ing cluster and within the region itself, sub-clusters are geographically
separated. Hence, within the Tasmanian wine region, any knowledge
exchanges among sub-clusters faces the issue of geographic distance.
J. Galbreath et al.
123
p = 0.620, Derwent Valley, F = 0.667, p = 0.678, East
Coast, F = 1.307, p = 0.280, Huon/Channel, F = 0.944,
p = 0.485, Pipers River, F = 0.667, p = 0.681, Tamar
Valley, F = 1.104, p = 0.369).7 The findings suggest that
knowledge exchange about climate change is not more
widespread internal to the sub-cluster with firms in other
sub-clusters; therefore, Hypothesis 1 does not find support.
Following the literature, Hypothesis 2 posited that
public knowledge exchange about climate change would
occur more readily than private knowledge exchanges.
Table 3 demonstrates the percentages of knowledge type
exchanges, by intensity level. Individually, and accounting
only for responses that indicate actual exchanges (i.e., a
response of 1, 2, or 3), industry knowledge (65.8 %) is the
most prominent type of knowledge exchanged on climate
change in this sample. This perhaps reflects the fact the
peak national industry bodies in Australia are investing
substantially in climate change research and in the dis-
semination of results to industry members. However, to test
differences between the means of each knowledge type, a
factor analysis of the knowledge types was conducted.
Coral River Valley = aDerwent Valley = bEast Coast = cHuon/ Channel =dNorth West = ePipers River = fTamar Valley = g
Isolates
Fig. 2 Network analysis (firm to sub-cluster exchanges). Line thickness represents intensity of knowledge exchange (very little, moderate, very
high)
7 Note: North West was not calculated as no exchanges were
indicated by these firms.
Knowledge and the Climate Change Issue
123
Factor analysis revealed two factors with Eigen values
greater than one, explaining 83 percent of the variance.
Varimax rotation demonstrated that technical, industry, and
market knowledge loaded on factor one (a = 0.88), which
was labeled ‘‘public’’ knowledge. Organizational, market-
ing, and strategy knowledge loaded on factor two
(a = 0.87), which was labeled ‘‘private’’ knowledge. The
mean for public knowledge exchange is 0.82 (SD = 0.71),
while for private knowledge exchange the mean is 0.75
(SD = 0.76). The resultant t test for the full sample indi-
cates that there is no significant difference between
exchanges of public and private knowledge (t = 0.721,
p = 0.475).
To further explore Hypothesis 2, differences in the
exchange of knowledge types were also conducted by
examining sub-clusters individually. Using t-tests to assess
the different knowledge types, there were no differences in
exchanges for Coal River Valley (t = 0.834, p = 0.436),
Derwent Valley (t = 1.000, p = 0.423), East Coast
(t = 1.168, p = 0.296), Huon/Channel (t = 1.000,
p = 0.391), Pipers River (t = 1.000, p = 0.500, and
Tamar Valley (t = 1.765, p = 0.110).8 Accounting for
both sets of tests, Hypothesis 2 does not find support.
Lastly, Hypothesis 3 seeks to determine if peak national
industry bodies are the primary source of extra-cluster
knowledge about climate change in wine clusters in Aus-
tralia. 47.2 % of the firms in the sample indicated that they
acquired knowledge about climate change from peak
national industry bodies, 19.4 % from institutions of higher
education, 8.3 % from suppliers, 16.7 % from consultants,
60.5 % from trade journals, and 8.6 % from wine firms
operating in regional clusters outside of Tasmania. To test
for differences, ‘‘yes’’ responses were coded one and ‘‘no’’
responses were coded zero. A Wilcoxon signed-rank test
was then used to compare the mean of peak national
industry bodies relative to all other sources. For institutions
of higher education the difference is significant (Z =
-2.887, p = 0.004); for suppliers the difference is signif-
icant (Z = -3.742, p = 0.000); for consultants the differ-
ence is significant (Z = -3.051, p = 0.002), and for wine
businesses outside of Tasmania the difference is also sig-
nificant (Z = -3.357, p = 0.001). However, for trade
journals, there is no statistically significant difference
(Z = -1.414, p = 0.157). Therefore, Hypothesis 3 is
partially supported.
Discussion
This is the first study, to the authors’ knowledge, that has
empirically explored clusters and the climate change
issue.9 Although exploratory—and given that wine pro-
duction is highly vulnerable to climatic changes—the
results therefore have implications that bear upon climate
change and cluster research. First, a knowledge perspective
is considered.
With respect to climate change, previous research
demonstrates that firms are responding to the issue through
both mitigative actions and adaptive actions (Galbreath
2011a, 2012). However, little is known about how firms
acquire knowledge about climate change in order to better
understand the issue. Following cluster theory, one way
firms are expected to achieve this is through knowledge
exchanges. Here, because of their geographic relatedness,
clusters develop strong collective identities (Porac and
Thomas 1995; Saxenian 1994), which give rise to a com-
munity consciousness that creates an environment for the
diffusion and sharing of knowledge about factors affecting
focal firms (Scott 1988). However, there is evidence to
suggest that within regional wine clusters in Australia (and
in other wine-producing countries as well), sub-clusters are
increasingly seeking to advance their own unique identities
within a given regional cluster, and that these identities are
increasingly critical to marketing and operational success,
as well as to their reputation (Aylward 2007b; Costley
2012; Cross et al. 2011; Schmitt 2013). Following this
shift, the present study posited that knowledge exchange
about climate change would, therefore, be more wide-
spread within sub-clusters than between them (Fig. 1).
Contrary to the hypothesis, the findings suggest that
knowledge exchange about climate change is not more
widespread within sub-clusters than between sub-clusters.
One explanation for this finding might be the way in which
wine production is affected by the climate. For example,
given wine’s dependence upon climatic conditions, the
natural environment, and eco-system services (Galbreath
Table 3 Type of knowledge exchange about climate change
Knowledge type Intensity of exchange (%)
No exchange Very little Moderate Very high
Technical 47.4 34.2 18.4 0
Industry 34.2 47.4 15.8 2.6
Market 42.1 28.9 28.9 0
Organizational 50.0 34.2 10.5 5.3
Marketing 44.7 31.6 21.1 2.6
Strategy 47.4 34.2 15.8 2.6
8 Note: North West was not calculated as no exchanges were
indicated by these firms.
9 For a related exception, see Etzion and McMahon (2012). They
study the environmental performance of industry clusters. However,
their study is not exclusive to climate change.
J. Galbreath et al.
123
2011a), in any sub-cluster, a firm’s knowledge about cli-
mate change might be equally applicable to a firm in
another sub-cluster in the same regional cluster—regard-
less of either firm’s precise location. Where this is the case,
barriers to knowledge spillovers would be lessened.
Another possible explanation for the finding might be the
easing of barriers of geographic proximity. For example,
economists interpret knowledge exchanges in clusters as
being consequent to geographic proximity (Porter 1998,
2000). Such proximity is described in terms of physical or
spatial proximity and is linked to knowledge exchanges
through its facilitation of face-to-face interaction. Simi-
larly, temporary geographic proximity has been posited as
a viable alternative to that of locations that are defined
exclusively by geography, so that, for example, meetings,
visits, or temporary colocation facilitate knowledge
exchanges (Torre 2008). However, with the advent of the
internet, social media, Skype, and other modern telecom-
munications tools, the possibility exists of technologically-
mediated knowledge exchanges. While shared communi-
ties and collective identities are still expected to be an
outworking of geographic proximity, technology reduces
physical barriers, and therefore offers a possible explana-
tion for why no differences were found between knowledge
exchanges internal to sub-clusters and those external to
sub-clusters.
Second, there is evidence to suggest that technical and
industry knowledge have become pervasive in the
knowledge exchanges of wine clusters in Australia and
around the world (Aylward 2007a, b; Giuliani and Bell
2005). However, little is known about whether firms in
clusters exchange knowledge beyond that which is tech-
nical or industry-related (Sammarra and Biggiero 2008).
This study finds that firms appear to be exchanging
knowledge about climate change by exchanging both
public and private knowledge. This might be due to per-
sonal, or relational, proximities of the sub-clusters, rather
than geographic proximities. Personal, or relational,
proximity is important to a regional clusters’ exchange of
explicit knowledge (Burt 1992; Hutchins 1991). Another
possible explanation for the lack of difference in the types
of knowledge exchanged might be the fact that private
knowledge about climate change is ‘‘similar’’ (Jenkins and
Tallman 2010), in the sense that firms in sub-clusters in
Tasmania might more willingly exchange private knowl-
edge about climate change because they face similar
conditions with respect to their need to gain as much
know-how and information on the issue, given its criti-
cality to wine production.
Hence, because of both relational and spatial proximi-
ties, ties between firms are likely to become personally
embedded (Knoben and Oerlermans 2006). As this occurs
in a regional cluster, firms develop trust between one
another, based on friendship or kinship, which encom-
passes emotional bonds and relationship-based commit-
ment (Boschma 2005). Under these conditions, while a
given firm’s private knowledge about climate change might
not become a widespread ‘‘public good’’ in the regional
cluster, it might explain why there are no differences
between the level of exchange of public and private
knowledge in the sample. That is, personal proximity and
trust-based social interactions could be one possible
explanation for why knowledge exchange about climate
change is similarly reflected in both public and private
knowledge exchanges (cf. Jenkins and Tallman 2010;
Tallman et al. 2004).
Lastly, despite the focus and emphasis of inter-firm
knowledge exchanges in clusters, some scholars have
stressed the importance of so-called extra-cluster sources
of knowledge, since the mere reliance on localized
knowledge of firms can result in entropy of the cluster
that remains locked-into an increasingly obsolete knowl-
edge base (Camagni 1991). This study finds that firms in
the sample are acquiring knowledge about climate change
from extra-cluster sources, particularly peak national
industry bodies and trade journals. The results confirm
previous studies (e.g., Giuliani and Bell 2005), suggesting
that the cluster as a knowledge system is not merely
influenced by the spatial and relational confines of firms
within the region, but instead is a complex system of
internal and external knowledge exchange and
acquisition.
Conclusion, Future Research Directions,
and Limitations
Little research has examined how firms in the wine industry
acquire knowledge so that they gain an understanding of
climate change and its impacts. This study explored spe-
cific cluster and extra-cluster effects. The findings suggest
that firms appear to be acquiring knowledge about climate
change through both types of effects. Even though less than
half of the firms in the sample are exchanging knowledge
about climate change, exchanges are nonetheless occur-
ring. But, contrary to this study’s prediction, these
exchanges are not mainly confined to sub-clusters. Firms
also appear to be exchanging knowledge about climate
change through the exchange of a variety of knowledge
types, including knowledge that is considered private and
firm-specific. Following the arguments of some scholars,
the results also suggest that firms are acquiring knowledge
about climate change from knowledge sources outside of
member embedded firms. These findings point to future
research opportunities.
Knowledge and the Climate Change Issue
123
First, future studies could use knowledge exchanges to
explore the nature of knowledge about climate change,
seeking to better understand the personal dimensions of
knowledge exchange across a regional cluster. Of partic-
ular interest might the philosophic or moral position of
actors (Markowitz and Shariff 2012) in the regional cluster
and whether or not this affects their sense of obligation to
exchange knowledge about climate change regardless of
their position spatially. Along these lines, climate change
has been acknowledged as a ‘‘great moral issue’’ (Carrell
2012; Moore and Nelson 2010). For business ethicists and
researchers with an interest in corporate social responsi-
bility and sustainability, the study of clusters could be a
fruitful avenue for future research, as there is some evi-
dence to suggest that clustered firms demonstrate higher
levels of environmental performance than non-clustered
firms (Etzion and McMahon 2012), that clusters might
possess deeply held traditions about the business–society
contract and the role of responsibility (Marquis 2003), and
that clusters might hold highly dominant values, such as a
value for environmental stewardship (Russo and Earle
2010). A better understanding of the role that clusters play
in these areas is needed.
Second, future research could further study how clus-
ters are influenced by the exchange of private, idiosyn-
cratic knowledge related to climate change and how
relational, rather than spatial, proximity might affect such
exchanges. According to Lounsbury (2007), knowledge
exchange is fundamentally shaped by cultural dynamics
that characterize specific communities, such as clusters.
Further understanding is therefore needed to determine
how such cultural dynamics could lead to an array of
knowledge exchanges between firms in clusters (Mitchell
et al. 2010), including path dependent, firm-specific
knowledge. Lastly, future research could further examine
the role of extra-cluster sources of knowledge, determin-
ing if there are circumstances in which such knowledge
sources dominate knowledge acquisition within clusters.
Such research could support those scholars who claim that
the advantages of clusters, via inter-firm knowledge
exchange, are less than received theory predicts (Huber
2012).
This study has limitations. First, the sample size is rel-
atively small. In light of this small sample, the results are
tentative at this stage, and should be interpreted with
caution. However, research on climate change in the
management literature is nascent, and scholars claim that
significantly more studies are needed to examine this
important—if not contested—topic (Ansari et al. 2011;
Goodall 2008). The present study is the first known
examination of the climate change issue in a cluster setting,
and thus serves as a foundation for future research. Second,
data on the main variables of interest were collected
through a single source. This has the potential to introduce
common method bias. Yet, a Harman’s ex post single
factor test (Podsakoff and Organ 1986) revealed the
absence of a single general factor accounting for most of
the observed covariance in the variables, indicating that
common method bias was likely minimal. Third, this study
investigated a single regional cluster, therefore generaliz-
ability is limited. However, the Tasmanian wine cluster is
increasingly seen as important to the future growth of
Australia’s wine production, for domestic consumption and
for export. Hence, it is a good setting, given the Australian
wine industry’s concern over the impacts of climate
change, both in economic and environmental terms (Rus-
sell and Battaglene 2005, 2007). Lastly, that specific
mechanisms that facilitate knowledge exchange were not
studied is a limitation. Thus, while modern communica-
tions tools such as the Internet and other electronic means
could act as facilitators, this study relied on economic
geographers’ interpretation of knowledge exchanges in
clusters as being consequent to geographic proximity
(Porter 1998, 2000). This perspective links knowledge
exchanges through its facilitation of face-to-face
interaction.
Acknowledgments This research was supported by a Linkage Grant
from Curtin Business School, Curtin University.
Appendix 1: Knowledge Type Items Used
in the Questionnaire
‘‘Public’’ Knowledge
(1) Technical knowledge Insight on technologies, tech-
nical enhancements, vineyard, and/or winery tech-
niques that relate to climate change.
(2) Industry knowledge Know-how gained from peak
industry bodies, specialist sources, or employees/
peers on addressing industry requirements or govern-
ment policies on climate change.
(3) Market knowledge Knowledge about the size of
opportunity for consumer markets sensitive to pro-
ducers’ environmental credentials, how competitors
are responding to climate change, impacts of climate
change on grape yield, quality, and price.
‘‘Private’’ Knowledge
(1) Organisational knowledge How your company has
coordinated and supervised organizational resources
and processes so that climate change impacts are
addressed efficiently and effectively.
J. Galbreath et al.
123
(2) Marketing knowledge How your company specifically
addresses customer preferences, marketing and brand-
ing, and new product development as they relate to
any climate change requirements.
(3) Strategy knowledge Insight on your company’s strat-
egy, planned competitive moves, long-term business
plans, and ability to manage change related to climate
change.
Appendix 2: Geographic Maps of Wine Production
See Figs. 3, 4 and 5.
Fig. 3 Global wine regions
(colored areas)
Fig. 4 Australian wine regions (colored areas) Fig. 5 Tasmanian wine sub-clusters
Knowledge and the Climate Change Issue
123
References
Amin, A., & Cohendet, P. (2004). Architectures of knowledge. Firms,
capabilities and communities. Oxford: Oxford University Press.
Ansari, S., Gray, B., & Wijen, F. (2011). Fiddling while the ice melts?
How organizational scholars can take a more active role in the
climate change debate. Strategic Organization, 9, 70–76.
Atkin, T., Gilinsky, A., Jr, & Newton,S.K. (2012). Environmental strategy:
Does it lead to competitive advantage in the US wine industry?
International Journal of Wine Business Research, 24, 115–133.
Aylward, D. (2007a). Innovation and inertia: The emerging disloca-
tion of imperatives within the Australia wine industry. Interna-
tional Journal of Technology and Globalization, 3, 246–262.
Aylward, D. (2007b). Fault lines: Emerging domains of inertia within
the Australian wine industry. Prometheus, 25, 85–97.
Barney, J. B. (1991). Firm resources and sustained competitive
advantage. Journal of Management, 17, 99–120.
Bell, M., & Albu, M. (1999). Knowledge systems and technological
dynamism in industrial clusters in developing countries. World
Development, 27, 1715–1734.
Borgatti, S. P., & Cross, R. (2003). A relational view in social
networks. Management Science, 49, 432–445.
Boschma, R. A. (2005). Proximity and innovation: A critical
assessment. Regional Studies, 39, 61–74.
Boschma, R. A., & Ter Wal, A. L. J. (2007). Knowledge networks
and innovative performance in an industrial district: The case of
a footwear district in the south of Italy. Industry and Innovation,
14, 177–199.
Brown, J. S., & Duguid, P. (2000). The social life of information.
Boston: Harvard Business School Press.
Burt, R. S. (1992). The social structure of competition. In N. Nohria
& R. G. Eccles (Eds.), Network and organizations (pp. 57–91).
Boston: Harvard Business School Press.
Camagni, R. (1991). Local milieu, uncertainty and innovation
networks: Towards a new dynamic theory of economic space.
In R. Camagni (Ed.), Innovation networks spatial perspectives
(pp. 121–142). London: Belhaven Press.
Carrell, S. (2012). Climate change ‘a moral issue’. Retrieved 23
January, 2013, at http://dawn.com/2012/04/09/climate-change-a-
moral-issue.
Costley, D. (2012). Wine regions to dig deep to promote unique
identity. Australian & New Zealand Grapegrower & Winemaker,
579, 67–68.
Cross, R., Plantinga, A. J., & Stavins, R. N. (2011). The value of
terroir: Hedonic estimation of vineyard sales prices. Journal of
Wine Economics, 6, 1–14.
Dahl, M. S., & Pedersen, C. O. R. (2004). Knowledge flows through
informal contacts in industrial clusters: Myth or reality?
Research Policy, 33, 1673–1686.
Dawkins, C., & Fraas, J. W. (2011). Coming clean: The impact of
environmental performance and visibility on corporate climate
change disclosure. Journal of Business Ethics, 100, 303–322.
Deloire, A., Howell, C., Habets, I., Botes, M. P., Van Rensburg, P.,
Bonnardot, V., & Lambrechts, M. (2009). Preliminary results on
the effect of temperature on Sauvignon blanc (Vitis vinifera L.)
berry ripening. Comparison between different macro climate
wine regions of the Western Cape Coastal area of South Africa.
In 32nd conference of the South African Society for Enology and
Viticulture, Cape Town, 27–30 July.
Eberlein, B., & Matten, D. (2009). Business responses to climate change
regulation in Canada and Germany: Lessons for MNCs from
emerging economies. Journal of Business Ethics, 86, 241–255.
Etzion, D., & McMahon, K. (2012). Industry clusters and environ-
mental performance. Paper presented at the 72nd annualmeeting of the academy of management, Boston.
Fenner, R. (2009). Foster’s turns to Tempranillo as climate change
bakes vineyards. Retrieved 15 November, 2012, at http://www.
bloomberg.com/apps/news?pid=20670001&sid=abcUGST60ZFM.
Galbreath, J. (2005).Which resourcesmatter tofirmsuccess?Anexploratory
study of resource-based theory. Technovation, 25, 979–987.
Galbreath, J. (2009). Addressing sustainability: A strategy develop-
ment framework. International Journal of Sustainable Strategic
Management, 1, 303–319.
Galbreath, J. (2011a). To what extent is business responding to
climate change? Evidence from a global wine producer. Journal
of Business Ethics, 104, 421–432.
Galbreath, J. (2011b). Margaret River study explores climate change
response. Australian & New Zealand Grapegrower & Wine-
maker, 565, 54–56.
Galbreath, J. (2012). Climate change response: Evidence from the
Margaret River wine region of Australia. Business Strategy and
the Environment, in press.
Giuliani, E. (2004). Laggard clusters and slow learners, emerging
clusters as locus of knowledge cohesion (and exclusion): A
comparative study in the wine industry. Working paper. Labo-
ratory of Economics and Management, Sant’Anna School of
Advanced Studies, Pisa.
Giuliani, E. (2007). The wine industry: Persistence of tacit knowledge
or increased codification? Some implications for catching-up
countries. International Journal of Technology and Globaliza-
tion, 3, 138–154.
Giuliani, E., & Bell, M. (2005). The micro-determinants of meso-
level learning and innovation: Evidence from a Chilean wine
cluster. Research Policy, 34, 47–68.
Goodall, A. H. (2008). Why have the leading journals in management
(and other social sciences) failed to respond to climate change?
Journal of Management Inquiry, 17, 408–420.
Grant, R. M. (1996). Toward a knowledge-based theory of the firm.
Strategic Management Journal, 17, 109–122.
Hall, A., & Jones, G. V. (2010). Spatial analysis of climate in
winegrape-growing regions in Australia. Australian Journal of
Grape and Wine Research, 16, 389–404.
Haugh, H. M., & Talwar, A. (2010). How do corporations embed
sustainability across the corporation? The Academy of Manage-
ment Learning and Education, 9, 384–396.
Henry, N., & Pinch, S. (2001). Neo-Marshallian nodes, institutional
thickness, and Britain’s ‘Motor Sport Valley’: Thick or thin?
Environment and Planning, 33, 1169–1183.
Hervas-Oliver, J.-L., & Albors-Garrigos, J. (2009). The role of the
firm’s internal and relational capabilities in clusters: When
distance and embeddedness are not enough to explain innova-
tion. Journal of Economic Geography, 9, 263–283.
Hoffman, A. J., & Forbes, M. (2011). The culture and discourse of
climate skepticism. Strategic Organization, 9, 77–84.
Huber, F. (2012). Do clusters really matter for innovation practices in
Information Technology? Questioning the significance of tech-
nological knowledge spillovers. Journal of Economic Geogra-
phy, 12, 107–126.
Hutchins, E. (1991). Organizing work by adaptation. Organization
Science, 2, 14–29.
Ibrahim, S. E., Fallah, M. H., & Reilly, R. R. (2009). Localized
sources of knowledge and the effect of knowledge spillovers: An
empirical study of investors in the telecommunications industry.
Journal of Economic Geography, 9, 405–431.
Inkpen, A. C., & Dinur, A. (1998). Knowledge management pro-
cesses and international joint ventures. Organization Science, 9,
454–468.
Jenkins, M., & Tallman, S. (2010). The shifting geography of
competitive advantage: Clusters, networks and firms. Journal of
Economic Geography, 10, 599–618.
J. Galbreath et al.
123
Jones, G. V., White, M. A., Cooper, O. R., & Storchmann, K. (2005).
Climate change and global wine quality. Climatic Change, 73,
319–343.
Keller, M. (2010). Managing grapevines to optimize fruit develop-
ment in a challenging environment: A climate change primer for
viticulturists. Australian Journal of Grape and Wine Research,
16, 56–69.
Kesidou, E., Caniels, M. C. J., & Romjin, H. A. (2009). Local knowledge
spillovers and development: An exploration of the software cluster
in Uruguay. Industry and Innovation, 16, 247–272.
Knight, E. R. W. (2011). The economic geography of European
carbon market trading. Journal of Economic Geography, 11,
817–841.
Knoben, J., & Oerlermans, L. A. G. (2006). Proximity and inter-
organizational collaboration: A literature review. International
Journal of Management Reviews, 8, 71–89.
Lazerson, M. H. (1990). Subcontracting in the Modena knitwear
industry. In F. Pyke, G. Becattini, & W. Sengenberger (Eds.),
Industrial districts and inter-firm co-operation in Italy. Geneva:
International Institute for Labor Studies.
Le Menestrel, M., van den Hove, S., & de Bettignies, H.-C. (2002).
Processes and consequences in business ethical dilemmas: The
oil industry and climate change. Journal of Business Ethics, 41,
251–266.
Liebeskind, J. P. (1996). Knowledge, strategy, and the theory of the
firm. Strategic Management Journal, 17, 93–107.
Lounsbury, M. (2007). A tale of two cities: Competing logics and
practice variation in the professionalizing of mutual funds.
Academy of Management Journal, 50, 289–307.
Malmberg, A. (2003). Beyond the cluster—local milieus and global
economic connections. In J. Peck & H. W. C. Yeung (Eds.),
Remaking the global economy (pp. 145–159). London: Sage.
Markowitz, E. M., & Shariff, A. F. (2012). Climate change and moral
judgement. Nature Climate Change, 2, 243–247.
Marquis, C. (2003). The pressure of the past: Network imprinting in
intercorporate communities. Administrative Science Quarterly,
48, 655–689.
Marshall, A. (1890). Principles of economics. London: Macmillan.
Martin, R., & Sunley, R. (2003). Deconstructing clusters: Chaotic concept
or policy panacea? Journal of Economic Geography, 3, 5–35.
Maskell, P. (2001). Towards a knowledge-based theory of the
geographical cluster. Industrial and Corporate Change, 10,
921–943.
Mitchell, R., Burgess, J., & Waterhouse, J. (2010). Proximity and
knowledge sharing in clustered firms. International Journal of
Globalization and Small Business, 4, 5–24.
Moore, K. D., & Nelson, M. P. (Eds.). (2010). Moral ground: Ethical
action for a planet in peril. Deerfield, IL: Trinity University Press.
Moreland, R. L., Argote, L., & Krishnan, R. (1996). Socially shared
cognition at work: Transactive memory and group performance.
In J. L. Nye & A. M. Brower (Eds.), What’s social about social
cognition? Research on socially shared cognition in small
groups (pp. 57–84). New York: Sage.
Munari, F., Sobrero, M., & Malipiero, A. (2011). Absorptive capacity
and localized spillovers: Focal firms as technological gatekeep-
ers in industrial districts. Industrial and Corporate Change, in
press.
Nicholas, K. A., & Durham, W. H. (2012). Farm-scale adaptation and
vulnerability to environmental stresses: Insights from winegrowing
in Northern California. Global Environmental Change, 22, 483–494.
Podsakoff, P. M., & Organ, D. W. (1986). Self reports in organiza-
tional research: Problems and prospects. Journal of Manage-
ment, 12, 531–544.
Porac, J., & Thomas, H. (1995). Rivalry and the industry model of
Scottish knitwear producers. Administrative Science Quarterly,
40, 203–227.
Porter, M. E. (1998). Clusters and the new economics of competition.
Harvard Business Review, 76, 77–90.
Porter, M. E. (2000). Location, competition and economic develop-
ment: Local clusters in a global economy. Economic Develop-
ment Quarterly, 14, 15–34.
Porter, M. E., & Bond, G. C. (2008). The California wine cluster.
Harvard Business School Case 9-799-124.
Rogers, E. M. (1995). Diffusions of innovation (4th ed.). New York:
The Free Press.
Russell, A., & Battaglene, T. (2005). Oiling the chain: Trends in
environmental assurances in the European market. Adelaide,
SA: Winemakers’ Federation of Australia.
Russell, A., & Battaglene, T. (2007). Trends in environmental
assurance in key Australian wine export markets. Adelaide, SA:
Winemakers’ Federation of Australia.
Russo, M. V., & Earle, A. G. (2010). The geography of sustainable
enterprise and the concentration of mission-driven companies.
Paper presented at the 2010 academy of management confer-
ence, Montreal.
Sammarra, A., & Biggiero, L. (2008). Heterogeneity and specificity of
intern-firm knowledge flows in innovation networks. Journal of
Management Studies, 45, 800–829.
Saxenian, A.-L. (1994). Regional advantage: Culture and competition
in Silicon Valley and Route 128. Cambridge, MA: Harvard
University Press.
Schmitt, P. (2013). Aussie wine trends: 7. Sub-regional recognition.
Retrieved 24 February, 2013, at http://www.thedrinksbusiness.
com/2013/01/aussie-wine-trends-7-sub-regional-recognition.
Scott, A. J. (1988). New industrial spaces. London: Pion Limited.
Seguin, B., & de Cortazar, I. G. (2005). Climate warming: Conse-
quences for viticulture and the notion of ‘terroirs’ in Europe.
Acta Horticulture, 689, 61–71.
Sellitto, C. (2006). Improving winery survey response rates: Lessons
from the Australian wine industry. International Journal of Wine
Marketing, 18, 150–152.
Tallman, S., Jenkins, M., Henry, N., & Pinch, S. (2004). Knowledge,
clusters, and competitive advantage. Academy of Management
Review, 29, 258–271.
Teece, D. J., Pisano, G., & Shuen, A. (1997). Dynamic capabilities
and strategic management. Strategic Management Journal, 18,
509–533.
Torre, A. (2008). On the role played by temporary geographical
proximity in knowledge transmission. Regional Studies, 42,
869–889.
Uzzi, B. (1996). The sources and consequences of embeddedness for
the economic performance of organizations: The network effect.
American Sociological Review, 61, 674–698.
Uzzi, B. (1999). Embeddedness in the making of financial capital:
How social relations and networks benefit firms seeking
financing. American Sociological Review, 64, 481–505.
Webb, L. B., Whetton, P. H., & Barlow, E. W. R. (2007). Modeled
impact of future climate change on the phenology of winegrapes
in Australia. Australian Journal of Grape and Wine Research,
13, 165–175.
Webb, L. B., Whiting, J., Watt, A., Hill, T., Wigg, F., Dunn, G., et al.
(2010). Managing grapevines through severe heat: A survey of
growers after the 2009 summer heatwave in south-eastern
Australia. Journal of Wine Research, 21, 147–165.
Winetitles. (2010). The Australian and New Zealand wine industry
directory (28th ed.). Adelaide, SA: Winetitles.
Winn, M., Kirchgeorg, M., Griffiths, A., Linnenluecke, M. K., &
Gunther, E. (2011). Impacts from climate change on organiza-
tions: A conceptual foundation. Business Strategy and the
Environment, 20, 157–173.
Knowledge and the Climate Change Issue
123