Revista de economía mundial 67, 2024, 145-173
ISSN: 1576-0162
DOI: http://dx.doi.org/10.33776/rem.vi67.8089
Eco-InnovatIon In WorkEr coopEratIvEs and InvEstor-oWnEd
IndustrIal FIrms: a comparatIvE analysIs
Eco-innovación En coopErativas y EmprEsas dE capital
industrialEs: un análisis comparativo
Imanol Basterretxea
Universidad del País Vasco (UPV/EHU)
imanol.basterretxea@ehu.eus
Ana Fernández-Sainz
Universidad del País Vasco (UPV/EHU)
ana.fernandez@ehu.eus
Jorge Gutiérrez-Goiria
Universidad del País Vasco (UPV/EHU)
jorge.gutierrez@ehu.eus
Josu Santos-Larrazabal
Universidad del País Vasco (UPV/EHU)
josu.santos@ehu.eus
Recibido: diciembre 2023; aceptado: mayo 2024
abstract
The study examines eco-innovation in cooperatives and investor-owned
firms, analysing their primary driving factors. After evaluating responses
from 718 industrial establishments in the Basque Country, including 57
cooperatives, we conclude that cooperative principles do not guarantee
success in eco-innovation. The voluntariness of eco-innovation is no more
relevant in cooperatives than in other firms; instead, regulatory pressures
and market forces are the primary drivers. Despite facing greater limitations,
cooperatives achieve similar environmental benefits. The results reinforce the
importance of public policies for an effective ecological transition, and support
the need for a re-evaluation based on empirical evidence of certain postulates
in social economy literature.
Keywords: Eco-innovation, Innovation, Cooperatives, Ecological Transition.
rEsumEn
El estudio examina la ecoinnovación en cooperativas y empresas de
capital, analizando sus factores impulsores. Tras evaluar respuestas de 718
establecimientos industriales vascos, incluyendo 57 cooperativas, se concluye
que los principios cooperativos no aseguran el éxito en ecoinnovación. La
voluntariedad de la ecoinnovación no es más relevante en las cooperativas,
siendo las presiones regulatorias y fuerzas del mercado los principales
impulsores. A pesar de enfrentar mayores limitaciones, las cooperativas logran
beneficios medioambientales similares. Los resultados refuerzan la importancia
de las políticas públicas para una efectiva transición ecológica. Así mismo,
instan a reevaluar con evidencia empírica algunos postulados de la literatura
de la economía social.
Palabras clave: Ecoinnovación, Innovación, Cooperativas, Transición
Ecológica.
JEL Classification/ Clasificación JEL: J54; O25; O32
Revista de economía mundial 67, 2024, 145-173
1. IntroductIon
In response to several decades of globalisation, environmental sustainability
has become a central aspect among development issues. Rockstrom et al.
(2009) and subsequent studies such as those by the Stockholm Resilience
Centre show that planetary boundaries are being exceeded, demonstrating an
overall negative environmental trend.
Within this framework, the difficulties in combining economic and social
development with environmental sustainability are evident. In practice, the
countries with the highest rankings in the Human Development Index are also
the largest consumers of resources and generators of emissions per capita,
and the contradictions between economic growth and global development
objectives are becoming increasingly apparent (Hickel, 2019).
Thus, a transition towards other models of production and consumption is
inevitable, the question being how to address this issue fairly and based on a
vision of sustainability. The 2030 Agenda (UN, 2015) establishes in its SDG 12
the need to move towards sustainable consumption and production patterns.
Its goals make abundant references to resource and waste management, and
the adoption of sustainable business practices. In fact, SDG 9, linked to the
industry, stresses that innovation and technological progress is fundamental
for responding sustainably to economic and environmental challenges.
Given these shortcomings, eco-innovation presents itself as an interesting
tool to help reduce the use of resources, facilitate their recycling and reduce
pollution (García-Granero et al., 2018). However, eco-innovation is still a poorly
studied aspect, especially in the case of cooperatives, and warrants greater
attention from the field of research. Current literature defends an innate ‘green’
condition of cooperatives based on their values and principles. However, highly
cited and influential papers within this body of literature are purely theoretical
and lack any evidence supporting this assumption (see, for example, Mozas
and Bernal, 2006 or Puentes and Velasco, 2009) or they simply present
the link between cooperative principles and environmental concern as a
conjecture (Novkovic, 2008). When these papers are subsequently cited by
other researchers (see, for example, Fernández et al., 2020), they are often
referred to as previous evidence of a link between cooperative principles and
environmental performance rather than conjectures. The few empirical studies
that exist are based on agricultural cooperatives (Rabadan et al., 2021; Calle et
148 Imanol Basterretxea · Ana Fernández-Sainz ·Jorge Gutiérrez-Goiria · Josu Santos-Larrazabal
al., 2020; Carchano et al., 2023). Thus, further research is needed to contrast
the green innateness hypothesis.
Our study considers the role of cooperatives as part of the social economy,
and their possible contribution to eco-innovation as a means of promoting the
transitions necessary to address environmental matters.
The questions that guide this study are the following: Are industrial
cooperatives contributing to an improvement in environmental impacts? What
are the reasons that drive or limit these entities to eco-innovate? Are there
differences in the above aspects between cooperatives and other companies?
Can exposure to external markets be a relevant factor in this framework?
To answer these questions, the paper begins by explaining the framework
and concept of eco-innovation, analysing its background, and looking more
closely at eco-innovation in cooperatives. We then analyse data from the 2021
Innovation Survey carried out by the Basque Institute of Statistics on industrial
firms (with a methodology common to the Community Innovation Survey of
the European Commission). This is followed by a discussion of the results and,
lastly, the conclusions, limitations, and future lines of research.
2. Eco-InnovatIon In coopEratIvEs: lItEraturE FramEWork.
2.1. Eco-InnovatIon: dEFInItIon and FramEWork
The opportunity that innovation offers for achieving sustainable
development, or for reducing the environmental impact of economic activity, is
increasingly recognised both at institutional and academic levels.
The studies and initiatives within this framework include diverse
denominations, such as “eco-innovation”, “ecological innovation”, “green
innovation”, or “environmental innovation”, as reflected in various
bibliographical and general studies (Afeltra et al., 2023; Bossle et al., 2016;
Díaz-García et al., 2015; García Granero et al., 2018). A broader concept,
incorporating social aspects that go beyond environmental concerns, is that of
“sustainable innovation”, which has followed its own evolutionary path (Afeltra
et al., 2023).
Although the theoretical debate is still ongoing, in this study we adopt the
widely used term “eco-innovation”, which focuses on environmental impacts,
as this corresponds to the data we use in the empirical analysis. In 2007,
based on the OECD definition of innovation, Kemp and Pearson proposed a
commonly accepted definition of eco-innovation:
“the production, assimilation or exploitation of a product, production
process, service or management or business method that is novel to the
organisation (developing or adopting it) and which results, throughout
its life cycle, in a reduction of environmental risk, pollution and other
negative impacts of resources use (including energy use) compared to
relevant alternatives.” Kemp and Pearson (2007: 7)
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The definition includes a reduction in negative environmental consequences
as a result of these innovations. This requires a vision of new process and
product lifecycles, modifying management systems and leading to new
business models (OECD, 2009).
Along these lines, the European Commission launched the Eco-Innovation
Action Plan (EcoAP) in 2011, in which it defines eco-innovation as follows:
any form of innovation resulting in or aiming at significant and
demonstrable progress towards the goal of sustainable development,
through reducing impacts on the environment, enhancing resilience to
environmental pressures, or achieving a more efficient and responsible
use of natural resources.” (EC, 2011: 2)
Along with the need to reduce negative impacts as stated by the OECD, the
approach by EcoAP introduces sustainable development, resilience, and the
efficient use of resources as goals. More recently, the drive for eco-innovation
can be found in relevant European initiatives such as Horizon Europe or the
European Green Deal itself.
Eco-innovation has begun to attract more interest as a topic in the
innovation literature (Aboelmaged, 2018) and is recognised by the European
Union (EU) as an important contributor to green growth and sustainability
(Melece & Hazners, 2017).
The positive impact of eco-innovation on business sustainability has been
widely debated (He et al., 2018). In practice, eco-innovation can be associated
with reducing the use of water, materials or energy, with improvements related
to recycling or the use of less polluting materials, or with reducing pollution
in different ways. These environmental benefits can occur in different phases
of the production and consumption process, both within the company and
during consumption or use by the end user. Along these lines, eco-innovation
measurement studies cover areas as diverse as those related to products,
processes, organisational issues and marketing (García-Granero et al., 2018)
2.2. thE drIvErs For Eco-InnovatIon
Within the framework of eco-innovation, knowing the motivation for these
processes, and their drivers, is fundamental for promoting their implementation.
It is important, therefore, to distinguish between external and internal factors,
as pointed out in studies by Bossle et al. (2016). External factors include
regulatory and normative pressures (the latter related to legitimacy and
behaviour in accordance with the standards of their field of action), cooperation
(with suppliers, clients, etc.), expanding market, and the characteristics of
technology at industry level. Internal factors include efficiency, adoption of
certifications, environmental managerial concerns, environmental leadership,
culture and capability, as well as questions related to human resources and
skills.
150 Imanol Basterretxea · Ana Fernández-Sainz ·Jorge Gutiérrez-Goiria · Josu Santos-Larrazabal
Regulatory pressure appears as a predominant and essential driver of eco-
innovation (see Bossle et al., 2016, Horbach, 2016 and Afeltra et al., 2023,
for reviews). Specific regulatory backing is deemed essential for fostering eco-
innovation, since relying solely on the factors of technology push and market
pull is not enough (Afeltra et al., 2023). Besides actual regulations, expected
future regulations also have a significant positive effect on the development
of eco-innovations (Díaz-García et al., 2015). Current and future legislation is
highly correlated to certain eco-innovation results such as CO2 and pollution
reduction (Horbach, 2016). Aside from regulation, market demand is the
second most cited driver of eco-innovation (Doran & Ryan, 2012; Horbach et
al., 2012; Horbach, 2016; Díaz-García et al., 2015).
A significant variation among countries regarding their eco-regulation, the
enforcement of these regulations, technological development and demand for
eco-innovative products and services leads to divergent findings in studies that
link exports with eco-innovation.
For example, Horbach (2016) finds a negative effect of exports on eco-
innovation, particularly in relation to environmental benefits from the after-
sales use of products by end users. These results can be explained by the fact
that the firms in Horbach’s sample belong to the EU. The majority of their
exports go to other EU countries with a similar regulatory environment. The
remaining exports go to countries with lower regulatory requirements and a
weaker market pull for eco-friendly products. Along the same lines, Chiarvesio
et al. (2015) find that Italian firms engaged in export activities are less likely
to adopt eco-friendly practices, and Wang et al. (2020) also find a negative
impact of export diversification on CO2 emissions in G7 economies. For the
specific case of Spanish industrial firms, research offers contradictory results.
De Marchi (2012) finds that environmentally innovative firms are more likely
to export but, at the same time, serving an international market is significantly
and negatively correlated with green innovation. However, Torrecillas and
Fernández (2022), find a positive effect of exports on eco-innovation.
Conversely, studies in countries exporting their products to markets which
are leaders in ecological innovations find that export firms are positively
associated with cleaner production (see Galbreath et al., 2021, and Tsai and
Liao, 2017 for the case of Taiwan, or see Hanley and Semrau, 2022, for Eastern
Europe countries).
A number of studies of key factors affecting eco-innovation identify those
linked to normative pressures and the need for efficiency, such as cost reduction
(Demirel & Kesidou, 2011; Horbach, 2008, 2016; Horbach et al., 2012). Other
studies cite factors such as firm size, and sector or public financing (Bossle et
al., 2016).
Table 2 shows a summary of the drivers appearing in the survey we use for
our study. As can be seen, these are mainly external drivers.
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2.3. EnvIronmEntal pErFormancE and Eco-InnovatIon In coopEratIvEs
While specific literature on cooperatives and eco-innovation is limited
to a few studies (Rabadan et al., 2021; Calle et al., 2020; Carchano et al.,
2023), research is much more extensive on the environmental performance of
cooperatives (see Candemir et al., 2021 and Liang et al., 2023, for literature
reviews). Environmental issues are also analysed in a greater number of studies
on sustainability in cooperatives (see Lafont et al., 2023, for a literature review).
A common axis of this literature is that cooperatives are socially responsible
(and thus, greener) by nature. This innate condition implies that cooperatives
are inherently sustainable, since they are based on principles and values which
differ from capitalist enterprise models (Calle et al., 2020; Henrÿ, 2017). These
researchers often cite the “concern for community” cooperative principle as
the cornerstone of this innate greener condition. This principle states that
cooperatives work for the sustainable development of their communities
through policies approved by their members” (ICA, 2015, 86). In its guidance
notes on cooperative principles, the International Cooperative Association
explains its three-dimensional concern for sustainability (economic, social, and
environmental) and also adheres to the innate hypothesis: “It is hard-wired in
our genes. There is a clear and demonstrable advantage to cooperatives which
flows from the three-dimensional commitment to the sustainable development
of the communities in which cooperatives operate” (ICA, 2015, 93).
Some researchers highlight that other cooperative principles, such as
collective ownership and democratic governance, and values, such as mutual
help, responsibility, democracy, equality, equity and solidarity, make it
“reasonable to expect that cooperatives will move towards inclusive, sustainable,
and environmentally friendly growth models” (Carchano et al., 2023, 3). While
some of these principles and values could hypothetically have an impact on
eco-innovation in certain kinds of cooperatives (for example in green energy
cooperatives created by energy consumers with a greater concern for ecology),
it is difficult to see how they could significantly influence eco-innovation in
industrial cooperatives.
In fact, the literature that defends the innate greener condition of
cooperatives does so in a naïve way: cooperatives endorse the “concern for
community” principle, therefore they have greater concern for the environment
(Mozas and Bernal, 2006; Puentes and Velasco, 2009) or at least we conjecture
that they are likely to be concerned (Novkovic, 2008).
Evidence that supports the innate environmentally-friendly condition comes
solely from limited studies of Chinese agricultural cooperatives. According to
these studies, cooperative membership significantly improves the probability
of farmers adopting green control techniques (Yu et al., 2021; Zhang et al.,
2023); substantially influences farmers’ decisions to invest in organic soil
amendments (Ma et al., 2018; Dong et al., 2023); reduces the overuse of
chemical fertilizers and pesticides (Liu and Wu, 2022; Zhou et al., 2019); and
increases the adoption of water-saving irrigation technologies (Dong et al.,
152 Imanol Basterretxea · Ana Fernández-Sainz ·Jorge Gutiérrez-Goiria · Josu Santos-Larrazabal
2023). Furthermore, training and technical services provided by cooperatives
enhance farmers’ capacity and knowledge to adopt green technology (Zhang
et al., 2023; Luo et al., 2022). While most researchers find positive effects,
Abebaw and Haile (2013) find detrimental impacts on the environment of
belonging to an Ethiopian agricultural cooperative and Li et al. (2021) report
an insignificant relationship between cooperative membership and safe
production behaviours in the use of fertilizers and pesticides.
Despite the relevance of agricultural cooperatives all over the world, almost
all publications on their environmental performance are based on Chinese
samples. Furthermore, to the best of our knowledge, no research has been
conducted on other kinds of cooperatives, such as worker cooperatives.
When it comes to studies on eco-innovation and cooperatives, the scarce
research that exists again focuses on agricultural cooperatives of a single
country: Spain.
Calle et al. (2020) study 251 Spanish firms in the wine sector (51 of them
cooperatives) and find no significant differences between cooperative and
non-cooperative firms concerning their environmental behaviour. They also
find that the cooperatives are divided in their commitment to these issues.
Half of the cooperatives in their sample demonstrate a strong commitment to
environmental issues by prioritising them in their strategies and organisational
structure. However, a similar proportion of cooperatives adopt a preventive
environmental approach, considering potential environmental impacts, but
this approach does not shape their core business strategies.
Carchano et al. (2023) also focus their research on eco-innovation in
Spanish wine companies, with a sample of 239 firms, 53 of them cooperatives.
They find that cooperatives address the environmental concerns of internal
and external stakeholders to a greater degree and, consequently, they seem
to adopt a more proactive position on eco-innovation. Nevertheless, they do
not find support for the hypothesis of “being a cooperative moderates the
relationship between eco-innovation and environmental performance”.
Rabadán et al. (2021) analyse eco-innovation in a sample of 52 olive-oil
sector firms (42 of them cooperatives) and find that large olive oil cooperatives
producing high quality extra-virgin oil are the firms with greater involvement
in eco-innovation. These authors consider that, although being a cooperative
increases the likelihood of seeking greater eco-innovation, other causal
conditions unrelated to the cooperative nature of the firms explain these results
(large size, intense cooperation with stakeholders, high quality production, high
percentage of exports, high R&D budgets, etc.).
Departing from the broader concept of social economy, Rousselière et al.
(2024) find, based on a survey carried out on 16,000 European firms, that
social economy enterprises (defined as those with non-profit orientation
and those with collective ownership) have a higher probability of developing
environmental innovation.
Despite the optimist view of much of the literature on cooperatives and
environmental sustainability, given that eco-innovation is highly correlated
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with non-environmental innovation, it can be assumed that some limitations of
innovation seen in cooperatives will also be reflected in eco-innovation (Calle et
al., 2020). These limitations include slower decision-making due to democratic
processes, greater risk aversion among members compared to capitalist
owners, limited access to capital, and small organisational size (Basterretxea
and Martínez, 2012).
Drawing from this literature overview, the following hypotheses are
proposed:
H1: Being a cooperative has a positive and significant effect on eco-
innovation.
H2: Exports have a positive and significant effect on eco-innovation.
H3: Regulatory pressures and market pull are the main drivers of eco-
innovation.
H4: Voluntary initiatives for environmental good practice are more
important drivers of eco-innovation in cooperatives.
3. data and mEthodology
The analysis uses data from the 2021 Innovation Survey, carried out by the
Basque Institute of Statistics (Eustat, 2022). The survey questions are based
on the Community Innovation Survey (CIS) of the European Commission. Since
2008, the CIS questionnaire includes specific questions on eco-innovation
results and drivers, and defines eco-innovation as follows:
An innovation with environmental benefits is a new or improved
product or business process of an enterprise that generates positive
or lower negative environmental impacts, compared to the enterprise’s
previous products or processes, and that has been made available to
potential users or brought into use. The environmental benefit can
be the primary objective of the innovation or a by-product of other
objectives. The environmental benefits of an innovation can occur during
the production of a good or service, or during its consumption or use by
the end user.” (Eurostat, 2021)
The survey focuses on diverse business establishments across various
sectors and sizes in the Basque Country. The data pertain to the year 2021,
although specific inquiries on eco-innovation cover the 2019-2021 period.
The total sample of Eustat’s Innovation Survey includes 3,777 establishments
(196 of them worker cooperatives) in the services sector and industrial sector.
We decide not to use the total sample of 3,777 firms, focusing instead on just
industrial firms since it is easier to compare innovation drivers, practices and
outcomes in this more homogeneous sample of industrial firms.
The sample of our study encompasses 718 industrial establishments (57
of them are worker cooperatives). Within our sample, 7.94% of establishments
are affiliated with cooperative firms, contributing to 15.17% of the total
154 Imanol Basterretxea · Ana Fernández-Sainz ·Jorge Gutiérrez-Goiria · Josu Santos-Larrazabal
employment. This closely reflects the current proportion of cooperative
industrial employment in the Basque Country, which stands at 12.4%.
Consequently, our sample size is representative of the study universe.
Building on CIS’s definition and existing literature (Table 1), eco-innovation
is measured considering the outcomes of innovative endeavours. If innovations
generate favourable environmental impacts, they are classified as eco-
innovations. The firms were asked to respond to the following question:
“During the three years 2019 to 2021, did your enterprise introduce
innovations with any of the following environmental benefits and, if yes, was their
contribution to environmental protection rather significant or insignificant?”
Six variables measure environmental benefits within the firm and four
measure benefits from after-sales use of goods by the end user. These variables
are well-rooted in existing literature (see Table 1).
The questionnaire also asks about the importance of several factors in
driving the firm’s decision to introduce innovations with environmental benefits.
These drivers of eco-innovation, which mainly refer to external factors, are also
well-rooted in literature (see Table 2).
We include the dummy variable Coop to consider whether the entity is a
cooperative. In addition, we take into account the level of the establishment’s
spending on R&D, both internal and external (Int-RD and Ext-RD) or the use of
perceived public funding to innovate (Pub-aid). The size of the establishment’s
parent firm (Size) is also considered. The natural logarithm of the number
of employees, commonly utilised in studies of firm innovation performance,
is used as a proxy for firm size. The questionnaire details the percentage of
tablE 1: varIablEs mEasurIng EnvIronmEntal bEnEFIts and lItEraturE WhErE mEntIonEd
Variable Sources (examples)
Reduced material or water use per unit of output
(Material) Hellstrom (2007), Alkaya & Demirer (2015).
Reduced energy use or CO2 ‘footprint’ (CO2*)
Van Hemel & Cramer (2002), Alkaya & Demirer (2015),
Doran & Ryan (2016), Castellacci & Lie (2017), Rodrí-
guez & Wiengarten (2017).
Reduced soil, noise, water or air pollution (Pollution*) Rodríguez & Wiengarten (2017).
Replaced a share of materials with less polluting or
hazardous substitutes (Substitute)
Doran & Ryan (2016), Castellacci & Lie (2017), Rodrí-
guez & Wiengarten (2017).
Replaced a share of fossil energy with renewable energy
sources (Energy) Nesta et al. (2014).
Recycled waste, water, or materials for own use or sale
(Recycled)
Van Hemel & Cramer (2002), Doran & Ryan (2016),
Castellacci & Lie (2017), Rodríguez & Wiengarten
(2017).
Facilitated recycling of product after use (Recycled) Dalhammar (2015), Castellacci & Lie (2017), Rodríguez
& Wiengarten (2017).
Extended product life through longer-lasting, more
durable products (Product life)
Van Hemel & Cramer (2002), Hellström (2007), Dal-
hammar (2015).
Source: compiled by the authors (*CO2 and pollution reduction are gauged as benefits within the firm
and by the use of the end user)
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turnover coming from exportation, which allows us to analyse the effect of
exports on eco-innovation.
Given the connections between variables revealed in the literature review,
and since we propose that each eco-innovation is independent of the others,
we estimate a Probit model for each eco-innovation using Maximum Likelihood
method with robust standard errors to correct possible heteroscedasticity. The
endogenous variable is defined as Yi = 1, when the firm obtained environmental
benefits. The model is formulated as follows (Greene, 2012, pp. 732-736):
(1) Pr(Yi = 1) = F(Xi ‘β + Zi’ γ)
(2) Pr(Yi = 0) = 1- F(Xi ‘β + Zi’ γ)
Where: Yi is the dependent variable: environmental benefits.
Xi is the matrix of the explanatory variables.
Zi is the matrix of the control variables.
F( ) is the standard Normal Distribution.
It should be noted that the estimation parameters of the Probit model are
not the marginal effect. In general, the marginal effects are ∂Pr (Y=1)/∂X= f(Xi
‘β) β, and these values vary with the values of X (and Z). So, when interpreting
the estimated model, it is necessary to calculate the marginal effects at the
sample means of the data.
tablE 2: varIablEs mEasurIng drIvErs oF Eco-InnovatIon
Drivers Short name Sources (examples)
Existing environmental regulations Regulation
Demirel and Kesidou (2011), Horbach (2008), Horbach et
al. (2012), Li et al. (2020), Mahmood et al. (2022).
Existing environmental
taxes Taxes
Environmental regulations or
taxes expected in the future Future regulation
Need to meet requirements for
public procurement contracts Public contracts
Government grants,
subsidies or other financial
incentives for environmental
innovations
Subsidies Tsai and Liao (2017), Horbach (2016).
Current or expected market
demand for environmental in-
novations
Market Doran & Ryan (2016), Horbach et al. (2012), Horbach
(2016), Díaz-García et al. (2015).
Improving the enterprise’s
reputation Reputation
Li et al. (2020), Horbach (2016).
Voluntary actions or
initiatives for environmental good
practice within the sector
Voluntary
High costs of energy, water or
materials Costs Demirel & Kesidou (2011), Horbach (2008, 2016),
Horbach et al. (2012).
Source: compiled by the authors
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4. rEsults
4.1. dEscrIptIvE statIstIcs
As Table 3 shows, the percentage of industrial establishments that have
introduced innovations with environmental benefits is 21% higher among
cooperative firms than among investor-owned firms.
A similar scenario is seen when considering exports and size. Establishments
with some sort of environmental benefit from their innovation activities
exported more and were bigger than those without environmental benefits.
These differences are statistically significant.
tablE 3. charactErIsatIon oF thE samplE accordIng to Eco-InnovatIon practIcEs
Full Sample Cooperatives
Non-
cooperatives
Exports/turnover
(mean)
Employees
(mean)
Eco-innovative
establishments
54.32% 73.68% 52.65% 27.57% 105.55
Non eco-innovative
establishments
45.68% 26.32% 47.35% 19.47% 47.48
Total 100% 100% 100% 23.87% 79.03
Source: compiled by the authors. The differences are statistically significant.
FIgurE 1. pErcEntagE oF Eco-InnovatIvE EstablIshmEnts accordIng to Export IntEnsIty
Figure 1. Percentage of eco-innovative establishments according to
export intensity
Source: compiled by the authors
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Source: compiled by the authors
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When relating eco-innovation and export intensity, we find that the higher
the share of turnover exported by establishments, the higher the proportion
of these establishments that introduce eco-innovation. This trend is clearer in
the case of cooperatives, and all cooperatives that export more than 75% of
their production are in the group of eco-innovative establishments (Figure 1).
Figure 2 shows the differences between cooperatives and non-cooperative
firms, using just the subsample of establishments that have achieved some
environmental benefits within the enterprise, generated by innovation activities.
Looking at the trend seen in Table 3 in more detail, cooperatives show
better results in five out of the six measured environmental benefits, even if
differences are not statistically significant. The most important benefits for
both cooperatives and non-cooperative firms are ‘recycled waste, water, or
materials for own use or sale’ (16.30% of the total sample) and ‘reduced
energy use or CO2 footprint’ (12.95%).
In relation to the environmental benefits from after-sales use of products
by the end user (see Figure 3), cooperatives achieve better outcomes in two
out of four indicators; those of ‘extended product life through longer-lasting,
more durable products’ and ‘reduced soil, noise, water or air pollution’. Again,
the differences shown in Figure 3 are not significant.
Figure 4 shows the importance firms give to different aspects as drivers of
eco-innovation (the percentages have been calculated on the establishments
that have actually achieved some sort of environmental benefit from their
innovation activities).
FIgurE 2. EnvIronmEntal bEnEFIts WIthIn thE EntErprIsE
Figure 2. Environmental benefits within the enterprise
Source: compiled by the authors
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158 Imanol Basterretxea · Ana Fernández-Sainz ·Jorge Gutiérrez-Goiria · Josu Santos-Larrazabal
FIgurE 3. EnvIronmEntal bEnEFIts From aFtEr-salEs usE oF products by thE End usEr
Source: compiled by the authors
FIgurE 4. drIvErs to IntroducE InnovatIons WIth EnvIronmEntal bEnEFIts
Figure 4. Drivers to introduce innovations with environmental benefits
Source: compiled by the authors. Significance codes: *** 0.01; ** 0.05; * 0.1
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Source: compiled by the authors. Significance codes: *** 0.01; ** 0.05; * 0.1
159
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With regard to the total sample (including both cooperatives and non-
cooperatives), more than 70% of the industrial firms of the sample highlight
existing environmental regulation as a driver of their eco-innovations. In
second place, is improving the enterprise´s reputation (66.67% of the total),
followed by high costs of energy, water or materials (64.62%) and voluntary
good practices within the sector (62.82%). Close behind are issues such as
market demand (55.90%), environmental regulations or taxes expected in the
future (51.28%), existing environmental taxes, charges or fees (45.13%) and
subsidies and financial incentives for environmental innovations (42.56%).
The need to meet requirements for public procurement contracts is the least
mentioned reason (36.15% of cases).
As can be seen in Figure 4, the differences between cooperatives and non-
cooperative firms in terms of the relevance given to the drivers of eco-innovation
are not substantial. The two drivers which are significantly more relevant
for cooperatives are the existing environmental taxes and environmental
regulations or taxes expected in the future. Government grants, subsidies
and financial incentives for environmental innovations are also mentioned by
50% of cooperatives (versus 41.67% of non-cooperative firms). In contrast,
the need to meet requirements for public procurement contracts and existing
environmental regulations seem more important drivers for non-cooperative
firms. The greater impact of taxes and subsidies on cooperatives can be
explained, theoretically, in light of the greater limitations they face in financing
FIgurE 5. Factors hampErIng thE dEcIsIon to start or ExEcutE InnovatIon actIvItIEs
Figure 5. Factors hampering the decision to start or execute innovation
activities
Source: compiled by the authors. Significance codes: *** 0.01; ** 0.05; * 0.1
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Source: compiled by the authors. Significance codes: *** 0.01; ** 0.05; * 0.1
160 Imanol Basterretxea · Ana Fernández-Sainz ·Jorge Gutiérrez-Goiria · Josu Santos-Larrazabal
their innovation (this is analysed later in the paper). Voluntary initiatives for
environmental good practices appear to be no more relevant as drivers of
eco-innovation in cooperatives than in non-cooperative firms. In fact, quite the
opposite is seen, although the differences are not significant.
Finally, the survey asks what obstacles these industrial firms encounter
when introducing or executing innovation activities. It should be noted that, in
this case, the question refers to the factors that hinder innovation in general
(not only eco-innovation).
With regard to the total sample, the three main obstacles to innovation,
highlighted by more than half of the establishments, are high costs (62.12% of
the total), the existence of other priorities (54.18%), and demand uncertainty
(54.04%). These are followed by issues such as difficulties in obtaining
subsidies (49.16%), excessive competition in the market (46.94%), and lack
of internal finance for innovation (43.59%).
Figure 5 shows important differences between cooperatives and investor-
owned industrial firms. Cooperatives place more importance on nine out of
ten factors hampering innovation compared to investor-owned firms. The
differences are large and significant when valuing certain factors such as the lack
of access to finance (both internal and external) and the lack of collaboration
partners. Two further factors which show substantial differences, although non-
significant, are the lack of access to external knowledge and the lack of skilled
personnel. All these barriers to innovation are widely acknowledged by the
research literature on cooperatives.
In summary, Figure 5 shows that, despite greater limitations to innovation
and eco-innovation, cooperatives are in a situation of parity or even
comparative advantage when it comes to eco-innovation, as illustrated in Table
3 and Figures 2 and 3.
4.2. EstImatIon rEsults
Taking into account the connections between variables identified by the
relevant literature (with special emphasis on the study of Horbach, 2016,
based on the same questions as the Community Innovation Survey) a Probit
model is established to test our hypotheses (See Table 4).
While the percentage of industrial firms introducing innovations that
generate environmental benefits is greater among cooperatives (table 3),
when we analyse solely the subsample of firms that have some sort of eco-
innovation, being a cooperative does not significantly influence eco-innovation
performance. A similar result is seen in relation to the size of the firm, while
level of exports is only significantly related to those innovations which achieve a
reduction in pollution. Among the control variables, external R&D expenditure
and having received public funding to innovate are the factors that positively
and significantly affect more environmental benefits.
Environmental regulations or taxes expected in the future lead to a greater
number of eco-innovation benefits than actual regulations or taxes. Future
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regulations have positive and significant marginal effects on fields such as a
reduction in pollution of soil, noise, water or air (pollution), replacing fossil
energy with renewable energy sources, and recycling. Future regulations also
pre-empt a reduction in pollution from use by the end user and help to extend
product life.
Although the need to meet requirements for public procurement is the least
mentioned driver for eco-innovation (Figure 4), this has a positive and significant
effect in 6 out of 10 environmental benefits (Table 4). This is, therefore, another
key driver of eco-innovation, positively related to reduced pollution, reduced
use of material, water or energy, substitution of fossil energy with renewable
energy and extended product life.
The factor Voluntary action is positively related to two after-sales
environmental benefits, but has no clear effect on benefits within the firm.
Improving the enterprise’s reputation is also an important eco-innovation
driver, which is mainly achieved within the firm via reduced use of materials,
replacement of materials with less polluting substitutes and use of renewable
energies. It is also linked to extended product life.
Current or expected market demand for environmental innovation also
has positive marginal effects on eco-innovation within the firm (reduced CO2
tablE 4. EstImatEd probIt modEls
Source: compiled by the authors. Significance codes: *** 0.01; ** 0.05; * 0.1
162 Imanol Basterretxea · Ana Fernández-Sainz ·Jorge Gutiérrez-Goiria · Josu Santos-Larrazabal
footprint within the firm and by the end user, replacement of materials and
recycling of materials).
Even though respondents consider costs as an important eco-innovation
driver (see Figure 5), high cost of energy, water or materials is not related to
greater environmental benefits.
As mentioned earlier, firms that have actually received public funding (Pub.
aid) for their innovation activities achieve greater environmental benefits.
Nevertheless, when asked about the relevance of subsidies for their eco-
innovation activities, this was among the least mentioned drivers (Figure 4),
and we find no link between the importance given to this driver and eco-
innovation benefits (Table 4).
5. dIscussIon
H1: Being a cooperative has a positive and significant effect on eco-
innovation.
We find partial support for our first hypothesis. The percentage of Basque
industrial firms that have introduced innovations with environmental benefits
is significantly higher among cooperatives than among investor-owned firms.
Nevertheless, when we analyse the subsample of eco-innovative firms and
the joint effects of different variables, we find that being a cooperative has
no significant effect on the introduction of any kind of eco-innovation. These
results add to the evidence from previous empirical studies conducted in
agricultural cooperatives with similar results (Rabadan et al., 2021; Calle et al.,
2020; Carchano et al., 2023).
Nevertheless, it is extraordinary that industrial cooperatives achieve similar
or even better eco-innovation benefits from their innovation activities, despite
facing much greater obstacles to innovation. In fact, our research finds strong
evidence of the greater relevance of factors hampering the decision to start
or execute innovation activities among cooperatives. Lack of internal finance
for innovation and lack of credit or private equity are significantly greater
problems among cooperatives than among investor-owned firms, adding
strong evidence to a persistent theme in the literature on cooperatives (see,
for example, Basterretxea and Martínez, 2012; Bonin et al., 1993; Grashuis
and Su, 2019; Maietta and Sena, 2010). In addition, cooperatives encounter
greater difficulties when seeking partners to collaborate in R&D activities and
in accessing external knowledge. A possible explanation proposed by some
authors, such as Bonin et al. (1993), to explain the reluctance of creditors
and financial markets to work with cooperatives could be the scarcity of
information about cooperatives outside their environment. This reluctance
may manifest as a lack of collaboration in innovation activities and may also
affect other stakeholders. Lack of skilled employees, which is another problem
highlighted more among cooperatives than among investor-owned firms, could
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be explained by salary limitations and low wage differentials of these firms
(Basterretxea and Martínez, 2012).
While our sample is limited to Basque industrial cooperatives, we consider
that some of our findings could also apply to a much broader and more
international spectrum of cooperatives. Basque industrial cooperatives are
much bigger, on average, than industrial cooperatives elsewhere, and they have
a long tradition of inter-cooperation to create joint investment funds such as
Mondragon Inversiones and ULMA Inversiones, or banks such as Mondragon’s
bank Laboral Kutxa. But, despite this, we find evidence that these cooperatives
are at a disadvantage in obtaining finance for their innovation activities.
This financing would likely be even more difficult to come by in industrial
cooperatives of other regions and countries where cooperatives have a weaker
presence.
We also anticipate that other factors limiting innovation in our sample
would be prevalent in international scenarios. Despite the fact that Basque
cooperatives have created a corporate university (Mondragon Unibertsitatea),
corporate vocational and management training centres and joint R&D units,
the cooperatives in our sample still highlight the lack of collaboration partners,
the limited access to external knowledge and not enough skilled personnel as
factors limiting their innovation. These limitations would likely be even greater
for industrial cooperatives elsewhere.
H2: Exports have a positive and significant effect on eco-innovation.
H2 is partially supported by our findings.
We find that the higher the export intensity of Basque industrial firms, the
more likely these firms are to be eco-innovative. However, when we consider
only the subsample of eco-innovative firms, we only find significant positive
effects of exports on eco-innovation in the form of reduced pollution.
Our results go against other studies that find negative relationship between
exports and eco-innovation in Europe (Horbach, 2016; Chiarvesio et al.,
2015, De Marchi, 2012) and are more in accordance with those conducted
in countries with lower regulatory requirements and weaker market pull for
eco-friendly products (Galbreath et al., 2021; Tsai and Liao, 2017). Results
are also coherent with those conducted among Spanish firms (Torrecillas and
Fernández, 2022) and among Eastern European countries, where the increased
exposure to environmentally more stringent markets enhances eco-innovation
(Hanley and Semrau, 2022).
64% of Basque exports go to countries of the EU, and France and Germany
are the main markets, with almost one third of Basque exports going to those
two countries (Eustat, 2024). While eco-regulatory frameworks are similar in
EU countries, market pull for eco-friendly products (and often more expensive
products, as in the case of cars) is higher in richer countries. Exports to EU and
other countries with high eco-regulatory pressure make up the vast majority of
Basque industrial exports. In addition, the leading export sectors in the Basque
164 Imanol Basterretxea · Ana Fernández-Sainz ·Jorge Gutiérrez-Goiria · Josu Santos-Larrazabal
country — oil and petroleum products, cars, car parts — are heavily influenced
by actual and future eco-regulations. All these factors support the logical
assumption that there is a positive relationship between export intensity and
eco-innovation. Similar results would likely be found in other European regions
with comparable export profiles.
Our results also show that the relationship between export intensity and
eco-innovation is higher among Basque industrial cooperatives than among
investor-owned firms. Basque industrial cooperatives export more than
investor-owned firms and the percentage of high-intensity exporters (those
exporting more than 75% of their turnover) is four times higher among
cooperatives. All of these high-intensity cooperative exporters show some sort
of eco-innovation.
The industrial cooperatives belonging to Mondragon have enjoyed
significant international exposure and their annual reports show that they
have been exporting a large part of their production for decades. Other
large Basque industrial cooperatives not belonging to Mondragon, such as
IRIZAR, AMPO, ORONA, ULMA, RPK or GOIZPER export most part of their
production. Thus, our findings cannot be easily projected to other regions with
fewer, smaller and less export-oriented industrial cooperatives. Nevertheless,
similar results can be seen in regions with large, high intensity, cooperative
exporters. In fact, our results are coherent with those found in Spanish olive
oil agricultural cooperatives; these cooperatives are more eco-innovative than
their non-cooperative competitors, mainly due to their larger size and higher
export intensity (Rabadan et al., 2021).
H3: Regulatory pressures and market pull are the main drivers of eco-
innovation.
As previous analyses indicate, current regulation is key to driving eco-
innovation (Bossle et al., 2016; Horbach, 2016; Afeltra et al., 2023), as well as
the effect of expected future regulations (Díaz-García et al., 2015).
In this regard, we find that environmental regulations or taxes expected in
the future are much more important eco-innovation drivers for Basque industrial
firms than actual regulations or taxes. The importance of the oil and petroleum
products and car parts industries in the Basque country —two industries that
are facing huge changes given future eco-regulations— partially explains this
phenomenon. Basque industrial cooperatives have a strong relationship with
the car industry (both as car parts producers and as producers of machine
tools for the car industry) and, consequently, actual and future eco-regulations
and eco-taxes are clearly going to be very important drivers of eco-innovation
for these firms.
A major driver of eco-innovation is the need to meet requirements for
public procurement, yet this driver is less important for Basque industrial
cooperatives, since they work mainly for business-to-business (B2B) private
customers. The need to meet requirements for public procurement can be
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more important in cooperatives operating in the service sector, where many
cooperatives operate in activities such as recycling, waste management,
housing, or care, highly dependent on public procurement. Another driver
of eco-innovation, improving the firm´s reputation, is equally important for
cooperatives and investor-owned firms.
The Basque Country is responsible for the legislative development and
execution within its territory of Spanish regulation on environment and
ecology, and the environmental challenge has been at the top of the agenda
of successive regional governments since the early 1980s (Valdaliso, 2015;
Tamayo et al. 2017). Basque public bodies also have autonomy when it comes
to regulating and taxing cooperatives, and have developed laws, tax exemption
or reduction systems and grant systems intended to help cooperatives
overcome their limitations. Despite all this local public support, we still find
that cooperatives face more limitations when it comes to eco-innovations,
leading us to conjecture that these limitations would likely be greater in regions
with lower legal and tax support for cooperatives and for eco-innovation.
H4: Voluntary initiatives for environmental good practice are more
important drivers of eco-innovation in cooperatives
Our results are contrary to H4 and, to a great extent, contrary to the innate
greener condition of cooperatives suggested by previous researchers despite
limited empirical evidence. Voluntary initiatives as a driver for environmental
good practices have no more relevance in eco-innovation in cooperatives than
in other firms. Cooperative principles can be a potential source of positive
attitudes towards eco-innovation. However, we lack sufficient empirical
evidence to affirm that these principles are actually a real source of better eco-
innovation performance.
The failure of our results to support hypothesis 4 could lead us to be
critical of Basque industrial cooperatives for not fulfilling the prophecy of social
economy literature or, alternatively, of the social economy literature for making
theoretical predictions with scarce empirical evidence.
As Heras-Saizarbitoria (2014) highlights for the case of Mondragon
cooperatives, cooperative principles can be symbolically adopted and
decoupled from the daily activity of the cooperatives. As seen in the case of
Heras-Saizarbitoria (2014), our findings also clash strongly with the utopic
scholarly perspective described in the literature review. The drivers of eco-
innovation in Basque industrial cooperatives are similar to those of non-
cooperative firms and there is no evidence to suggest voluntary eco-innovation
is motivated by cooperative principles.
Our results are in line with the few previous empirical studies conducted in
agricultural cooperatives in Spain and in China. These studies show no clear
evidence to support the eco-innovative innate condition of cooperatives. This
emphasises the need for future advances in the social economy literature to
ensure that any statements made are based on hard evidence.
166 Imanol Basterretxea · Ana Fernández-Sainz ·Jorge Gutiérrez-Goiria · Josu Santos-Larrazabal
comparIson oF rEsults WIth thosE obtaInEd In othEr rEgIons and countrIEs
Based on the international framework, in which eco-innovation already
has a certain theoretical and practical background, this section compares our
results with those of other regions and countries.
Table 5 summarises the cases in which our paper adds evidence in line
with previous studies, and those in which it provides contrary results. The
information has been organised according to the study’s hypotheses, to which
we have added the question of financing, which is key to explaining some of
the differences in terms of innovation in cooperatives. As Table 5 shows, the
tablE 5: comparatIvE rEsults In dIFFErEnt rEgIons and countrIEs
Results Adds evidence in line with previ-
ous research
Finds evidence contrary to
other studies
H1: Being a coopera-
tive has a positive and
significant effect on
eco-innovation.
Partially supported
(cooperatives more eco-
innovative, due to their
size and other factors)
Calle et al. (2020): Spanish wine
cooperatives
Carchano et al. (2023): Spanish
wine cooperatives
Rabadan et al. (2021): Spanish
olive oil agricultural cooperatives
H2: Exports have a
positive and significant
effect on eco-inno-
vation.
Partially supported
Galbreath et al. (2021): Taiwan-
ese manufacturing and service
companies
Hanley and Semrau (2022): 14
European countries
Rabadan et al. (2021): Spanish
olive oil agricultural cooperatives
Torrecillas and Fernández
(2022): Spanish manufactur-
ing firms
Tsai and Liao (2017): Taiwanese
manufacturing firms
Chiarvesio et al. (2015):
Italian firms
De Marchi (2012): Spanish
manufacturing firms
Horbach (2016): European
countries
H3: Regulatory pres-
sures and market pull
are the main drivers of
eco-innovation.
Supported
Key drivers present in empirical
studies worldwide (see Horbach,
2016 for European countries,
and Afeltra et al. (2023), Bossle
et al. (2016) and Díaz-García et
al. (2015): for literature reviews).
H4: Voluntary initiatives
for environmental
good practice are
more important drivers
of eco-innovation in
cooperatives
Rejected
No previous empirical
evidence, but several in-
fluential academic papers
suggest a more ecological
innate condition of co-
operatives (Mozas and
Bernal, 2006; Novkovic,
2008;
Puentes and Velasco,
2009)
Lack of internal finance,
credit or private equity Supported
Basterretxea and Martínez
(2012): Basque industrial
cooperatives
Grashuis and Su (2019): Farmer
cooperatives, review of the
empirical literature.
Maietta and Sena (2010): Italian
producers´ cooperatives
Source: compiled by the authors
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rEvIsta dE Economía mundIal 67, 2024, 145-173
study reinforces in many cases the evidence from previous literature. The main
differences concern the exports effect, which is still under debate, and the
voluntary initiatives.
6. conclusIons
The need to move towards new forms of production and consumption,
reducing environmental impacts, is currently a challenge at the core of many
initiatives. Cooperatives can be a key player in this context.
Our study confirms the greater presence of eco-innovation among
cooperatives compared to traditional firms. However, it raises doubts as to
whether it is precisely this issue (being a cooperative) that makes a difference,
or whether this is due to other factors, such as external R&D, or higher export
intensity.
Nevertheless, the performance of cooperatives in terms of eco-innovation
is particularly noteworthy, considering the greater difficulties or obstacles they
encounter.
Our results could help guide policy makers towards promoting sustainable
practices among both cooperative and non-cooperative firms. Given that
future eco-regulations and taxes are the main driver of eco-innovation (even
more so in the case of cooperatives), policymakers should provide clear signals
about upcoming changes in regulations so that firms can align their strategies
accordingly. Our study also highlights several factors which hamper innovation
activities more acutely among cooperatives: lack of internal finance, lack of
credit or private equity and lack of collaboration partners. In accordance,
grants and subsidies for innovation activities are more important drivers of
innovation among cooperatives and so policymakers should complement
actual and future eco-regulations with specific aids for cooperatives (subsidies,
access to credit, collaboration via public research partners, etc.).
7. lImItatIons and FuturE rEsEarch dIrEctIons
Among the limitations of our study, we should mention that some factors
which, according to our results, have little influence on eco-innovation could
be highly context-dependent. For example, the high cost of energy, water
or materials was not an important eco-innovation driver for the 2019-2021
period in which our data were gathered. However, surveys for the period 2021-
2023 might show this factor as being more significant.
The Innovation Survey of the Basque Institute of Statistics from which the
data were extracted included most of the relevant drivers of eco-innovation,
but did not include some internal drivers discussed in other papers, such as
environmental leadership and managerial concern, or questions related to
human resources and capabilities. If we had developed our own ad-hoc survey,
we would have included these questions, but it would have been difficult for us
to achieve a similar response rate and such rich comparative data.
168 Imanol Basterretxea · Ana Fernández-Sainz ·Jorge Gutiérrez-Goiria · Josu Santos-Larrazabal
An interesting research direction would be to complete an international
analysis of eco-innovation in agricultural cooperatives and investor-owned
agricultural firms. This would enable eco-innovation to be researched from an
international perspective, given that agricultural cooperatives are important in
many different countries.
While we have studied eco-innovation in industrial cooperatives versus
investor-owned firms, further studies could use the Eustat’s innovation survey
to analyse eco-innovation among cooperatives in the service sector. In fact,
this survey offers data on 3,061 establishments in the service industry (139
of them cooperatives), a large source of data which was not used in our study.
data avaIlabIlIty
Data are available for research purposes upon request to the Basque
Institute of Statistics (Eustat).
acknoWlEdgmEnts
The authors would like to thank the Basque Institute of Statistics (Eustat)
for its support in providing microdata.
This study was supported financially by the State Programme for the
Promotion of Scientific and Technical Research of Excellence/Spanish Ministry
of Economy and Competitiveness [Refs. PID2019-105986GB-C22, TED2021-
131763A-100, PID2021-122846NB-I00]; by the Department of Education
of the Basque Government [research grant numbers IT-1508-22 and IT 1735-
22] and by the University of the Basque Country [research grant number
GIU21/011].
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