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Editorial
The potential of ecosystem-based management to integrate biodiversity
conservation and ecosystem service provision in aquatic ecosystems
Simone D. Langhans
a,b,c
, Sonja C. Jähnig
c
, Manuel Lago
d
, Astrid Schmidt-Kloiber
e
,ThomasHein
e,f,
⁎
University of Otago, Department of Zoology, 340 Great King Street, Dunedin 9016, New Zealand
Basque Centre for Climate Change (BC3), 48940 Leioa, Spain
Leibniz-Institute of Freshwater Ecology and Inland Fisheries, Müggelseedamm 310, 12587 Berlin, Germany
Ecologic Institute, Pfalzburger Str. 43/44, D-10717 Berlin, Germany
University of Natural Resources and Life Sciences Vienna, Institute of Hydrobiology and Aquatic Ecosystem Management, Gregor Mendel Strasse 33, 1180 Vienna, Austria
WasserCluster Lunz, WG Biger, Dr. Carl Kupelwieser Promenade 5, A 3293 Lunz am See, Austria
abstractarticle info
Available online 03 April 2019 Global aquatic biodiversity keeps declining rapidly, despite international efforts providing a variety of policies
and legislations that identify goals for, and give directions to protecting the world's aquatic fauna and flora.
With the H2020 project AQUACROSS, we have made an unprecedented effort to unify policy strategies, knowl-
edge, and management concepts of freshwater, coastal, and marine ecosystems to support the achievement of
the targets set by the EU Biodiversity Strategy to 2020. AQUACROSS has embraced the concept of ecosystem-
based management (EBM), which approaches environmental management from a social-ecological system per-
spective to protect biodiversity and to sustainably harvest ecosystem services. This special issue includes contri-
butions resulting fromAQUACROSS, which either tackle selected EBM challenges from a theoreticalpoint of view
or apply EBM in one of the selected case studies across Europe. In this article, we introduce relevant topics, ad-
dress the most important lessons learnt, and suggest where research should go with aquatic EBM. We hope
that this special issue will foster and facilitate the uptake of EBM in aquatic ecosystems and, therewith, provide
the on-ground applications needed for evaluating EBM's utility to safeguard aquatic biodiversity.
© 2019 Published by Elsevier B.V.
Keywords:
Aquatic ecosystems
Ecosystem-based management
Nature's contributions to people
Policy making
Resilience
Social-ecological system
Spatial planning
1. Introduction
Aquatic ecosystems including freshwater, coastal and marine envi-
ronments are rich in biodiversity, providing a diverse array of habitats
to species while delivering numerous economic benefits to society
(Bennett et al., 2015). Many of these valuable ecosystems are at risk of
being irreversibly damaged by human activities and pressures, includ-
ing pollution, watershed disturbance, water resource development
(sensu Vörösmarty et al., 2010) or invasive species, overfishing, and cli-
mate change (Secretariat of the Convention on Biological Diversity,
2014). These pressures threaten the sustainability of the ecosystems,
their provision of ecosystem services (ESs) and ultimately human
well-being (Vörösmarty et al., 2010). So far, existing EU policies have
been unable to halt or even reverse the trend of declining aquatic biodi-
versity (Voulvoulis et al., 2017). In Europe, the current broad policy
landscape, such as the EU Water Framework Directive (Council of the
European Communities, 2000), the Marine Strategy Framework Direc-
tive (Council of the European Communties, 2008), the Habitats Direc-
tive (Council of the European Communities, 1992) or the Renewable
Energy Directive (Council of the European Communities, 2009)among
others, implies that sustainable management solutions require coordi-
nation and cooperation between different policy areas tacklingfreshwa-
ter, coastal, and marine ecosystems. In addition, innovative business
solutions and public-private engagement are needed to consider and
manage aquatic ecosystems as truly social-ecological systems
(Virapongse et al., 2016).
2. What is ecosystem-based management?
To support long-term sustainable management in aquatic ecosys-
tems, strong policy integration in terms of objectives, knowledge base,
Science of the Total Environment 672 (2019) 1017–1020
⁎Corresponding author at: University of Natural Resources and Life Sciences Vienna,
Institute of Hydrobiology and Aquatic Ecosystem Management, Gregor Mendel Strasse
33, 1180 Vienna, Austria.
E-mail address: thomas.hein@boku.ac.at (T. Hein).
https://doi.org/10.1016/j.scitotenv.2019.04.025
0048-9697/© 2019 Published by Elsevier B.V.
Contents lists available at ScienceDirect
Science of the Total Environment
journal homepage: www.elsevier.com/locate/scitotenv
methods and tools, as well as engagement and knowledge exchange, is
essential. The integrative nature of ecosystem-based management
(EBM) shows in theory a lot of promise for supporting all of the
above. Ultimately, EBM is a collaborative management approach used
with the intention to restore, enhance and protect the resilience of an
ecosystem so as to sustain or improve ESs and protect biodiversity,
while considering nature and society, i.e. the full social-ecological sys-
tem (Gómez et al., 2016a;Gómez et al., 2016b;Langhans et al., 2019).
Hence, EBM treats human society as one of the essential elements that
constitute an ecosystem, making use of different concepts such as inte-
grated ecosystem assessments, marine spatial planning, resilience
thinking, and complex adaptive systems (Table 1).
3. Ecosystem-based management in the AQUACROSS project
With this special issue we advance and, therewith, foster the under-
standing and application of EBM in aquatic ecosystems by showcasing
selected results of AQUACROSS –an EU-funded Horizon 2020 project
(Lago et al., 2019). Finished in November 2018, AQUACROSS aimed to
support EU efforts to enhance th e resilience of aquatic ecosystems, man-
aged as a continuum, and to stop the loss of aquatic biodiversity in line
with the EU2020 Biodiversity Strategy as well as to ensure the ongoing
provision of ESs. Hence, AQUACROSS provided the perfect opportunity
to advance the knowledge base and demonstrate practical applications
of the EBM concept across a range of European case studies. One part of
AQUACROSS was the development of a common and free of charge
open-access online platform –the AQUACROSS Information Platform
(http://dataportal.aquacross.eu/)–to disseminate research and innova-
tion results. On one hand, this platform acted as a publishing tool for
project partners focusing on the AQUACROSS case studies. On the
other hand, it is now a central access point for data on different types
of aquatic ecosystems, biodiversity, and EBM practices addressed to
the entire scientific community, stakeholders, and policy makers. Sup-
ported by the Information Platform, we believe that AQUACROSS
made an unprecedented effort to unify policy strategies, knowledge,
and management concepts of freshwater, coastal, and marine ecosys-
tems to support the cost-effective achievement of the targets set by
the EU Biodiversity Strategy to 2020 (European Commission, 2011).
4. Roadmap to the special issue
ThespecialissueopenswithLago et al. (2019),whodescribetheaims
and approaches of AQUACROSS, its conceptual framework and case stud-
iesacrossEurope(Fig. 1). Gómez et al. (2016b) introduce an integrated
assessment framework (further called the AQUACROSS assessment
framework) to help operationalise the aims of AQUACROSS. The assess-
ment framework is based on the water-biodiversity-nexus as the corner-
stone to coordinate sectoral policies for sustainabl e land use, the provision
of ESs, and biodiversity conservation. Core elements of the AQUACROSS
assessment framework include i) harmonising and streamlining environ-
mental policies within the context of biodiversity conservation strategies,
ii) coordinating policies in different ecosystems (freshwater, marine,
coastal) where different legislation applies, iii) amalgamating the relevant
analytical approaches for the assessment of aquatic ecosystems and iv)
addressing social-ecological systems in a truly holistic way.
A suite of studies identifies individual challenges associated with the
operationalisation of the AQUACROSS assessment framework and pro-
pose ways forward. O'Higgins et al. (2019) choose the Ria de Aveiro
case study in Portugal to demonstrate a methodology to characterise
supply and demand for ESs. This is done on the basis of spatial proper-
ties and interdependencies between the lagoon and locations outside
of the management area, and economic properties. Culhane et al.
(2019) use insights from the case studies to explore aggregated impact
risks from human activities on ES supply components across a range of
aquatic ecosystems, including lakes, rivers, inlets, and coastal realms.
Daam et al. (2019) analyse the causal links between aquatic biodiversity
and ecosystem functioning. Teixeira et al. (2019) identify linkages on
the supply-side of the social-ecological system, i.e. from biodiversity to
ES supply, for all of the case studies. Borgwardt et al. (2019) link
human activities through pressures to different ecosystem components
in fresh-, coastal and marine waters, to identify the risk by each impact
Table 1
EBM components relevant for the protection of aquatic biodiversity, explanations of the
components and examples of how they were considered in individual studies of this spe-
cial issue.
EBM component Explanations of EBM
component
AQUACROSS examples
1) EBM considers
ecological integrity,
biodiversity,
resilience and ESs
- Joint evaluation of
multiple ESs
- Protection of ecosystem
integrity as a means to
preserve ESs and
biodiversity
- Focus on multiple
benefits or environmental
services
Consideration of multiple
ESs to select protected area
sites that deliver broader
benefits than just
biodiversity protection
(Barbosa et al., 2019) and
social equity (Domisch
et al., 2019)
2) EBM is carried out at
appropriate spatial
scales
- Consideration of
ecosystems rather than
jurisdictional boundaries
- Can require
transboundary
cooperation
Selection of sites for
efficient and effective river
restoration based on a
multi-national catchment
rather than at the national
level, to reach better
biodiversity outcomes at
lower costs (Funk et al.,
2019)
3) EBM develops and
uses
multi-disciplinary
knowledge
- Understanding of the
ecological and social
systems to be managed
- Drawing on local &
traditional knowledge
Combination of a
semi-quantitative
description of the
social-ecological system
with stakeholder input to
identify drivers and
pressures to be managed
(Piet et al., 2019)orto
meet societal goals (Lillebø
et al., 2019;
Martínez-López et al.,
2019a); using spatial
ecological and economic
data to map the most
cost-effective location to
meet biodiversity goals
(Barbosa et al., 2019,
Domisch et al., 2019,
Kuemmerlen et al., 2019)
4) EBM builds on
social-ecological
interactions,
stakeholder
participation, and
transparency
- Balance of ecological and
social concerns
- Prominence to
transparent and inclusive
decision making
- Power to collective
action by building
consensus on a shared
vision for the future
Development of
semi-quantitative models
with stakeholder input,
increasing scientific
knowledge and building
stakeholder understanding
and consensus (Lillebø
et al., 2019;Robinson
et al., 2019)
5) EBM supports policy
coordination
- Creation of new
opportunities of pursuing
different policy objectives
simultaneously by
breaking silos
Targeting river,
transitional estuary, and
coastal area objectives
therewith aligning
biodiversity and Water
Framework Directive
indicator monitoring and
evaluation (Lillebø et al.,
2019)
6) EBM incorporates
adaptive
management
- Ability to respond to a
range of possible futures
- Weighting short-term
actions against long-term
benefits of alternative
actions
Development of scenarios
that incorporate
projections of population
and economic growth to
include them in
management planning to
make better informed
decisions (Kuemmerlen
et al., 2019,Piet et al.,
2019)
1018 Editorial
chain, providing a more integrated view on different aquatic ecosys-
tems. Martínez-López et al. (2019b) develop five ES models that can
be applied to any place in the world without user input, while giving
the option to customise the models with context-specific data.
Domisch et al. (2019) analyse potential management plans for the Dan-
ube River basin that spatially optimise areas for conservation and ESs
delivery, while accounting for social equity. Piet et al., (2017) introduce
a cyclical adaptive EBM approach, each cycle consisting of four phases:
i) the identification of the relevant societal goals, ii) establishing the
knowledge base and identifying the main threats to the achievement
of the societal goals, iii) EBM planning, and iv) EBM implementation,
monitoring, and evaluation.
Seven manuscripts describe specific applications of the AQUACROSS
assessment framework and EBM measures in selected case studies. Piet
et al. (2019) provide guidance for (more)EBM in the North Sea based on
an evaluation of the effectiveness of specific management measures in
contributing to the conservation of marine biodiversity, while consider-
ing a range of societal goals such as sustainable food supply or clean en-
ergy. Barbosa et al. (2019) propose a spatial design for a Green and Blue
Infrastructure network and the implementation of EBM measures in
freshwater, coastal, and marine realms in a transboundary setting,
namely the Intercontinental Biosphere Reserve of the Mediterranean
in Andalusia and Morocco. Funk et al. (2019) prioritise river-
floodplain segments for conservation and restoration along the whole
Danube River, based on the multi-functionality of these segments re-
garding biodiversity and selected ESs, the availability of remaining
semi-natural areas, and the reversibility of multiple human activities in-
cluding flood protection, hydropower, and navigation. Robinson et al.
(2019) explore the dependencies and interactions in the Lough Erne
catchment in Northern Ireland with a social-ecological system ap-
proach, focusing on exploring how individual stakeholders perceived
the goals to be affected by both biodiversity and activities found in the
catchment. Lillebø et al. (2019) develop a collaborative EBM plan to-
gether with different stakeholder groupsin the Ria de Aveiro coastal ter-
ritory in Portugal using a spatial multi-criteria analysis approach aiming
to mitigate foreseen changes connected to human activities and poten-
tial conflicts. Martínez-López et al. (2019a) focus on the same area to
find optimal management actions to compensate for the predicted
loss of biodiversity due to the floodbank extension in the Baixo Vouga
Lagunar. Finally, Kuemmerlen et al. (2019) present a strategy based
on decision support methods that aggregates reach-scale ecological as-
sessments to describe the ecological state of entire catchments. They
test the approach for selected sub-catchments in the Swiss Plateau
and recommend a set of spatial criteria, which represent ecological pro-
cesses orconcepts such as migration, resilienceand habitat diversity in a
spatially explicit way.
5. Lessons learnt
EBM embraces six broader components (Table 1), reaching far beyond
traditional management approaches. Equipped with these six compo-
nents, EBM should be able to tackle pressing current and future environ-
mental challenges. Indeed, the case studies described in this special issue
exemplify individual components, i.e. the strengths of EBM (Table 1,col-
umn 3). In summary the case study applications show that EBM is practi-
cally doable and can be used to design more effective, efficient, and
equitable management measures and policies for protecting biodiversity.
The holistic management perspective, which is taken in EBM, allows
trade-offs between ESs to be considered and takes several societal goals
into account. EBM approaches promote the most efficient allocation of fi-
nancial resources, while contributing to the sustainability of the whole
social-ecological system. Hence, we conclude that this comprehensive ap-
proach has the potential to unveil win-win situations.
There are also strengths from a practitioner's perspective: EBM sup-
ports the integration of objectives and policy coordination, develops and
uses quantitative, qualitative and spatial science, places stakeholders at
the center of biodiversity management, recognises beneficiaries beyond
biodiversity for its own sake, considers long-term and transboundary im-
pacts, as well as prioritises evaluation and ongoing adaptive management.
6.Wheretogofromhere?
To facilitate EBM implementation in aquatic systems and across differ-
ent realms, four key challenges need particular attention: 1) Successful
EBM requires well-defined, long-term monitoring and evaluation pro-
cesses, considering time and costs, and relying on consistency in gover-
nance. This is, however, not unique to EBM, but a prerequisite for any
adaptive management process. 2) EBM is not revolutionary, but is likely
Fig. 1. Roadmap to the papers of this special issue. Manuscripts labelled with an asterisk* are deliverables of the project AQUACROSS.
1019Editorial
beneficial in most circumstances providing innovative solutions sup-
ported by stakeholders. The conditions under which an EBM process
will yield superior results need to be identified. 3) EBM can appear diffi-
cult to practitioners and stakeholders and, therefore, they may hesitate
to use the concept. Hence, EBM applications always need a fair amount
of time to be dedicated to communication and discussions. 4) Tackling
transboundary issues, e.g. across geographic boundaries or legislative
landscapes is supported by EBM, but certainly remains challenging in
practice.
Besides these challenges, integrating biodiversity protection into
sectoral policy agendas and communicating the complex issue of biodi-
versity to different stakeholders generally needs more attention. Fur-
thermore, research has to make an effort to better understand the
links between biodiversity, ecosystemsand ESs, to further develop prac-
tical models capturing the social-ecological system to support effective
decision making across scales, and to support the transition from EBM
as an academic concept to actually implement it on ground. We believe
that EBM shows great potential for managing aquatic systems in a sus-
tainable way, if future research and practical development is able to
meet the remaining challenges.
Acknowledgements
We thank all the authors for theircontributions,the many colleagues
for reviewing manuscripts, and Damian Barcélo and Elena Paoletti for
editing the VSI. This work was funded by theEuropean Union's 2020 Re-
search and Innovation Programme under the grant agreement No.
642317. SDL has received additional funding from the European Union's
Horizon 2020 Research and Innovation Programme under the Marie
Skłodowska-Curie grant agreement No. 748625. SCJ acknowledges
funding for the “GLANCE”project (Global Change Effects in River Eco-
systems; 01 LN1320A) through the German Federal Ministry of Educa-
tion and Research (BMBF).
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1020 Editorial