Open Access
Review
Issue
Aquat. Living Resour.
Volume 32, 2019
Article Number 13
Number of page(s) 9
DOI https://doi.org/10.1051/alr/2019012
Published online 30 May 2019

© EDP Sciences 2019

Licence Creative Commons
This is an Open Access article distributed under the terms of the Creative Commons Attribution License (http://creativecommons.org/licenses/by/4.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

1 Introduction

The native European Oyster Ostrea edulis once covered vast areas of the open North Sea and other European coastal waters. As an ecosystem engineer it built biogenic reefs and played a key ecological role for the wider ecosystem by providing many essential ecosystem services. O. edulis is a sublittoral species and was abundant up to 50m depth (Kerckhof et al., 2018; Pogoda, 2019). Oysters have been heavily fished as a valuable resource over centuries. During the era of industrialization and the introduction of powered dredging technologies, oyster habitat was fished down to functional extinction in most European regions (Berghahn and Ruth, 2005; Lotze, 2005; Lotze et al., 2005; Thurstan et al., 2013; Duchêne et al., 2015). In many areas oyster fisheries were abandoned as catches were no longer profitable. But bottom trawling for other target species remains a barrier to regenerating structured habitat such as oyster beds or reefs because shellfish habitats are vulnerable to physical impact (Cook et al., 2013). In many European regions, remaining and managed oyster beds, contributing to commercial production, have been severely affected by diseases (e.g. Marteilia, Bonamia) in the 1920s and the 1970s/1980s, which resulted in elevated mortalities (Arzul et al., 2006; Pogoda, 2019). Together with human induced stressors, the absence of broodstock and substrate impedes natural recovery of native oyster populations. Today, natural oyster beds and reefs have vanished or are in a degraded state, with limited ecological function, throughout Europe (Thurstan et al., 2013). This status was reached before the end of the 19th century and consequently, there is a shifted baseline (Pauly, 1995; Alleway and Connell, 2015; Pogoda, 2019) leading to a debate about the extent to which native oysters formed reefs. The current perception of oyster habitat vastly underestimates its historical and ecological significance. Historical fishing reports document “living crusts of shellfish” or “clumps of oysters in the dredges” or “oysters are so often found in clusters on the natural beds instead of singly” (Möbius, 1877; Fulton, 1896; Korringa, 1946). Current experimental research shows that Ostrea edulis is capable of forming biogenic reef structures through shell accretions (Christianen et al., 2018; Merk et al., 2019) and underlines the ecological importance of oysters as biogenic habitat builders. Nature conservation goals need to acknowledge the historical extent and importance of oyster habitat and the role restoration of oyster habitat can play for biodiversity, for the increased production of many fish species and for improving water quality (zu Ermgassen, 2016Hancock and zu Ermgassen, 2018).

In Europe, habitat restoration as a marine nature-conservation measure and obligation of the EU Habitats Directive (European Parliament, 1992, 2008) and the Oslo-Paris Commission (OSPAR recommendation OSPAR, 2010), is a relatively new practice. Some skepticism still exists regarding the risk of negative impacts on the ecosystem in the case of mismanagement or failures. The alternative course, of protection or passive restoration (“allow nature to do the work”) may be supported as a better option (Prach, 2016). However, we argue that for native oysters, breeding is only possible when densities are sufficiently high, in which case protection or passive restoration would suffice. Where the native oyster is either absent or present in very low densities, or shell substrates have been totally removed, active restoration becomes a necessity for the return of native flat oyster reefs. Therefore, restoration trials have to be planned, implemented and communicated carefully, incorporating the benefit of the experience gained from examples in other areas of the world, especially from USA and Australia. For the relatively new field of restoring native flat oyster reefs in Europe, the development of best practice and decision-making tools is of fundamental importance (Metzger et al., 2017). Against this background, partners from science, technology, nature conservation, consultancies, commercial producers and policy-makers founded the Native Oyster Restoration Alliance (NORA) and developed the initial Berlin Oyster Recommendation, which is presented here:

2 BERLIN OYSTER RECOMMENDATION - Bringing back an ecological key-player: principles for native oyster restoration in Europe

2.1 Preface

Oyster habitats are hot-spots of biodiversity and are vital to the health of the surrounding ecosystem but are among the most threatened marine habitats worldwide (Beck et al., 2011). Oyster reefs and beds are biogenic structures formed by oysters that occur at high densities and provide the dominant structural component and significant vertical relief on otherwise unstructured sea-floor (Reise, 2005; OSPAR, 2009). As an ecological keystone-species it offers substrate, spawning ground, food and shelter for many more species (Smyth and Roberts, 2010). Their ecological role can be compared to the function of coral reefs in tropical regions. In Europe, native oysters once formed extensive beds and reefs along North Atlantic coastlines and in the North Sea, even in offshore regions of moderate depth (Olsen, 1883; Gercken and Schmidt, 2014). However, over 90% of former oyster reefs have been lost (Lotze, 2005; Beck et al., 2011).

Over the past two decades, substantial headway has been made in progressing restoration of oyster habitats in the USA. While restoration efforts historically sought to address declines in oyster landings, many recent efforts focus on recovering the valuable and diverse ecosystem services these oyster habitats provide (Luckenbach et al., 2005; Hancock et al., 2006; Peabody and Griffin, 2008). Across Europe, native oyster restoration is also starting to gain momentum. The Oslo-Paris-Commission (OSPAR) included Ostrea edulis on the list of threatened and declining species and habitats, for which restoration measures should be developed and the EU Habitats Directive also calls for the protection, conservation and restoration of biogenic reefs in European waters (OSPAR, 2008). Over the last 3–5 years, several projects have started with the aim of recovering the biodiversity and the ecosystem services provided by oysters (Laing et al., 2005; Shelmerdine and Leslie, 2009; Woolmer et al., 2011; Gravestock et al., 2014; Smaal et al., 2015; Harding et al., 2016).

High fishing pressure and poor shell management practices not only resulted in the decline of living oysters, but also in the loss of the most important natural settlement substrate for oyster larvae: oyster shells (Korringa, 1941; Laing et al., 2005; Airoldi and Beck, 2007). In waters with sufficient larval abundances, the lack of suitable substrate can be the limiting factor for the recovery of oyster populations (Smaal et al., 2015). Throughout much of Europe, a lack of broodstock (adult breeding individuals) in sufficiently high density for successful breeding may also be the reason for low larval abundances. Furthermore, in many European ecoregions the invasive protozoan parasite Bonamia ostreae is present today and able to increase mortality in native oysters (van Banning, 1991; Cáceres-Martínez et al., 1995; Arzul et al., 2006; Culloty and Mulcahy, 2007; Abollo et al., 2008; Laing et al., 2014). Bonamia-monitoring will be an important tool for the selection of eventually tolerant populations.

Against this background the Marine Directorate of the German Federal Agency for Nature Conservation and the Alfred-Wegener-Institute Helmholtz Centre for Polar and Marine research organised a Kick-off Workshop in Berlin “Native oyster restoration in Europe − current activities and future perspectives” with the idea of exploring interest in the foundation of a European Network for Native Oyster Restoration.

The workshop was attended by 65 participants from 11 countries, representing experts from science, nature conservation, commercial production, bio-consulting and policy advisers. It became obvious that despite the existing momentum and will for restoring native oysters and their valuable ecosystem services, several barriers to the successful wide scale uptake of native oyster restoration still needed to be addressed. Addressing these barriers requires the combined focus of a “network” of restoration practitioners as well as academics and managers who recognise the environmental benefits to be gained from restoring this once dominant habitat. Thus, a European “Native Oyster Restoration Alliance” was conceived as an ideal mechanism to accelerate the impact of restoring native oyster habitats in Europe.

The participants of the workshop discussed a number of pertinent issues related to native oyster restoration and protection while:

  • considering that oysters have historically played a critical role both ecologically and economically in marine environments worldwide;

  • noting that globally wild and native shellfish populations − including those throughout Europe − are largely degraded, and their ecosystem service value is similarly reduced;

  • accepting that conditions in many areas are different now from when oysters were abundant 100–200 years ago;

  • confirming that successful oyster restoration projects have been implemented around the globe on various scales;

  • realising that native oyster restoration in Europe should be promoted and facilitated by defined cooperative actions;

  • believing that restoration should be integrated into conservation policy, marine spatial planning and marine development;

  • agreeing that participants and key institutions will work together towards the recovery of native oyster habitat and the associated services on an ecosystem scale.

Following these discussions workshop participants established the Native Oyster Restoration Alliance (NORA) for the protection and restoration of the endangered European oyster.

The undersigned workshop participants (which represented the core group of the European expertise on the subject) formulated a series of specific recommendations. These recommendations are addressed to national, international, intergovernmental agencies, as well as regulators, scientists, NGOs and potential investors of the respective countries and urges them to strongly support these recommendations with the aim to provide a healthy and resilient ecosystem in the North East Atlantic and the North Sea.

2.2 Recommendations

Participants and members of the Native Oyster Restoration Alliance (NORA) agreed on the following recommendations:

  • 1.

    Produce sufficient oysters for restoration of oyster reefs
    Background: Sufficient seed oyster supply is a key limiting factor for native oyster restoration projects in Europe. Translocation between sites of seed oysters or any other size classes from wild beds should be discouraged to avoid increasing the pressure on still existing wild beds and reduce the risk of spreading invasive species and disease.
    Recommendation: Action should be undertaken to support existing hatcheries, spatting ponds and spat collector techniques and to establish new hatcheries and spatting ponds for the production of robust and genetically diverse Ostrea edulis seed. Broodstock sanctuaries should be established and used for local reinforcements.

  • 2.

    Identify and create suitable sites for restoration of oyster reefs
    Background: Restoration projects to recover Ostrea edulis habitat will only succeed in areas where environmental conditions are suitable and no bottom disturbance, e.g. bottom trawl fishery, occurs.
    Recommendation: Sufficient undisturbed and suitable areas should be identified for the restoration and protection of Ostrea edulis in all regions of its indigenous range. This includes the restoration of suitable substrate in some areas. It will be important to identify and afford protection to several major sites in Europe, where:

    • Ostrea edulis was recorded previously but has disappeared (“reintroduction” sites)

    • Ostrea edulis is still present, but in very low density (“reinforcement” sites)

    • Ostrea edulis is abundant with sufficient reproduction and settlement for the habitat to persist in the long term (“conservation” sites)

  • 3.

    Provide suitable substrate for successful recruitment
    Background: Sustainable success of restoration efforts depends on successful recruitment and, therefore, not only on the supply of sufficient larvae but also on the availability of suitable substrate. After their planktonic phase, oyster larvae prefer to settle on oyster shells. Suitable and abundant settlement substrate is a major limiting factor for Ostrea edulis recovery in areas with natural spatfall and of high importance for sustainable restoration.
    Recommendation: Extraction of Ostrea edulis shells from the marine environment for other usages should be stopped. The addition of suitable substrate will ease recruitment of larvae.

  • 4.

    Respect Bonamia-free areas
    Background: In many European ecoregions, the invasive parasite Bonamia is present today. Bonamia ostreae is an invasive protozoan parasite infecting haemocytes of native oysters and inducing physiological disorders, potentially resulting in the eventual death of the animal. High mortality rates have been described for cultivation sites with high densities of oysters and elevated summer temperatures. Despite this, tolerant populations appear to exist in France, The Netherlands, Spain and Ireland. Genetic studies have demonstrated that tolerance to this parasite is heritable and genomic studies have identified QTLs and expressed genes associated with tolerance.
    Recommendation: Research to better understand the biology of the Bonamia parasite and infection dynamics should be encouraged. Biosecurity protocols must be strictly followed in Bonamia-free areas. Any area where there is functional extinction of Ostrea edulis should be treated as a Bonamia-free area. Techniques should be sought to take advantage of any disease tolerance that has developed in broodstock from high disease load areas, without transferring pathogens.

  • 5.

    Create common monitoring protocols
    Background: Native oyster restoration is in its infancy in Europe. There are numerous outstanding questions regarding best practice for restoration of the European native oyster. A shared monitoring protocol will allow lessons and outcomes to be shared between all European restoration efforts. This will reduce duplication of effort and ensure that progress towards successful restoration is as rapid as possible.
    Recommendation: Monitoring protocols that will provide comparable results for projects throughout Europe and for restored sites should be developed and followed. Where possible, monitoring should include the assessment of ecosystem services on a habitat and ecosystem scale.

  • 6.

    Preserve genetic diversity
    Background: The preservation of the genetic diversity of European native oyster populations is of central importance for maintaining its ability to adapt to changing environmental conditions, stress factors (disease, climate change) and to facilitate the long-term survival of native oyster habitats in Europe.
    Recommendation: Established hatchery and pond production protocols should be adapted to preserve the extant genetic diversity of native oysters in Europe.

The full list of contributors to the Berlin Oyster Recommendation is available at noraeurope.eu.

Table 1

Recommendations as listed in the Berlin Oyster Recommendation on the Future of Native Oyster Restoration in Europe. These are based on agreements of participants of the first meeting of the Native Oyster Restoration Alliance (NORA) in Berlin 2017, NORA members and on a literature review focusing on restoration of Ostrea edulis.

3 Current European pilot restoration initiatives

Ostrea edulis survived in coastal and estuarine areas in several European countries, mainly due to management of oyster beds within commercial farming. These managed populations, as well as hatchery produced seed oysters, provide important starting populations for restoration attempts, to be undertaken in areas where any bottom disturbance (such as bottom trawling fishery) is excluded, e.g. Marine Protected Areas. Currently, pilot projects for native oyster restoration are being carried out in UK, France, the Netherlands and Germany.

In England, two restoration projects have been established in locations that historically supported large oyster populations. On the south coast, the Solent Oyster Restoration Project (SORP) was established after catastrophic declines in stock densities and the collapse of a fishery (Gravestock et al., 2014; Harding et al., 2016). It aims to reseed the Solent with oysters, and restore oyster bed habitat to support a self-sustaining population. Since 2017, broodstock oysters are suspended in novel restoration cages from marina pontoons across the Solent to increase reproduction and provide a source of larvae to populate the surrounding seabed. Monitoring of growth, health, survival, reproduction and recruitment is ongoing. In addition, seabed cages containing native oysters were deployed to test their physiological performance and ecosystem service provision at different elevations above the seabed. Effects of density on survival, growth, reproduction, benthic structure and biodiversity are assessed estuary-wide to provide data for future seabed deployment within designated European and UK marine sites. On the east coast, The Essex Native Oyster Restoration Initiative (ENORI) was established in 2011 as a collaboration between oyster fishermen, nature conservation organisations, academia and government regulators. It is restoring self-sustaining populations of native oysters within a Marine Conservation Zone across the Blackwater, Roach, Crouch and Colne estuaries. Broodstock oysters and substrate (shell material) were deployed to the seabed to increase reproduction and recruitment of a nationally important breeding population. ENORI has created an adaptive management fisheries plan to recover native oyster populations which may allow a sustainable fishery.

In Wales, a feasibility study and baseline surveys identified the need for native oyster restoration (Woolmer et al., 2011). In 2019, the Wales Native Oyster Restoration Project has been established by Natural Resources Wales. It will focus on a series of restoration plots and will address fundamental site-specific questions relating to survival, recruitment, density effects, and the impacts of Bonamia disease and non-native species. Associated habitat and biodiversity enhancement will also be assessed.

In Scotland, oyster restoration feasibility studies started in the late 1990s and have recently gained momentum (Shelmerdine and Leslie, 2009; Fariñas-Franco et al., 2018). Oysters have been extirpated for over one hundred years in many sites (Thurstan et al., 2013; Fariñas-Franco et al., 2018). In 2013 the Dornoch Environmental Enhancement Project (DEEP) was initiated. After a feasibility study (Fariñas-Franco et al., 2018), Scottish oysters were successfully translocated to the Dornoch Firth in 2017. Monitoring of growth, health, survival, reproduction and recruitment is ongoing (Sanderson, in prep.). Supporting research projects have been established to examine the contribution oysters make to blue carbon storage as well as the behaviour and therefore likely destinations of oyster larvae from the restoration sites (Rodriguez-Perez et al., 2019). Furthermore, substrate (shell material) was deployed to the seabed to increase recruitment by creating a series of “reefs” and “beds”. These habitats are being populated with oysters, grown by suppliers from across Scotland. Additional restoration projects are planned in Plockton, Ardfern and Loch Ryan.

In France, the flat oyster was once a dominant species in coastal waters, but is now confined to only a few localized environments. Since 2018, the Flat Oyster Recovery project (FOREVER) promotes the reestablishment of native oysters in Brittany (France). It will provide a regional inventory of the main native oyster beds and a detailed analysis of the ecology and dynamics of the still remaining beds in the Bays of Brest and Quiberon. General functional status will be evaluated by density, size structure, mortality, health and genetic status, as well as by a better understanding of the recruitment dynamics within an oyster bed (larval abundance, larval behaviour, settlement processes). Associated benthic diversity and trophic interactions will also be assessed. Restoration and management measures will be implemented in partnership with local stakeholders (fisheries and shellfish farming bodies, regional government authorities, environmental management organizations, e.g. Natura 2000). The development of substrate structures is an important goal to increase recruitment.

In the Netherlands, oyster restoration studies started in 2014. A feasibility study, initiated by the Dutch government, identified potential locations and requirements for restoration, e.g. environmental conditions for survival, growth, reproduction and recruitment (Smaal et al., 2015, 2017; Kamermans et al., 2018a, 2018b). Since 2016, the Voordelta restoration project aims at enlarging an existing nearshore bed of European oyster (O. edulis) and Pacific oyster (Crassostrea gigas) by translocation of Dutch broodstock oysters and by introduction of substrate (shell material) to increase reproduction and recruitment (Sas et al., 2016, 2018). Monitoring of growth, health, survival, reproduction and recruitment is ongoing. Associated benthic diversity was also assessed (Christianen et al., 2018; Sas et al., 2018). In 2018, restoration experiments were started at offshore sites (e.g. Borkum Reef Ground). Monitoring of growth, health, survival, reproduction and recruitment is ongoing.

As the O. edulis population in Lake Grevelingen is infected with Bonamia ostreae (Engelsma et al., 2010) and spreading of the disease should be avoided (Pogoda and von Nordheim, 2019), these oysters can only be used in the nearby Voordelta area (Kamermans et al., 2018c). Recently, O. edulis was rediscovered in the Dutch Wadden Sea (van der Have et al., 2018). At present, it is unknown if these oysters are disease free. Ongoing efforts to supply oysters for Dutch restoration projects focus on local spat collection and hatchery production of disease free, and at the same time disease tolerant, spat.

In the German Bight, the European oyster is believed to be functionally extinct since the 1950s. A feasibility study (Gercken and Schmidt, 2014) and further restoration projects were initiated by the German Federal Agency for Nature conservation (BfN). Since 2016, the testing and development project RESTORE aims at the sustainable restoration of the European oyster Ostrea edulis in the German North Sea. Two experimental sites are located within the historical distribution around the Island of Helgoland. Monitoring of growth, health, survival, reproduction and recruitment is ongoing. Field experiments with juvenile oysters show excellent growth and condition (Pogoda, 2019; Merk et al., 2019). Furthermore, adequate restoration sites have been identified and will be established in the Marine Protected Area and Natura 2000 site Borkum Riffgrund in 2019. Associated benthic diversity and trophic interactions will also be assessed. Sufficient supply of healthy and certified seed oysters was defined as a critical limiting factor for long-term restoration. The project PROCEED addresses biological and technological research questions to establish a healthy broodstock and a sufficient seed oyster production for native oyster restoration. Furthermore, it focuses on knowledge transfer and it will raise and improve a general awareness for this former native species and the importance of its restoration. The native oyster is characterized as an ecological key-player and oyster reefs are used as an example to explain biodiversity as a stabilizing factor for the wider ecosystem and to underline the general significance of ecosystem services.

thumbnail Fig. 1

Map of the North Sea and adjacent European seas (GCS_WGS_1984). It shows European countries contributing to the Native Oyster Restoration Alliance and currently planning or implementing restoration pilot projects or nature conservation measures with Ostrea edulis.

4 Outlook

The Native Oyster Restoration Alliance (NORA) is timely, and with its commitment and agreed “Berlin Oyster Recommendation” it is positioned to provide a solid basis for supporting European countries to implement commitments under the Habitats Directive, the Marine Strategy Framework Directive and OSPAR recommendations. NORA was initiated and supported by BfN and AWI who have now established an online presence at noraeurope.eu. Maintaining this communication, triggering relevant meetings and helping to advance the topics critical to developing oyster habitat restoration in European Seas will be essential activities of NORA. Similarly, maintaining communication with other shellfish restoration networks worldwide where valuable lessons can be learnt.

One important task of NORA is to implement the recommendations in coordination with the alliance members as a significant undertaking involving administrative, political and conservation or commercial aspects in the context of the various national jurisdictions. NORA subgroups will address issues such as site selection, monitoring and disease management. Their essential work will be instrumental for generating best practice at national levels in marine conservation and for ensuring that progress and developments are supported. NORA will facilitate marine habitat restoration and help to expand understanding and awareness of the ecological importance of oyster habitats.

Acknowledgements

We thank the funding institutions, ARK Natuurontwikkeling, Blue Marine Foundation, European Maritime Fund, German Federal Program for Biological Diversity, FEAMP Aquaculture Innovation, Marine Conservation Society, Marine Directorate of the German Federal Agency for Nature Conservation and Natural Resources Wales, for the substantial support of oyster restoration projects. We also acknowledge our industry project partners Cochet-Environnement, CRC Bretagne, ESITC-Caen, Glenmorangie, MDL Marinas, WindMW. Furthermore, we would like to thank the members of the Native Oyster Restoration Alliance (NORA) for their valuable contributions to the Berlin Oyster Recommendation and for sharing their knowledge and thoughts. Two anonymous reviewers helped to improve the manuscript; we thank them for their constructive criticism and helpful comments.

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Cite this article as: Pogoda B, Brown J, Hancock B, Preston J, Pouvreau S, Kamermans P, Sanderson W, Nordheim Hv. 2019. The Native Oyster Restoration Alliance (NORA) and the Berlin Oyster Recommendation: bringing back a key ecosystem engineer by developing and supporting best practice in Europe. Aquat. Living Resour. 32: 13

All Tables

Table 1

Recommendations as listed in the Berlin Oyster Recommendation on the Future of Native Oyster Restoration in Europe. These are based on agreements of participants of the first meeting of the Native Oyster Restoration Alliance (NORA) in Berlin 2017, NORA members and on a literature review focusing on restoration of Ostrea edulis.

All Figures

thumbnail Fig. 1

Map of the North Sea and adjacent European seas (GCS_WGS_1984). It shows European countries contributing to the Native Oyster Restoration Alliance and currently planning or implementing restoration pilot projects or nature conservation measures with Ostrea edulis.

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