Aquaculture Europe 2026

September 28 - October 1, 2026

Ljubljana, Slovenia

Add To Calendar 01/10/2026 15:00:0001/10/2026 15:15:00Europe/ViennaAquaculture Europe 2026RETHINKING THE RESPONSIBLE APPLICATION OF NATURE-INCLUSIVE DESIGN IN MARINE INFRASTRUCTURE TO RESTORE ECOSYSTEMS AND ENHANCE BIODIVERSITYMarmorna 2The European Aquaculture Societywebmaster@aquaeas.orgfalseDD/MM/YYYYaaVZHLXMfzTRLzDrHmAi181982

RETHINKING THE RESPONSIBLE APPLICATION OF NATURE-INCLUSIVE DESIGN IN MARINE INFRASTRUCTURE TO RESTORE ECOSYSTEMS AND ENHANCE BIODIVERSITY

S Degraer 1, L Cornacchia2*, A Ziemba2,3, T Agardy4, S van den Burg5, K van de Braak6, L van Duren2, A Declercq7, M Eggermont7, A Van Gerven1, T Kerkhove1, I Moulaert8, T Patel1, J Kjerulf Petersen9, M Poelman10, V Stratigaki11, 12, E Strothotte13, J Vanaverbeke1, G El Serafy2,3

1 Royal Belgian Institute of Natural Sciences (RBINS), Operational Directorate Natural Environment, Marine Ecology and Management, Vautierstraat 29, 1000 Brussels, Belgium

2 Deltares, P.O. Box 177, Delft 2600 MH, The Netherlands

3 Delft University of Technology, Mekelweg 2, Delft 2628 CD, The Netherlands

4 Sound Seas, Bethesda, MD, USA

5 Wageningen Social and Economic Research, Wageningen Research, Prinses Beatrixlaan 582 – 528, 2595 BM Den Haag, the Netherlands

6 Sustainable Aquaculture Solutions, The Netherlands

7 Laboratory of Aquaculture and Artemia Reference Center, Faculty of Bioscience Engineering, Ghent University, Coupure Links 653, 9000, Ghent, Belgium

8 Flanders Marine Institute (VLIZ), Jacobsenstraat 1, 8400 Ostend, Belgium

9 National Institute of Aquatic Resources, Technical University of Denmark, Section for Coastal Ecology, Kemitorvet, DK-2800 Kgs Lyngby, Denmark

10 Wageningen Marine Research, Wageningen University and Research, P. O. Box 77, 4400 AB Yerseke, The Netherlands

11 Jan De Nul Group, Tragel 60, 9308 Hofstade-Aalst, Belgium

12 Coastal Engineering Research Group, Faculty of Engineering and Architecture, Ghent University, 9000, Ghent-Zwijnaarde, Belgium

Nature-inclusive design (NID) of marine infrastructure refers to the creation of optimized artificial habitat to locally enhance biodiversity. In essence, NID comprises the local addition of something non-natural to infrastructure with the aim of providing habitat for biodiversity assets in its widest sense. In its purest sense, NID is inspired by how the local environment would be without the infrastructure being present. However, NIDs of marine infrastructure often comprise actions that promote biodiversity which does or did not naturally occur at that location.

In this presentation, we review existing definitions of NID and introduce the perspective of the ULTFARMS project consortium (Degraer et al., 2026). We propose a clear distinction between three different types of NID: (1) restorative NID, linked to the restoration of lost local ecosystem values, and (2) creative NID, referring to artificially created ecosystem assets and containing either (2a) optimized infrastructure or (2b) add-on structures. Restorative NID refers to measures which facilitate and speed-up nature restoration, while creative NID refers to measures to boost biodiversity "beyond the natural".

Beyond the importance of distinguishing different types of NID, it is important to also reflect on which biodiversity assets we elect to boost. We argue that NID should move beyond a focus on species richness towards supporting functional ecosystem assets, which also provide better options for climate-proof NID designs. To adopt NID in an offshore renewables context, it is imperative to hold our horses and carefully consider what is the target to be achieved and how to get there. Moreover, we highlight that NID interventions carry potential negative impacts such as natural habitat loss, the spread of non-indigenous species and unintended shifts in the food web, with the latter issue being strongly scale-dependent. These risks need to be weighed against the expected ecological benefits. Applying NID in offshore renewable energy therefore requires clear goals, careful selection of the ecological assets that we aim to promote and consideration of potential trade-offs.

In summary, restorative NID can be actively promoted, whereas creative NID requires more careful reflection; NID preferably prioritizes functional ecosystem assets and explicitly considers which ecological values to promote and why.

Acknowledgment

This project has received funding from the European Union's Horizon Europe research and innovation programme under Grant Agreement No 101093888. Views and opinions expressed are however those of the author(s) only and do not necessarily reflect those of the European Union. Neither the European Union nor the granting authority can be held responsible for them.

References

Degraer S., Cornacchia L., Ziemba A., Agardy T., van den BurgS. W.K., van de Braak K., van Duren L.A., DeclercqA., EggermontM., Van Gerven A., Kerkhove T.R.H., MoulaertI., PatelT., Kjerulf PetersenJ., PoelmanM., Stratigaki V., Strothotte E., VanaverbekeJ., El Serafy G. (2026). Rethinking the responsible application of nature-inclusive design in marine infrastructure to restore ecosystems and enhance biodiversity. ICES Journal of Marine Science (in press).