Summary status of the OSPAR Network of Marine Protected Areas (2016)
Since the 2010 Quality Status Report, OSPAR countries have nominated a further 289 marine protected areas to the Network, now comprising 448 protected areas, representing 5.9% of the OSPAR Maritime Area. Considerable progress has been made towards an ecologically coherent and well-managed network, particularly within the Greater North Sea and Celtic Seas. Nevertheless, further work is required.
In 2003, OSPAR set the goal to establish a network of marine protected areas (MPAs) across the North-East Atlantic and to ensure that it is ecologically coherent and well-managed. It is intended that the MPA network makes a significant contribution to the sustainable use, protection and conservation of marine biodiversity across the North-East Atlantic, including in Areas Beyond National Jurisdiction (ABNJ).
The assessment of ecological coherence was based on OSPAR’s principles for an ecologically coherent network of MPAs. The following criteria were used:
- The geographic distribution of MPAs across the OSPAR Maritime Area to assess connectivity;
- The proportion of biogeographic provinces within MPAs to assess representativity; and
- The extent to which OSPAR listed habitat and species are protected within MPAs, to assess sufficiency of protecting features and their resilience.
The following questions were used to explore how well-managed the OSPAR MPA network is. These are based on the key stages in the implementation cycle of an MPA:
- Is MPA management documented?
- Are measures implemented?
- Is monitoring in place?
- Movement towards or achievement of conservation objectives?
With a better understanding of ecological coherence and management within the MPA network, OSPAR will be better able to identify gaps in the network and whether management measures need adjustment. Further details of both assessments are provided in the 2016 Status Report of the OSPAR MPA Network.
Ecological coherence is a term summarising the ultimate goal in the design, establishment and assessment of MPA networks. It is an overarching concept, encompassing a number of different principles and associated criteria. OSPAR’s aim of achieving an ecologically coherent network seeks to ensure that the MPAs interact with, and support, the wider marine environment as well as other MPAs.
MPAs are considered to be well-managed when appropriate management measures have been put in place that demonstrate a clear benefit to the conservation status of the protected features on an MPA.
The reference to the 10% target refers to Aichi Target 11 of the Convention on Biological Diversity (CBD) for at least 10% coverage of coastal and marine regions within MPAs as well as other effective area-based measures and reiterated in the North-East Atlantic Environment Strategy 2020.
See 2016 Status Report of the OSPAR MPA Network for further information.
Overall Status of the OSPAR MPA Network
On 1 October 2016, the OSPAR Network comprised 448 MPAs (Figure 1), including seven MPAs situated in ABNJ. The OSPAR MPA network covers 5.9% of the OSPAR Maritime Area and there is good coverage of coastal waters (16.7%). In the Exclusive Economic Zones (EEZs) of OSPAR countries, 2.3% of waters are covered and 8.9% are covered in areas beyond national EEZs.
The coverage of MPAs in the OSPAR Regions is shown in Table 1. In the Greater North Sea, the Convention on Biological Diversity target of 10% coverage by area-based measures has been exceeded.
|OSPAR Region||Total Area (km²)||MPAs|
|Arctic Waters||5529 716||107 109||1.9|
|Greater North Sea||766 624||112 968||14.7|
|Celtic Seas||366 459||27 795||7.6|
|Bay of Biscay and Iberian Coast||539 153||32 076||5.9|
|Wider Atlantic||6346 159||526 525||8.3|
|OSPAR Maritime Area||13 548 111||806 472||5.9|
Ecological Coherence of the OSPAR MPA Network
Despite good progress since 2010, the OSPAR MPA network cannot yet be considered ecologically coherent. Although the OSPAR MPA network is well distributed in the Greater North Sea and Celtic Seas, substantial gaps remain in Arctic Waters and the Wider Atlantic.
Nineteen of the 54 OSPAR listed features (i.e. species or habitats) are protected by more than one MPA in those parts of the North-East Atlantic where they are considered to be at risk. This includes all five listed invertebrates, three of the seven bird species, one of the two reptile species, one of the three marine mammal species, five of the 22 fish species and four of the 15 types of habitat.
Management of the OSPAR MPA Network
MPA management information is publicly documented for 61% of OSPAR MPAs, with a further 16% partially documented (Figure 2). The latter is largely due to Contracting Parties updating conservation objectives or because work to identify potential management actions is ongoing.
Management measures have been implemented for 12% of OSPAR MPAs, with partial action for a further 54% (Figure 2). The situation is similar for site condition monitoring, where data have not yet been collected for all MPAs. As a result, only 11% of OSPAR MPAs are known to be moving towards or have achieved their conservation objectives.
Countries have started to implement management actions for OSPAR MPAs in ABNJ. Successful management, however, requires cooperation with international organisations with competence for the management of human activities, such as fishing, shipping and deep sea mining. A mechanism to help cooperation and communication between such organisations has been initiated in the North East Atlantic, referred to as ‘the collective arrangement’.
Figure a shows the biogeographic areas and MPAs located within the OSPAR Maritime Area. Three biogeographic areas have more than 10% of their surface area within MPAs, while four biogeographic areas have no MPA coverage. Figure b summarises the proportion of biogeographic areas across the North-East Atlantic that occur within MPAs.
Figure b summarises the proportion of biogeographic areas across the North-East Atlantic that occur within MPAs.
Considerable progress has been made towards an ecologically-coherent and well-managed MPA network within the OSPAR Maritime Area, particularly within the Greater North Sea and Celtic Seas.
In the context of ecological coherence, efforts are needed to fill the perceived gaps in the MPA network. The Arctic Waters, Bay of Biscay and Iberian Coast and the Wider Atlantic could benefit from further MPA nominations. Further work is also required to ensure that habitats and species considered by OSPAR to be at risk, are adequately protected by MPAs where appropriate.
In the context of MPA management, additional efforts to implement management measures necessary to achieve the conservation objectives of the protected features of OSPAR MPAs should be considered. In parallel, long-term monitoring programmes could be broadened to evaluate with greater confidence whether the conservation objectives of OSPAR MPAs are being achieved.
For OSPAR MPAs in ABNJ, cooperation through dialogue and information sharing with relevant competent international organisations should be continued, in order to help the implementation of effective management measures for these MPAs.
The assessment methodologies for establishing ecological coherence and management effectiveness within Marine Protected Areas require development before the next OSPAR assessment, to ensure the results are robust.
To further develop these assessments the following information is required:
- Data and information to help support evaluation of the OSPAR conservation objectives, distribution, protection, and status of OSPAR listed features and habitats;
- Knowledge of critical areas for wide-ranging species; and
- Improved information on the management status of all OSPAR MPAs.
OSPAR (2017) 2016 Status Report on the OSPAR Network of Marine Protected Areas. Biodiversity Series [Publication number 693/2017].
Biological Diversity and Ecosystems - Marine protected areas (MPAs)
• OSPAR Decision 2010/1 on the establishment of the Milne Seamount Complex Marine Protected Area;
• OSPAR Recommendation 2003-03 as amended by 2010-02 on a network of marine protected areas;
• OSPAR agreement 2003 – 17 Guidelines for the Identification and Selection of Marine Protected Areas in the OSPAR Maritime Area as amended by BDC 2007 (BDC 2007 Summary Record (BDC 07/12/1) § 3.43b), and BDC 2016 (BDC 16/9/1, §5,27 and Annex 13)
• OSPAR Publication 2007-320 Background document to support the assessment of whether the OSPAR Network of Marine Protected Areas is ecologically coherent
|Context (3)||D1 - Biological Diversity, D6 - Seafloor Integrity, D4 – Marine Food Webs|
|Context (4)||D1.1 - Species Distribution, D1.2 - Population Size, D1.6 - Habitat Condition, D6.2 - Condition of benthic community , D4.1 - Productivity (production per unit biomass) of key species or trophic groups, D6.1 - Physical damage, having regard to substrate characteristics, D1.4 - Habitat distribution, D4.3 - Abundance/distribution of key trophic groups/species, D4.2 - Proportion of selected species at the top of food webs, D1.7 - Ecosystem Structure, D1.3 - Population condition, D1.5 - Habitat extent, D1.2 - Population Condition|
|Point of contact|
Summary status of the OSPAR Network of Marine Protected Areas (2016)
Coverage and extent of the OSPAR network of marine protected areas (MPAs) and assessments of its ecological coherence and management, based on data submitted by Contracting Parties up to and including 2016.
|Indirect spatial reference|
BE,DE, DK, ES, FR, IS, IE, NL, NO, PT, SE, UK
|Conditions applying to access and use|