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Resilience of Urban Social-Ecological-Technological Systems (SETS): A Review

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Resilience is a widely debated concept that encompasses various interpretations and definitions. Recently, in science and policy circles, there has been a growing interest in the concept of Social-Ecological-Technological Systems (SETS) resilience which offers a new interpretation. While this concept is now used frequently, it is not properly understood and there is still a lack of clarity on what it means and its underpinning principles. This lack of clarity and understanding may confuse and even disorient researchers and policy makers. To address this issue, we review the literature published in the context of urban systems. The reviewed literature is mainly focused on nature-based solutions, indicating more contributions from the ecological field. Also, flooding, extreme heat, and drought are major stressors discussed in the literature. We elaborate on the definition of SETS resilience and discuss that its dominant principles are adaptability, transformability, flexibility, redundancy, equity, diversity, foresight capacity, connectivity, robustness, multi-functionality, learning, and non-linearity. We also expound upon the key components of SETS, how they are intertwined, and potential trade-offs that may emerge between them. Our study demonstrates that the implementation of the SETS approach leads to numerous ancillary benefits. These include benefits for climate change adaptation and mitigation, pandemic prevention and response, human health and well-being, and justice. If multi-level and polycentric governance strategies are adopted, it can also help avoid trade-offs that may emerge between social, ecological, and technological dimensions. We conclude by emphasizing that the literature is dominated by epistemological approaches and more empirical research is needed to understand better the complex dynamics of SETS resilience.
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Sustainable Cities and Society 99 (2023) 104910
Available online 3 September 2023
2210-6707/© 2023 Elsevier Ltd. All rights reserved.
Resilience of urban social-ecological-technological systems (SETS):
A review
Ayyoob Shari
a
,
b
a
Hiroshima University, The IDEC Institute & Network for Education and Research on Peace and Sustainability (NERPS), 1-5-1 Kagamiyama, Higashi Hiroshima City,
Hiroshima, 739-8529, Japan
b
School of Architecture and Design, Lebanese American University, Beirut, Lebanon
ARTICLE INFO
Keywords:
Social-ecological-technological systems
Urban resilience
Trade-offs
Adaptability
Justice
Resilient cities
ABSTRACT
Resilience is a widely debated concept that encompasses various interpretations and denitions. Recently, in
science and policy circles, there has been a growing interest in the concept of Social-Ecological-Technological
Systems (SETS) resilience which offers a new interpretation. While this concept is now used frequently, it is
not properly understood and there is still a lack of clarity on what it means and its underpinning principles. This
lack of clarity and understanding may confuse and even disorient researchers and policy makers. To address this
issue, we review the literature published in the context of urban systems. The reviewed literature is mainly
focused on nature-based solutions, indicating more contributions from the ecological eld. Also, ooding,
extreme heat, and drought are major stressors discussed in the literature. We elaborate on the denition of SETS
resilience and discuss that its dominant principles are adaptability, transformability, exibility, redundancy,
equity, diversity, foresight capacity, connectivity, robustness, multi-functionality, learning, and non-linearity.
We also expound upon the key components of SETS, how they are intertwined, and potential trade-offs that
may emerge between them. Our study demonstrates that the implementation of the SETS approach leads to
numerous ancillary benets. These include benets for climate change adaptation and mitigation, pandemic
prevention and response, human health and well-being, and justice. If multi-level and polycentric governance
strategies are adopted, it can also help avoid trade-offs that may emerge between social, ecological, and tech-
nological dimensions. We conclude by emphasizing that the literature is dominated by epistemological ap-
proaches and more empirical research is needed to understand better the complex dynamics of SETS resilience.
1. Introduction
Resilience has been a buzzword in research and policy circles for
over two decades. This is unsurprising given the increasing trends of
adverse events and the projected increase in their frequency and in-
tensity due to climate change. The eld of resilience is constantly
evolving, and various concepts such as ‘engineering resilience,
‘ecological resilience, ‘social resilience, and ‘community resilience
have been introduced over time (Cinner & Barnes, 2019; Donagh Hor-
gan & Dimitrijevi´
c, 2018; Kang, Bowman, Hannibal, Woodruff & Port-
ney, 2023; Pickett, McGrath, Cadenasso & Felson, 2014). Further, there
has been a growing recognition of the need for integrated approaches
across multiple social, ecological, economic, and technological domains
of resilience (Ahlborg, Ruiz-Mercado, Molander & Masera, 2019;
Cabezas, Pawlowski, Mayer & Hoagland, 2004; Chang et al., 2021;
Holling, 2001; Wang, Wang, Chen & Liu, 2022). In particular,
considering the complex interlinkages between humans and natural
ecosystems, much work has been done on social-ecological resilience
(Anderies, Janssen & Ostrom, 2004; Holling, 2001; Ostrom, 2009;
Ramaswami et al., 2012; Turner et al., 2022; Xiang, 2019). This entails a
systemic approach acknowledging that social and ecological systems
co-evolve, and socio-ecological resilience is more than the sum of social
and ecological resilience (Cucuzza, Stoll & Leslie, 2020; de Vos, Biggs &
Preiser, 2019). Such systemic approaches can be further expanded to
integrate other domains and dimensions of resilience. For instance, Li,
Dong and Liu (2020) mentioned the need to include the economic
dimension and emphasized that coupled interactions across various
social, economic, and ecological systems should be considered. The
importance of integrating the economic dimension has also been
emphasized in other studies (Hirt & Campbell, 2023; Wang et al., 2022).
Similarly, it is argued that social-ecological resilience cannot be disen-
tangled from the ever-evolving technological world (McPhearson et al.,
E-mail address: shari@hiroshima-u.ac.jp.
Contents lists available at ScienceDirect
Sustainable Cities and Society
journal homepage: www.elsevier.com/locate/scs
https://doi.org/10.1016/j.scs.2023.104910
Received 20 May 2023; Received in revised form 30 July 2023; Accepted 30 August 2023
Sustainable Cities and Society 99 (2023) 104910
2
2022). On the one hand, technological advances could pose risks to
human and ecological systems and exacerbate vulnerabilities. On the
other hand, wellmanaged disruptive technologies could offer solutions
to enhance resilience to multiple socioeconomic and ecological hazards
and stressors and help avoid crossing tipping points. Accordingly, the
resilience of Social-Ecological-Technological Systems (SETS) has gained
traction. While this concept is now used frequently, it is not properly
understood, and there is still a lack of clarity on what it means and its
underpinning principles. This lack of clarity and understanding may
confuse and even disorient researchers and policy makers.
Against this background, this study aims to synthesize information
reported in the literature to better understand the theoretical basis and
underpinning principles of SETS resilience. While we acknowledge that
there is a long history of research on various aspects of resilience (e.g.,
socio-ecological and ecological-social-economical), we focus on SETS
because it is a relatively new strand of resilience that has been relatively
less studied. By focusing on SETS, we do not intend to overemphasize the
role of technology in enhancing urban resilience. In fact, we acknowl-
edge that technologically deterministic approaches may cause
inequality issues, lead to a false sense of security, and increase vulner-
abilities in the long run (Eubanks, 2017; Kaika, 2017). Therefore, ho-
listic approaches that consider the needs of different stakeholders,
recognize interlinkages between multiple dimensions (i.e., social, eco-
nomic, ecological, and technological), and facilitate social learning and
transformation are essential (Cretney & Bond, 2014; Pickett, Cadenasso
& Grove, 2004). As will be discussed later, these are key components of
SETS resilience.
The following questions guide this scoping review: What are the
general characteristics of research on SETS? How is socio-ecological-
technological resilience dened in literature? What are the underlying
characteristics (principles) of social-ecological-technological resilience?
What are the key components of SETS, and how are they intertwined?
and What potential trade-offs may emerge between different compo-
nents of SETS and how can be dealt with?
The remainder of this paper is structured as follows. Review mate-
rials and methods are explained in Section 2. The review ndings are
synthesized and reported in Section 3. Finally, Section 4 concludes the
study by highlighting the main ndings and recommending priority
research areas.
2. Materials and methods
We adopted a systematic approach for literature search and selec-
tion. This was guided by the Preferred Reporting Items for Systematic
Reviews and Meta-Analyses (PRISMA) framework (Page et al., 2021),
commonly employed for systematic literature reviews, bibliometric re-
views, and scoping reviews. Academic research indexing databases,
namely Web of Science (WoS) and Scopus, were utilized for the litera-
ture search on December 31st, 2022. This yielded 483 documents. After
excluding documents not written in English and duplicates, 319 docu-
ments remained in the database. The titles and abstracts of these studies
were reviewed to determine if they met the objectives of the review. At
this stage, 283 documents that did not address interactions across social,
ecological, and technological components were excluded. The remain-
ing 28 documents were examined in detail to extract the necessary data
for analysis. In addition, four documents cited in the reference sections
of the reviewed papers were found relevant and added to the database.
In the end, 32 documents were reviewed for the purpose of this study.
This process is shown in Fig. 1.
A thorough content analysis was performed on the chosen papers to
obtain essential data for analysis. A Microsoft Excel spreadsheet was
created to gather data on the studies geographic, methodological, and
sectoral focuses. In addition, separate columns were allocated to collect
data on the denition and underlying principles of SETS and co-benets
and trade-offs between SETS components. An inductive approach guided
the content analysis. In this approach, the extracted data is coded iter-
atively. In other words, initial codes are developed based on the contents
of the rst reviewed paper. New codes are added to the data extraction
Fig. 1. The PRISMA framework for literature search and selection. Adapted from Page et al. (2021).
A. Shari
Sustainable Cities and Society 99 (2023) 104910
3
sheet if applicable after reading the next paper. This process will
continue until all papers in the database are reviewed. Next, the
collected data were synthesized to answer the review questions
mentioned earlier.
3. Results
3.1. Overview of the reviewed papers
The rst paper on this topic was published in 2010, indicating that
the resilience of urban SETS is still a new concept. Few papers were
published prior to 2018. However, in recent years, the number of pub-
lished papers has increased; the highest recorded count was 8 in 2022.
Most of the reviewed papers are ‘research papers(~59%). The rest are
‘review papers(~19%), and other types of papers, including ‘synthesis,
‘editorial, ‘forum, ‘insight, ‘letter, and ‘concept paper (~ 22%).
Regarding the sources, there are 21 unique journals covering various
city-related issues. This indicates the inter-disciplinary nature of SETS.
In terms of the number of publications, noteworthy journals are ‘Current
Opinion in Environmental Sustainability, ‘Ecology and Society,
‘Earths Future, and ‘Sustainability. Geographically, the majority of
studies have a generic scope. The United States is the primary focus of 11
papers. No other country has been studied in more than one paper. Half
of the papers are purely theoretical, but the rest have some level of
empirical focus. In terms of methodological approaches, 24 papers are
qualitative, four are quantitative, and the rest have adopted mixed ap-
proaches. The most common method is qualitative/descriptive case
study (7 papers), followed by discourse-based analysis (4 papers), geo-
spatial analysis (2 papers), questionnaire survey (2 papers), modeling (2
papers), and composite index and capital portfolio approach (each one
paper). The case studies are mainly from the United States (including
cases from Arizona, Texas, Oregon, Maryland, New York, Georgia, and
Florida). There are also a few cases from other countries, including
Australia, Italy, India, Nepal, and South Korea. It is clear that more case
studies from countries other than the US are needed. Further, there is a
need for more quantitative case studies that explore future scenarios.
Information related to these cases has been provided across different
parts of the Results section (Section 3). Regarding sectoral focus, apart
from generic studies, most papers are focused on Nature-based Solutions
(NbS) (n =11). Other noteworthy sectors are infrastructure (n =7),
water (n =4), and energy (n =2). Finally, ooding (n =9), extreme heat
(n =5), and drought (n =3) are key stressors studied in the reviewed
papers.
3.2. Denitions of SETS and their resilience
Despite the absence of explicit denitions for SETS and their resil-
ience in the reviewed papers, it is possible to extract denitions from the
descriptions provided in the literature. There is a consensus that SETS
and their resilience have gained traction following three main de-
velopments: the increasing understanding of the unsustainability of
human-environment interactions, the growing concerns over the
adverse events that are likely to grow in frequency and intensity due to
climate change, and the broad recognition of the importance of systemic
approaches for making human-environment interactions more sustain-
able and address the adverse events that are facing cities (Chang et al.,
2021; Kim et al., 2022; McPhearson et al., 2022).
Socio-Ecological Systems (SES) resilience is a more established
concept that aims to offer frameworks for optimizing human-
environment interactions and providing solutions to address the risks
of natural and climate-induced hazards through different adaptation and
mitigation measures (Anderies et al., 2004; Kim et al., 2022). In other
words, achieving socio-ecological resilience necessitates acknowledging
the intricate and dynamic interactions between social and ecological
systems, while making fundamental transformations in
human-environmental interactions to sustain system functionality amid
stressors. This is done to steer clear of surpassing crucial thresholds and
tipping points that lead to unsustainable regimes, ultimately endan-
gering both human welfare and ecosystem vitality (Olsson, Galaz &
Boonstra, 2014; Smith & Stirling, 2010). The SETS framework builds on
SES perspectives by emphasizing the important roles that technological
infrastructures play in shaping and managing human-environment in-
teractions. For instance, through its nuanced analysis of the intricate
interplay between environment, infrastructure, and equity consider-
ations, SETS enables us to comprehend how hazards impact society and
their distribution across various segments (Chang et al., 2021).
Based on the SETS perspective, a citys resilience is determined by
complex and dynamic interactions between interdependent sub-systems
such as the economy, humans, social networks, ecological networks,
biophysical features, regulatory systems, cultural norms, governance
and institutions, physical infrastructure, and built environment. These
interactions occur across multiple spatial and temporal scales (Bixler
et al., 2019; Kotzee & Reyers, 2016; McPhearson et al., 2022). In other
words, system-based and transdisciplinary approaches that account for
such multiscale interactions are essential for cities to effectively and
efciently mitigate, cope with, respond to, recover from, and more
successfully adapt to shocks (i.e., sudden or instantaneous) or stressor-
s/pressures (i.e., long term and incremental) (Ariyaningsih & Shaw,
2022; Bixler et al., 2019; Kotzee & Reyers, 2016; McPhearson et al.,
2022). The SETS perspective, therefore, emphasizes that only enhancing
the capacity of individual urban sub-systems is not sufcient for building
resilience, and the complex and dynamic interactions among them
should also be taken into account (Bixler et al., 2019).
3.3. The underlying principles of urban SETS resilience
Various principles have been used to understand better what con-
tributes to the resilience of SETS. As shown in Fig. 2, these principles are
diverse and cover issues related to different social, ecological, and
technological aspects of resilience. According to Fig. 2, the dominant
principles associated with SETS resilience are adaptability, trans-
formability, exibility, redundancy, equity, diversity, foresight capacity,
connectivity, robustness, multi-functionality, learning, non-linearity,
resistance, and interdependency. Fig. 3 shows that these are mainly
related to the adaptation, absorption, and mitigation stages and abilities
of the resilience-building process (Cutter et al., 2013). These will be
further discussed in the remainder of this section. An important issue
that needs to be mentioned is that there could be different types of
interlinkages between these principles (e.g., co-benets and trade-offs).
Such interlinkages are not adequately addressed in the SETS literature.
However, there have been efforts in other strands of resilience to shed
light on them (Parizi, Taleai & Shari, 2021). Such modeling studies
should also be conducted in the context of SETS.
There is a consensus in the urban resilience literature that resilient
urban systems should be able to plan and prepare for, absorb, recover
from, and adapt to adverse events (Cutter et al., 2013). The SETS
resilience principles mentioned in the literature either cut across all
these abilities or can be mainly associated with a single ability (i.e.,
either planning, absorption, recovery, or adaptation). Most principles
can be categorized as overarching, given their linkages to multiple
abilities. These are often linked to different processes that various
stakeholders undertake to enhance resilience abilities. These processes
are characterized by complex, non-linear, and non-stationary dynamics
across spatial and temporal scales. Integrating technological measures
offers opportunities to capture and optimize such dynamics. Further,
addressing the complex interactions between various social, ecological,
and technological systems of urban systems requires adopting adaptive
systems thinking approaches that consider interactions across multiple
temporal and spatial scales to avoid mismatches/conicts and enhance
synergies (McPhearson et al., 2022). Considering such complex in-
teractions could be challenging. However, technological advances,
particularly in the realm of big data analytics and scenario-making,
A. Shari
Sustainable Cities and Society 99 (2023) 104910
4
could offer solutions to overcome such challenges.
It should be noted that, the amount of attention that should be paid
to various social, ecological, and technological aspects may vary over
time (McPhearson et al., 2022). For instance, during the early stages of
project deployment, attention to technological aspects may be more
important. However, over time social aspects related to governance and
accessibility become paramount (McPhearson et al., 2022). Further, to
address complexity, SETS should be able to manage non-linear slow
variables and feedback (Kotzee & Reyers, 2016).
Interconnectedness, connectivity, and interdependence are closely
related principles that indicate the strong interdependencies between
social, ecological, and technological systems. Interdependencies can be
of different types and natures. For instance, they could be physical or
institutional. However, regardless of their type, interdependencies could
be hierarchical, lateral, or longitudinal (Gim & Miller, 2022). ‘Hierar-
chicalrefers to the interdependencies between specic systems across
geographical scales (e.g., between a specic urban infrastructure system
with corresponding regional or national systems); ‘lateraldenotes the
interdependencies between two or more different infrastructure sys-
tems; and ‘longitudinal indicates the path dependencies arising from
the extended operation of various urban systems over time (Gim &
Miller, 2022). These have been articulated in a study by Gim and Miller
(2022). Physical interdependencies are well-studied in urban resilience
literature. For instance, in many contexts, hierarchical and lateral in-
terdependencies can be observed between energy infrastructure and
water infrastructure due to the strong energy-water nexus (Shari &
Yamagata, 2016). The nexus could be expanded to include other sectors,
such as food. Obviously, a lack of attention to interdependencies across
these may result in chained effects that could ground the whole system
to a halt (Gim & Miller, 2022). Institutional mechanisms govern such
physical infrastructures to improve their connection and functionality
(e.g., through regular maintenance and upgrading). Therefore,
Fig. 2. Major resilience principles mentioned in the reviewed literature. The size of each term is proportional to the number of times it has appeared in the reviewed
papers. The colors are only for presentation purpose.
Fig. 3. The four key stages of resilience planning and the main principles related to each stage. Note that, in addition to the overarching ones listed on the left panel,
some principles may be related to more than one stage. We have allocated them to one stage based on their main contribution.
A. Shari
Sustainable Cities and Society 99 (2023) 104910
5
institutional dependencies are also essential to SETS resilience (Gim &
Miller, 2022). Technological approaches can also be used to enhance the
governance mechanisms and optimize interlinkages across multiple
components.
Participatory and collaborative approaches are necessary to address
the interdependencies between different systems properly. Such ap-
proaches facilitate smooth interactions and help break self-reinforcing
feedback loops that are a barrier to transformation and reinforce lock-
in into existing undesirable patterns (Olsson et al., 2014). The likeli-
hood of lock-in increases when institutions do not facilitate participation
in the design, development, and evaluation of infrastructure. This, in
turn, may restrict innovative ideas and perspectives that could be
incorporated to develop transformative resilience approaches (Gim &
Miller, 2022). To avoid that, among other things, there is a need for
participatory governance mechanisms that acknowledge the existence of
multiple interdependencies across different sectors and stakeholders and
establishes innovative and transformative mechanisms to optimize them
during different resilience-building stages, ranging from planning to
absorption, recovery, and adaptation (Gim & Miller, 2022; Donagh
Horgan & Dimitrijevi´
c, 2021). Participatory approaches can also help
promote equity and justice that should be prioritized during different
stages of resilience building. This is because socially vulnerable groups
and communities often lack access to infrastructures, resources, and
services necessary to adequately deal with adverse events (McPhearson
et al., 2022). Further, they are more exposed to risks. Indeed, often,
there is spatial overlap between social, ecological, and technological
vulnerabilities. For instance, socially vulnerable groups are more likely
to be located in ecologically vulnerable areas exposed to technological
hazards (H. J. Chang et al., 2021). Efforts aimed at enhancing resilience
should reduce such vulnerabilities and minimize exposure to hazards. In
this regard, the SETS approach allows integrated measures that enhance
synergies and reduce trade-offs. For instance, without paying attention
to social issues, plans aimed at ecological improvement may result in
gentrication and/or displacement of some groups. Similarly, inequi-
table access to technologies may exacerbate societal inequalities,
thereby undermining resilience. An integrated approach can help avoid
such problems by, among other things, providing affordable housing
options (Chang et al., 2021). While smart technologies such as
web-based platforms and smartphone apps offer unique solutions for
participatory and collaborative governance (Kitchin, 2015), they cannot
always replace face-to-face engagement with stakeholders (D. Horgan &
Dimitrijevic, 2019). Therefore, while smart technologies can support
participatory approaches in the context of SETS, the role of traditional
approaches for co-design and co-implementation of initiatives should
not be overlooked.Robustness, resistance, reliability, and foresight ca-
pacity are principles mainly related to planning and preparation for
adverse events. These can help mitigate the potential impacts of di-
sasters. Robustness and resistance are closely linked; greater levels of
robustness and resistance can increase system reliability, the capacity to
buffer shocks, and the ability to maintain system functionality even
under stress (Krueger, McPhearson & Levin, 2022). However, over-
reliance on these physical characteristics can lead to physical/techno-
logical determinism that creates a false sense of safety/resilience and
may result in catastrophic consequences if tipping points and critical
thresholds are crossed (Shari & Yamagata, 2016). Investing in other
capacities, including absorption and adaptation, is necessary to prevent
that from happening. Further, an enhanced foresight capacity to deal
with uncertainties and emerging characteristics is needed (Munoz-Er-
ickson et al., 2021). Among other things, this demands visioning,
long-term planning, and integration of scenario-making in efforts aimed
at building urban resilience. In this regard, technological advances
enabled by big data analytics and information and communication
technologies can offer useful solutions.
The principles linked to absorption capacity are multi-functionality,
redundancy, diversity, polycentricity, coping capacity, and exibility.
Investment in the absorption capacity is important as, no matter how
robust a system is, it is always likely to be vulnerable to hazards. Ab-
sorption capacity helps minimize damages and loss of system function-
ality, thereby enabling rapid recovery (Shari & Yamagata, 2016).
Having higher tolerance and margin capacity contributes to better ab-
sorption of shocks. This can be achieved by incorporating diverse
components with redundant capacity in the system to meet needs and
demands under different future scenarios (e.g., diverse and redundant
options for stormwater management system or diverse tree species). In
addition, it will contribute to urban resilience by promoting exibility
and multi-functionality of urban infrastructure (e.g., green infrastruc-
ture that can enhance resilience to multiple adverse events such as
extreme heat or urban ooding), investing in decentralized and poly-
centric infrastructure systems that can disperse risk and help prevent
complete system failure, and adopting modular and polycentric gover-
nance mechanisms that allow nimbler reactions when needed. Techno-
logical advances have provided opportunities to promote such
decentralized and polycentric systems. For instance, smart technologies
are increasingly used to decentralize urban energy systems (Bixler et al.,
2020; Smith & Stirling, 2010; Wellmann et al., 2023).
Following a disruptive event that causes disturbance to a socio-
ecological-technological system, the recovery stage entails restoring
the system to its pre-event state or a new state of stability through a
range of short-, medium-, and long-term measures. However, short- and
medium-term measures and actions should be prioritized, as agility is
the essence of any successful recovery (Shari & Yamagata, 2016).
Successful recovery facilitates returning to the pre-event conditions
or a new state of stability. However, adaptation capacity is needed to
enhance the ability of the system to withstand future disturbances and
changing conditions and contribute to the long-term sustainability and
resilience of socio-ecological-technological systems. According to the
reviewed literature, this capacity can be strengthened through various
principles such as learning, adaptability, self-organization, and trans-
formability. Learning is essential as lessons taught by the adverse event
can be used to enhance the overall functionality of urban systems and
ensure better performance against similar events in the future (Shari &
Yamagata, 2016). Adaptability and self-organization are capacities that
enable the system to go through an adverse event with minimum func-
tionality loss. In other words, these capacities allow the system to
continue its operations without the need for a regime shift (Olsson et al.,
2014). This may not, however, be possible when tipping points are
crossed. Under such circumstances, transformative resilience is needed.
Transformability entails the ability to make changes in plans, policies,
and technologies so that regime shifts become possible in response to
emergent needs and issues (Elisabeth H. Krueger et al., 2022; Olsson
et al., 2014).
3.4. SETS components and examples of their interlinkages for SETS
resilience
The three key dimensions of SETS are social, ecological, and tech-
nological (see Fig. 4). For a system to be resilient, interlinkages of the
different components of these dimensions should be maintained. In
other words, any internal or external shocks that disrupt these inter-
linkages will undermine resilience (Grimm, Pickett, Hale & Cadenasso,
2017). This is because disturbances in one component can cause dis-
ruptions in others. For instance, disturbance in the physical infrastruc-
ture could result in the depopulation of a city, thereby affecting the
social structure (Grimm et al., 2017). Also, the Great Fire of Baltimore in
1904 showed that the absence of social infrastructure, such as strict
zoning and warehousing codes and national standards for re hydrant
ttings, can cause physical disruption. The re spread quickly and
caused signicant damage (Grimm et al., 2017). More recently, the
devastating wildre that took place in Fort McMurray during May 2016
resulted in extensive destruction and the displacement of more than 88,
000 individuals. This event serves as a stark reminder of the potential
consequences of the lack of integrated approaches that consider social,
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Sustainable Cities and Society 99 (2023) 104910
6
ecological, and technological dimensions and their interactions (Vail-
lant, 2023). In light of ongoing climate change trends, it is imperative to
adopt such integrated strategies to effectively manage and reduce the
risks associated with natural hazards. The reminder of thsi section out-
lines the interactions between SETS components and their implications
for resilience.
3.4.1. Social-ecological coupling
The coupling between social and ecological dimensions is well
recognized in the literature. Indeed, socio-ecological resilience has
become a key strand of resilience research over the past decade
(Afriyanie et al., 2020; Cretney, 2014; Sterk, van de Leemput & Peeters,
2017). As shown in Fig. 4, multiple social and ecological components
should be linked to each other to enhance the resilience of a system.
For instance, co-managing natural resources and ecosystems is
crucial for adapting to changing conditions and sustainability transi-
tions. This should involve considering the norms, beliefs, and values of
different social groups and stakeholders. Indeed, stakeholder engage-
ment is needed for promoting a sense of ownership and for the co-design,
co-production, and co-implementation of plans and programs for
ecosystem conservation and natural resource management (Nel et al.,
2016). Such approaches contribute to enhancing resilience by, among
other things, addressing inequalities, building local capacity, securing
nancial resources, providing platforms for knowledge sharing, and
strengthening feedback loops between human and natural factors that
can offer learning and adaptation opportunities (Branny et al., 2022; De
Luca, Langemeyer, Va, Bar´
o & Andersson, 2021; Kernaghan & da Silva,
2014; Singletary et al., 2022). In this sense, if governed properly,
technological solutions such as web-based platforms can be used to
strengthen and streamline stakeholder engagement (Nitoslawski, Galle,
Van Den Bosch & Steenberg, 2019).
The socio-ecological approach can also be used to modify human-
nature interactions by optimizing urban-rural linkages and regulating
urbanization patterns and dynamics (Song, Pandey, Dong, Shari &
Subedi, 2022). These could contribute to resilience against adverse
events such as pandemics and/or any other events resulting in supply
chain disruptions (Suleimany, Mokhtarzadeh, & Shari, 2022). As a case
in point, it is widely argued that human encroachment on natural eco-
systems increases the risk of exposure to zoonotic diseases and could
result in pandemics (Shari, 2022; Spencer, Marasco & Eichinger,
2021). Further, unfettered urban expansion can erode urban-rural
linkages that are critical for the social, ecological, and economic resil-
ience of cities and city regions. For instance, the vulnerability of cities
with weakened urban-rural linkages to global supply chain disruptions
was demonstrated during the COVID-19 pandemic (Khor et al., 2022;
Shari, 2022). Multi-level governance approaches considering inter-
linkages between actors and stakeholders across various spatial and
temporal scales can help minimize vulnerability to such disruptions and
enhance urban and regional resilience (Amirzadeh, Sobhaninia, Buck-
man, & Shari, 2023). For instance, multi-level governance that sup-
ports the protection of periurban areas and promotes urban agriculture
can help overcome food insecurity issues in the face of major global
supply chain disruptions (Khor et al., 2022). Based on this, the Food and
Agriculture Organization (FAO) recommends a City-Region Food Sys-
tems approach that calls for a paradigm shift from capital-oriented food
systems to ones largely reliant on collaborative networks of stakeholders
across city regions
1
. This approach enhances food security, improves
environmental quality, and provides co-benets for resilience against
other adverse events such as ooding (Khor et al., 2022). Supply chain
resilience can be further enhanced by integrating technological
Fig. 4. SETS dimensions and components. Based on the synthesis of the reviewed literature with more input from the following references (Ariyaningsih & Shaw,
2022; H. Chang et al., 2020; Markolf et al., 2018).
1
https://www.fao.org/in-action/food-for-cities-programme/overview/crfs/
fr/
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Sustainable Cities and Society 99 (2023) 104910
7
measures into social-ecological systems (Di Paola, Cosimato & Vona,
2023). For instance, urban green infrastructure systems feature in-
teractions between different social, ecological, and technological com-
ponents, thereby providing multiple co-benets for supply chain
resilience, climate change adaptation/mitigation, and human and
ecosystem health and well-being (Ramyar, Ackerman & Johnston, 2021;
Sch¨
afer & Swilling, 2013).
Other examples have also been mentioned in the literature. For
instance, Bixler et al. (2020) discuss how local governments can use sale
tax policies to acquire the budget necessary for environmental protec-
tion in San Antonio, Texas. Since 2000, the public-supported initiative
has enabled the city to generate over $250 million. The budget is
designated for acquiring and preserving 65,000 hectares of land over the
Edwards Aquifer. Additionally, it supports enhancing urban green
infrastructure within the city. In addition to ecosystem protection, the
initiative has contributed to urban resilience against multiple stressors
such as water stress (through aquifer recharge), ooding (through
stormwater inltration), and extreme heat (through mitigating the
urban heat island effect) (Bixler et al., 2020).
As discussed in other sections of this paper, the relationship between
social and ecological dimensions can be mediated by technologies.
Indeed, technology can be utilized to strengthen the coupling between
social and ecological dimensions. For instance, smart solutions and
technologies such as citizen science, virtual reality, wearable sensors,
and the Internet of Things (IoT) can improve feedback mechanisms
between humans and nature, thereby enabling stakeholder engagement
and contributing to better monitoring, protection, and management of
ecosystems and natural resources (Branny et al., 2022). Such technolo-
gies can also facilitate other types of services and benets, such as
enhanced environmental awareness through visualization of human
dependence on nature or real-time information on how to respond to
environmental exposure (Branny et al., 2022). Further, as Wellmann
et al. (2023) argue, in the context of Nature-Based Solutions (NbS),
technology can improve resilience by integrating citizen science and
local knowledge into practices for biodiversity conservation.
3.4.2. Social-technological coupling
Considering interactions between technological infrastructure sys-
tems and social systems is critical for enhancing the resilience of urban
systems (Kim et al., 2022). This is essential to avoid undesirable
trade-offs that may emerge when isolated approaches are adopted. For
instance, the emphasis on technological solutions such as sensor-based
monitoring and management of urban green spaces, within the frame-
work of NbS, can potentially diminish human engagement with nature.
In turn, this may limit opportunities for fostering social capital devel-
opment (Branny et al., 2022). Technological approaches may also erode
the sense of place among urban residents (Branny et al., 2022). This has
implications for resilience building as the sense of place is important for
active engagement in collective actions aimed at planning for, absorp-
tion, recovery from, and adaptation to adverse events (Shari, 2016).
These arguments do not mean that smart technologies should not be
utilized for the management of NbS. Indeed, smart solutions provide
multiple benets, such as enhanced monitoring, and can facilitate
crowdsourced efforts for enhancing ecosystem health. Therefore, better
governance of technologies such as smart solutions is needed to ensure
they will also connect people with each other and nature (Branny et al.,
2022).
In the context of infrastructure management, online platforms
enabled by smart technologies (e.g., web-based apps, smartphone apps,
GIS-platforms, larger cloud computing systems for data analysis, or
video conferencing suites) can support evidence-based decision-mak-
ing and offer learning and knowledge-sharing opportunities that
strengthen adaptive capacity (Wellmann et al., 2023, p. 493). Through a
combination of bottom-up and top-down approaches, they can engage
multiple stakeholders (e.g., developers, residents, private sector, man-
agers, etc.) in the co-design and co-implementation of initiatives for
enhancing resilience (Wellmann et al., 2023). It is crucial to involve
vulnerable and marginalized groups in these initiatives, as it can facil-
itate a better understanding of their unique requirements and boost their
abilities to plan, cope with, recover from, and adapt to challenges
(Hasala, Supak & Rivers, 2020). This should be prioritized, given that
adverse events often disproportionately affect vulnerable and margin-
alized groups (Thomas et al., 2019). Engaging such groups, however,
could be challenging given their limited access to technologies and the
precarious living conditions that may deter them from engaging in
collaborative initiatives. Addressing these issues requires support from
economic, nancial, and governance systems. Generally, funding is a
major component of social systems and is key in facilitating interactions
between different components of social-ecological-technological sys-
tems (Kim et al., 2022).
Overall, a better understanding of and attention to the mutually
reinforcing or conicting relationships between social and technological
systems is important to reduce vulnerabilities and accelerate the trans-
formation toward resilience in urban systems (Bixler et al., 2020). This
requires transformations across political, nancial, educational, regu-
latory, and governance structures and policies (Kim et al., 2022). As a
case in point, the transition from siloed to networked and collaborative
governance enables more efcient and effective generation, access, and
sharing of information. Collaborative governance helps mobilize stake-
holders from different sectors to respond and adapt to emerging needs
and collectively manage urban systems toward shared objectives (Bixler
et al., 2020).
3.4.3. Technological-ecological coupling
Technology has traditionally played a key role in human-nature in-
teractions. Humans use technology to efciently harness existing re-
sources to meet their needs and demands. However, due to the limits to
growth, the unsustainable use of technologies has caused major envi-
ronmental problems with socioeconomic ramications in recent de-
cades. For instance, conventional water, energy, building, and
transportation systems (as critical urban infrastructure systems) are
developed with little consideration of the environment (Chen, Long,
Chen, Feng & Hubacek, 2020; Rees & Wackernagel, 2008). To address
this issue, there have been calls for integrated approaches that recognize
the nexus between various systems, such as water, energy, food, and
carbon (Meng, Liu, Liang, Su & Yang, 2019).
The literature emphasizes the need to integrate green and gray
infrastructure to enhance the resilience of urban systems. Benets of
hybrid gray-green infrastructures have been demonstrated across
various sectors such as energy (e.g., photovoltaic-green roofs), water (e.
g., bioswales and rainwater harvesting systems), transportation (e.g.,
green bike lanes), and buildings (e.g., green walls and roofs) (Aboulnaga
& Fouad, 2022; Branny et al., 2022; de S´
a Silva, Bimbato, Balestieri &
Vilanova, 2022; Shaque, Luo & Zuo, 2020). These also provide other
co-benets. For instance, green roofs can also be used for urban farming
(Aboulnaga & Fouad, 2022).
Regarding SETs, the technological-ecological coupling has mainly
been discussed in the context of NbS and smart technologies. Various
ecological systems, such as bioswales, rain harvesting systems, green
facades, green roofs, bio-retention ponds, constructed wetlands, etc.
have been discussed as hybrid technological-ecological solutions that
enhance urban resilience (McPhearson et al., 2022). Creating more
livable, resilient and sustainable cities for current and future generations
is possible by linking technological advancements with green infra-
structure. Moreover, if combined with a transition from conventional
technocratic planning approaches to democratic governance models
that engage citizens in the design and implementation stages, hybrid
technological-ecological solutions can enhance the connection between
individuals and nature (Branny et al., 2022). In addition to providing
co-benets for health and well-being, this can offer opportunities for
better stewardship of natural resources. Investment in hybrid solutions
such as green public transportation networks also offers opportunities to
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Sustainable Cities and Society 99 (2023) 104910
8
regenerate old and low-income neighborhoods, thereby contributing to
social and economic resilience (Branny et al., 2022).
In addition to the above-mentioned co-benets of hybrid
technological-ecological systems, technological solutions are increas-
ingly utilized to improve the efciency and functionality of ecological
systems. Cities need to regularly monitor green infrastructure as the
poor environmental conditions in urban areas result in high mortality
and disease rates among trees, shorter lifespans, and degradation of
ecosystem services when compared to rural environments (Branny et al.,
2022). Among other technologies, satellite-based remote sensing pro-
vides reliable and cost-efcient means for regularly monitoring vege-
tation functionality in urban areas. Remote sensing enables planners and
urban managers to track the functioning of urban green infrastructure
and the ecosystem services that they provide. The specic spatial and
temporal data obtained from remote sensing allow more timely, effec-
tive, and efcient management of green infrastructure. The data can be
analyzed to assess urban trees health and diversity and evaluate the
environmental pressures they face, including droughts and heat waves.
Urban authorities can use these real-time data to swiftly respond to
emerging needs and uctuating conditions if necessary (Branny et al.,
2022; Wellmann et al., 2023).
Apart from remote sensing, other technological solutions (e.g.,
sensor networks, the Internet of Things, smart meters, etc.) are available
to monitor the performance of urban infrastructure. Those could
improve the efciency and functionality of transportation, buildings,
energy, and water systems. Such improvements provide ecological
benets (e.g., reducing energy consumption, stormwater management,
habitat diversication, biodiversity conservation, etc.). They also facil-
itate socioeconomic gains related to cost-efciency, sense of place,
emergency management, etc. (Branny et al., 2022; Wellmann et al.,
2023). Needless to mention, the real-time data sensing and analysis
capacities offered by smart technological solutions allow having a better
understanding of the changing climatic conditions and the necessary
response and adaptation measures that should be taken by technological
and ecological systems (Ariyaningsih & Shaw, 2022).
Overall, technological-ecological coupling offers opportunities to
strengthen different abilities across different stages, including planning
(e.g., foresight capacity), absorption (e.g., exibility), recovery (e.g.,
agility and timely response), and adaptation (e.g., learning and behav-
ioral changes).
3.4.4. Social-ecological-technological coupling
The above-mentioned bilateral couplings between social, ecological,
and technological components demonstrate the signicance of holistic
and integrated approaches for building resilient urban systems. In-
teractions between these components shape the dynamics of urban
systems in a collective way. Attention to and optimal management of
these interactions is critical to developing resilient urban systems (Kim
et al., 2022). Therefore, considering all components is necessary when
taking action to enhance resilience to different hazards and stressors.
One tangible example is urban heat (See Box. 1). Air conditioning is an
essential component of technological solutions increasingly used to
mitigate urban heat. However, it alone cannot effectively solve the issue.
On the one hand, excessive reliance on air conditioning will further
increase the cooling demand by exhausting heated air into the envi-
ronment; on the other hand, low-income groups may not afford air
conditioning systems. Therefore, this technological solution should be
coupled with and embedded into other solutions such as refurbishment
of building infrastructure to promote passive cooling (technological),
expansion of green infrastructure systems to regulate urban microcli-
mate and offer other ecosystem services (ecological), awareness cam-
paigns to enhance adaptive behavior and capacity of people (social), and
institutional and managerial practices to minimize disproportionate
impacts on low-income and vulnerable groups.
Kim et al. (2022) explain how the SETS approach has been adopted
to deal with extreme heat in Phoenix, Arizona. As temperatures rise
during the summer season in the city, the electrical demand for cooling
also escalates. This surge in demand pushes the power grid to its critical
limits and can result in power outages that have severe consequences,
including loss of life. While technical measures such as upgrading old
electrical infrastructure and installing backup generators are necessary
to solve this problem, they cannot be considered stand-alone solutions
due to cost implications and limitations posed by extreme weather
conditions. Therefore, alternative solutions become necessary. To this
end, local authorities have been collaborating with vulnerable com-
munities by adopting a systemic approach that leverages diverse sus-
tainable energy transition strategies embedded in social solutions, such
as educational programs aimed at teaching children safe practices for
handling heat during summer breaks and provision of funds to home-
owners to improve their homesinsulation. Such initiatives are essential
for enhancing adaptive capacity. In addition, investment in the expan-
sion of green infrastructure and shading has been adopted as strategic
ecological measures to reduce ambient air temperature. This combined
SETS approach provides a comprehensive solution to the problem of
power grid failure and contributes to climate change adaptation and
mitigation (Kim et al., 2022). While not discussed in the reviewed
literature, integrated SETS approaches can also be utilized to improve
resilience to extreme cold. As a case in point, Balsas (2021) show how
the underground space can be optimized to design walkable environ-
ments during cold winters in Albany, New York, thereby contributing to
socioeconomic resilience. This requires considering interactions among
multiple factors, such as building design guidelines, aesthetics, and
climatic conditions.
An exemplary case of technological innovation is the development of
digital tree inventories, which have been made possible through satel-
lite- and sensor-based monitoring techniques. These advanced tools are
capable of providing instant and up-to-date information about the status
of urban greenery and soil health. As a result, they play an essential role
in identifying when human intervention becomes necessary to ensure
that these vital elements remain healthy within our citiesecosystem. By
enabling real-time data analysis, this innovative solution provides pol-
icymakers with valuable insights into their decision-making processes
concerning urban planning policies and environmental management
practices. The application of this methodology guarantees a deeper level
of communication between humans and nature, ultimately resulting in
an augmentation of urban forest management that can effectively sus-
tain healthy tree growth, ensure the survival of trees, and maintain
ecological balance amidst challenging city environments. Looking at it
from a SET standpoint, such innovative techniques hold promising po-
tential for promoting responsible environmental behavior amongst in-
dividuals by fostering attentiveness toward urban biodiversity
conservation efforts. They could help increase human awareness about
sustainability concerns within cities - enabling efcient maintenance
methods to strengthen environmental resilience while bolstering
biodiversity levels across metropolitan areas (Branny et al., 2022).
The Melbourne Urban Forest- Visual program also serves as an
exemplary initiative that strives to promote active social engagement by
employing various strategies. Through the utilization of a state-of-the-
art digital platform, it encourages citizens to delve deeper into the in-
tricacies of their citys publicly managed urban forest ecosystem. By
providing access to ‘big tree data, individuals can initiate discussions
and gain insights about vital aspects such as ecosystem services. This
system meticulously tracks approximately 70,000 trees under municipal
ownership in Melbourne, including essential details concerning each
trees health status and projected lifespan. The interface facilitates easy
navigation for users since all trees on public right of way are strategi-
cally placed on an interactive map alongside comprehensive site-specic
information highlighting current diversity levels and canopy cover sta-
tistics, among other performance metrics within the greater context of
the urban forest landscape. What sets this innovative program apart
from others is its ability to empower residents with invaluable tools
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Sustainable Cities and Society 99 (2023) 104910
9
designed explicitly for visualization purposes while also promoting un-
derstanding regarding the unique values of the citys diverse ecosys-
tems. The implementation of this strategy in 2012 has enabled the City
of Melbourne to acquire citizens social-ecological viewpoints on trees
and effectively interact with their diverse and subjective attitudes to-
ward them. As a result, thousands of trees have been planted every year
through citizensparticipation (Branny et al., 2022).
The examples discussed above serve as a powerful illustration of the
remarkable potency that social-ecological-technological approaches
hold in boosting urban resilience and fostering positive socioeconomic
outcomes. Moreover, their potential for addressing pressing urban
challenges through multifaceted systemic tactics cannot be overstated.
By taking a holistic approach to problem-solving, these strategies offer
transformative solutions that go beyond supercial xes and create
lasting impacts at every level of society. More opportunities for the
promotion of coupled social-ecological-technological approaches can
emerge with the rapid technological advances. For instance, disruptive
technologies such as digital twins or metaverse may make it easier to
adopt systems-based approaches to examine various interactions across
social, economic, ecological, and technological domains. They may also
facilitate a better engagement of different stakeholders in actions toward
urban resilience.
4. Summary and conclusions
To effectively promote sustainable and resilient urban futures and
address the complex challenges faced by cities, it is imperative that we
undertake transformative changes in the way our cities are designed,
built, and managed. Urban planners must collaborate closely with other
experts and stakeholders, including architects, ecologists, engineers, and
policy makers, to create innovative solutions for various issues such as
climate change, resource depletion, and social inequality. This collab-
orative approach should not be limited to professionals alone; govern-
ment bodies at various levels must join hands with private entities and
local communities to bring about these necessary changes. This collec-
tive effort will foster sustainable growth while ensuring equitable access
to resources across all urban areas - regardless of socioeconomic back-
ground or geographic location (Bixler et al., 2020).
The incorporation of transdisciplinary approaches is necessary as
urban systems entail complex dynamics that cannot be comprehensively
understood through any specialized disciplinary perspective (Bixler
et al., 2020; Hamborg, Meya, Eisenack & Raabe, 2020; McPhearson
et al., 2022). Such transdisciplinary and integrated approaches will
facilitate better linkages between urban systemssocial, ecological, and
technological components. Otherwise, siloed approaches that fail to
Box 1
An example of SETS approach for addressing urban heat.
The SETS approach can help planners and policy makers deal with urban heat issues. Among other things, it can help address trade-offs that may
emerge when isolated or bilateral measures are taken. For instance, as shown in Figure below Fig. 5, air conditioning as a technological (T)
measure may fail to address the heat issue as it can cause positive feedback loops (i.e., further intensify urban heat through heat exhaust) and
may also not be affordable. Isolated ecological (E) measures such as urban greening may also have limited impact due to distribution and
accessibility issues. Similarly, social (S) measures such as promoting behavioral changes to reduce reliance on air conditioning may not be
sufcient due to limits to adaptation. Bilateral approaches can address these issues to some extent. For example: integrating green infrastructure
into building design technologies (T-E) reduced the demand for cooling; institutional measures to ensure equitable distribution of urban
greenery (S-E) helps reducing disproportionate impacts on certain social groups; and funding to enhance building insulation (S-T) reduces
demand for air conditioning. Combining all these measures (S-E-T) allows minimizing potential trade-offs and maximizes synergies.
Fig. 5. An example showing how the SETS approach can provide opportunities for addressing urban heat challenges in cities.
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Sustainable Cities and Society 99 (2023) 104910
10
consider complex interactions between different components may be
followed. When different social, ecological, and technological compo-
nents are linked to each other, a system is likely to be more resilient and
capable of enduring risk. In other words, systems that only pay attention
to one component are more vulnerable (Hamborg et al., 2020).
Adopting SET approaches also helps avoid trade-offs. Indeed, trade-
offs may emerge as socio-technical approaches may exclude ecological
issues, socio-ecological approaches may overlook the role of technology,
and technological-ecological issues could have negative impacts on the
social sphere (Bixler et al., 2019; Iwaniec, Cook, Davidson,
Berbes-Blazquez & Grimm, 2020). For example, investments in green
infrastructure have the potential to enhance the desirability of resi-
dential areas resulting in elevated property values. Consequently, in-
dividuals with limited nancial resources may be compelled to relocate
and inadvertently become more susceptible to natural hazards that
nature-based remedies are meant to mitigate. To circumvent such
inadvertent outcomes associated with green gentrication, it is neces-
sary to pay greater attention to comprehending the interrelationships
between social dynamics, ecological factors, and technology involved
therein McPhearson et al. (2022). Indeed, studies indicate that green
infrastructure projects which are not inclusive and lack effective plan-
ning can result in heightened levels of social inequality, as individuals
from underprivileged backgrounds may be compelled to relocate or
denied access to the advantages offered by enhanced ecosystem services
(Ward et al., 2019). SETS approach also takes into account the various
trade-offs that arise with respect to scale. By adopting this approach, one
can ensure that boosting resilience at a certain scale does not come at the
expense of reduced resilience at other scales. Adopting this compre-
hensive approach makes it possible to understand better and address the
complex urban dynamics vital for promoting sustainable development
across different scales (Olsson et al., 2014).
The SETS approach also has the potential to prevent cities from
becoming locked-in into unfavorable trajectories with implications for
the people and the planet. It is argued that self-perpetuating social,
ecological, and technological feedback can result in lock-ins that impede
transitions to different regimes or trajectories. This inclination toward
lock-in into established patterns has a negative impact on the ability to
adapt effectively to emerging challenges and possibilities (Olsson et al.,
2014). A case in point is technological lock-in, when the emphasis on
improving specic characteristics such as resistance and robustness
comes at the cost of compromising others like exibility and adapt-
ability. The implementation of technological xes to bolster short-term
preparedness can impede transformative resilience and amplify
long-term vulnerabilities (Butler et al., 2017; Munoz-Erickson et al.,
2021). Holistic and plural approaches allow accounting for emerging
threats through proper preparatory, response, and adaptation measures.
Despite its signicance, the task of integrating these research areas
presents signicant challenges, primarily due to the distinct values and
characteristics inherent in social, ecological, and technological elds.
Historically, each eld has been explored independently, leading to a
lack of emphasis on their integration. This deciency may have also
been translated into implementation and practice. Indeed, technological
advancement has frequently taken place without sufcient consider-
ation for maintaining ecological or social integrity; moreover, it tends
towards a top-down approach while disregarding user needs and pref-
erences (Mehvar et al., 2021; Olsson et al., 2014).
In order to successfully integrate SETs approaches and tackle urban
challenges, it is crucial to implement multi-level and polycentric
governance strategies. These strategies are essential as they cover
various spatial and temporal scales, enabling a comprehensive under-
standing of the resilience cycles in cities while linking different social-
ecological and technological aspects. Nevertheless, implementing
these measures poses signicant difculties as it requires operating
across multiple political entities that may have conicting interests or
priorities. The challenge lies in inuencing key intervention areas and
actors that are widely dispersed geographically and temporally;
additionally, they may not always be easily accessible (Bixler et al.,
2020; Smith & Stirling, 2010).
Despite the various challenges faced, we hope this study will expand
our understanding of the intricate concept of social-ecological-
technological resilience and allow improved communication of its
principles to interested stakeholders. One key issue to be mentioned is
that the literature is dominated by epistemological approaches, and
limited empirical research exists. Accordingly, the insights reported here
may offer limited practical lessons to facilitate better operationalization
of the concept. To address this issue, we suggest conducting case studies
in different contexts that show real-world examples of resilience in the
context of SETS. Another limitation of this study is that we have relied
only on peer-reviewed literature indexed in the WoS and Scopus. We call
for future studies that also examine gray literature and technical reports
to better reect discussions from other sectors such as policy. Including a
broader range of literature and insights from different stakeholders
could also provide means to developing standards and guidelines for
assessing the resilience of SETS. Furthermore, as this is a concept in
transition, follow-up studies are needed to understand SETS and their
dynamics better. Such studies should also examine how the SETS
approach is aligned with and related to other approaches to conceptu-
alize urban resilience (e.g., ‘ecological-social-economic). That would
allow developing a more comprehensive approach that considers mul-
tiple aspects of urban resilience. In turn, this would also help to un-
derstand better how SETS approach can integrate innovative and
disruptive solutions to deal with emerging risks that may undermine
urban resilience. Finally, this review showed that the literature is
dominated by studies that focus on certain stressors (e.g., heat) in the
context of specic sectors (e.g., NbS). Future research should further
examine the resilience of SETS in context of other stressors and sectors to
obtain a more comprehensive understanding.
Declaration of Competing Interest
The authors declare that they have no known competing nancial
interests or personal relationships that could have appeared to inuence
the work reported in this paper.
Data availability
Data will be made available on request.
Appendix
Search string
TS
2
=(("social-ecological-technical" OR "social, ecological, and
technical" OR "social, ecological, technical" OR "socio-ecological and
technical" OR "socio-ecological-technical" OR "social, ecological, and
technological" OR social-ecological-technolog*" OR "social, ecological,
and technolog*" OR "social, ecological, technolog*" OR "socio-ecological
and technolog*" OR "socio-ecological- technolog*" OR "social, ecolog-
ical, and technolog*" OR social-ecological- infrastructur*" OR "social,
ecological, and infrastructur*" OR "social, ecological, infrastructur*" OR
"socio-ecological and infrastructur*" OR "socio-ecological- infra-
structur*" OR social-ecological system* and socio-technical system*
OR social-ecological system* and social-technical system*OR socio-
ecological system* and socio-technical system* OR socio-ecological
system* and social-technical system* OR social-ecological system*
and socio-technological system* OR social-ecological system* and
social- technological system* OR socio-ecological system* and socio-
2
Note that this is the search string used in WoS. For Scopus, we have used the
TITLE-ABS-KEY eld.
A. Shari
Sustainable Cities and Society 99 (2023) 104910
11
technological system* OR socio-ecological system* and social- tech-
nological system* OR social-ecological system* and socio-
infrastructur* system* OR social-ecological system* and social-
infrastructur*system* OR socio-ecological system* and socio- infra-
structur*system* OR socio-ecological system* and social- infra-
structur*system*OR socio-eco-technicalOR SETSOR SET) AND
(urban resilience OR resilient cities OR city resilienceOR resil-
ient cityOR resilient urban))
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... Human activities directly affect the functioning of the planet, modifying its ability to recover [12,13]. Currently, resilience has been developed for use in many fields, and a growing amount of research demonstrates the need for an integrated methodology to enhance resilience in social, ecological, and multiple fields [14][15][16]. The resilience of social-ecological systems has been extensively studied [4,[17][18][19], however, social-ecological systems could not fully reflect the sustainability of urban development, and more complex dimensions and intuitive scales need to be taken into account [20]. ...
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