Banc d'Arguin National Park

Country
Mauritania
Inscribed in
1989
Criteria
(ix)
(x)
The conservation outlook for this site has been assessed as "significant concern" in the latest assessment cycle. Explore the Conservation Outlook Assessment for the site below. You have the option to access the summary, or the detailed assessment.
Fringing the Atlantic coast, the park comprises sand-dunes, coastal swamps, small islands and shallow coastal waters. The contrast between the harsh desert environment and the biodiversity of the marine zone has resulted in a land- and seascape of outstanding natural significance. A wide variety of migrating birds spend the winter there. Several species of sea turtle and dolphin, used by the fishermen to attract shoals of fish, can also be found. © UNESCO
© IUCN/Wendy Strahm

Summary

2025 Conservation Outlook

Finalised on
11 Oct 2025
Significant concern
The values of PNBA have attracted major efforts by the Government of Mauritania and international partners for the protection and sustainable management of the site. These efforts have created a legal, institutional and financial basis for the management of the park, which should be used to its full potential in order to avert emerging pressures and threats from unsustainable fishing, climate change, oil exploration and the degradation of terrestrial ecosystems. While the overall marine and avian values remain largely intact and the protection and management framework for the Banc D’Arguin National Park is strong, its conservation outlook is of significant concern due in large part to emerging challenges originating within and outside its boundaries, principally from unsustainable fisheries, climate change and increasing industrial activities. Unsustainable fishing within and outside the PNBA, plastic waste accumulation and climate change are the main current pressures. Increasing effects of climate change can already be observed, especially on intertidal ecosystems, and need to be monitored to anticipate their influence on the values of the PNBA.

Current state and trend of VALUES

High Concern
The values of PNBA were nearly undisturbed until the late 20th century, but are increasingly under pressure and some values have begun to deteriorate. While there is a good follow up of fish landing in the park, fish stocks are not evaluated and the importance of the park as a nursery zone is not well documented. Knowledge on this subject requires updating with new surveys, at least in regard to species of commercial value, and assessments of the effective contribution of the PNBA nursery to adult stock. The status of terrestrial ecosystems and their fauna remains of low concern but signs of degradation appear despite management efforts. The property continues to host significant numbers of migratory and breeding shorebirds and although overall the population seems to be decreasing, some species populations have stabilised. Increasing effects of climate change are observed, especially on intertidal ecosystems, and need to be monitored to anticipate their influence on the values of the PNBA. Regular monitoring effort conducted by the PNBA will allow to better assess trends in the future.

Overall THREATS

High Threat
Unsustainable fishing (including fishing for sharks and rays) within and outside PNBA and climate change are the main current pressure. Fishing effort and captures inside the park have steeply increased and the increasing commercialization of artisanal fishing is a real concern. Climate change and especially the related sea level rise already has already modified the coastline and led to flooding of new areas. With increasing air and water temperature, the occurrence of extreme weather events and ocean currents, climate change will have significant consequences on marine and terrestrial ecosystems of the PNBA. Increasing accumulation of solid waste is also observed in the PNBA, especially in the coastal area. Accidental oil spills from oil platforms or tankers near PNBA are an increasing potential threat. Mining activities are likely to expand in the near future and may cause negative impacts on freshwater resources. Pressures on terrestrial ecosystems may increase in the short term due to new urban developments under construction outside of the park’s eastern boundary in Chami and in Mamghar, inside of the park. All of these developments will require a thorough assessment of their impacts on the park, including their cumulative impacts.

Overall PROTECTION and MANAGEMENT

Some Concern
The legislative, institutional and financial framework for the protection and management of PNBA is strong, but the wider protection of the surrounding seas needs to be developed further in order to meet emerging challenges to the site, principally from unsustainable fisheries and exploration and increasing shipping of hydrocarbons. The management effectiveness and capacity of the Park to raise sustainable funding are also in need of further improvement. The PNBA also needs to address the issue of increasing solid waste accumulation in the site. The banning of shark and ray fishing in 2020 continues to constitute an important issue to manage with regards to the relationships with local people. The relocation of the PNBA headquarters to Chami should develop these relationships and provide additional support to local communities and field work activities. Unfortunately, many staff still spend more time in Nouakchott than in Chami, and the refurbished field stations within the property tend to be empty apart from on special occasions.

Full assessment

Click the + and - signs to expand or collapse full accounts of information under each topic. You can also view the entire list of information by clicking Expand all on the top left.

Description of values

Intertidal ecosystems

Criterion
(ix)
Banc d'Arguin National Park is an ecosystem rich in biodiversity of nutrients and organic matter due to the vast expanse of marshes covered with seagrass beds, and an important windblown sediment addition from the continent and the result of the permanent upwelling of the Cap Blanc. The sites hosts extensive seagrass beds of Zostera noltei (35,500 ha; Pottier et al. 2021), salt marshes, 3,100 ha of mangrove swamps, 63,000 ha of mudflats, channels and creeks. This supports extensive fish nursery areas, occurrence of marine mammals (e.g. Humpback Dolphin) and large aggregations of migratory waterbirds (World Heritage Committee, 2010; UNEP-WCMC, 2012; Ramsar, 2023).

Subtidal ecosystems

Criterion
(ix)
There are 630,000 ha marine areas within PNBA including a submarine bank/shelf extending up to 80 km from coast, with some extensive seagrass beds of Cymodocea nodosa with Halodule wrightii. This is an exceptionally productive marine ecosystem due to coastal upwelling, containing rich invertebrate communities (UNEP-WCMC, 2012). The area belongs to a WWF 200 priority marine ecoregion (WWF, 2013).

Terrestrial ecosystems

Criterion
(ix)
570,000 ha of terrestrial lands within PNBA. Landscapes consist of dunes, sand hills, sandstone cliffs, islands with their typical ecosystems and Saharan vegetation with some Mediterranean and tropical influences (Diagana, 2005). The area testifies to ongoing ecological processes, primarily desert ecosystem succession (World Heritage Committee, 2010; UNEP-WCMC, 2012).

Migratory and breeding shorebirds

Criterion
(x)
More than 2 million shorebirds (30% of those using the eastern Atlantic Flyway) winter at PNBA – one of the world’s largest concentrations of wintering waterbirds. PNBA is the most important breeding area on the Atlantic seaboard, with 15 breeding species of fish-eating birds. Several species of global conservation concern and endemic subspecies make this an outstanding Important Bird Area (World Heritage Committee, 2010; BirdLife International, 2019).

Fish fauna

Criterion
(x)
Banc d’Arguin provides the biggest fish feeding, nursery and spawning area in West Africa. Three distinct fish communities with high abundance and species richness. Important spawning and nursery area for sharks and rays (World Heritage Committee, 2010; UNEP-WCMC, 2012).

Marine mammals and turtles

Criterion
(x)
Marine mammals regularly recorded include killer whale, Atlantic Humpbacked Dolphin, Common Dolphin, Rough-toothed Dolphin, Bottlenose Dolphin and Risso's Dolphin. Fin Whale (or Common Rorqual) and Common Porpoise have also been sighted. A small population of about 150 Monk Seal is found north of Nouadhibou. Four species of turtles frequent the area: Green, Loggerhead, Hawksbill and Leatherback. The shallow tidal flats act as important breeding and nursery areas. The site is an important feeding area for adult and immature Green Turtle due to the pristine and extensive seagrass beds (World Heritage Committee, 2010; UNEP-WCMC, 2012; Catry et al., 2023).

Terrestrial mammals

Criterion
(x)
Among terrestrial mammals, there are still some remnant populations of Dorcas gazelle (Gazella dorcas) (World Heritage Committee, 2010).
Imraguen cultural heritage
The local people, the Imraguen (Amrig), relate many of their customs to the natural environment: their name means 'the ones who gather life'. Until the 1990's these tribesmen still maintained age-old life styles, based almost exclusively on harvesting the migratory fish populations using traditional sailing boats (lanches) and techniques, such as a collaboration with wild dolphins in catching schools of mullet (UNEP-WCMC, 2012).

Assessment information

High Threat
Unsustainable fishing (including fishing for sharks and rays) inside and outside PNBA, both large scale commercial and artisanal, is the main current pressure. Fishing inside the park requires improved control and the rules agreed with the fishermen implemented, which is not presently the case. A number of other threats remain of high concern, including the increasing impacts of climate change especially on coastal ecosystems and bird populations, the noticeable accumulation of solid waste from micro to macroscale and the spreading of some aquatic invasive species.
Fishing, Harvesting & Controlling Aquatic Species
(Fishing inside and outside the site)
Other targeted species names
Chelonia mydas (Green Turtle); Monachus monachus (Mediterranean Monk Seal); Sphyrna lewini (Scalloped Hammerhead); Rhinobatos cemiculus (Blackchin Guitarfish); Pteromylaeus bovinus (Bull Ray); Rhinoptera marginata (Lusitanian Cownose Ray)
High Threat
Inside site
, Widespread(15-50%)
Outside site
Reduction in catch following overfishing by external poachers made local fishermen use unsustainable fishing methods (UNEP-WCMC, 2012). Illegal fishing within PNBA strongly reduced by 2009, owing to agreements with local Imraguen fishermen, improved patrolling capacity and an effective surveillance scheme. However, the results of maritime surveillance show that trawler pressure remains strong in the northern and southern parts of the PNBA and, on the other hand, that sail-lines represent an increasing internal pressure in 2022 and 2023 on fishery resources, particularly through the use of monofilament nets, prohibited by law (State Party of Mauritania, 2024). Artisanal fishing is becoming increasingly commercial, and the increasing number of non-Imraguen fishermen in the park, as well as the increasing targeted fishing of sharks and rays, which reaches up to an estimated 1,000 tonnes per year since 2014, are a significant concern (State Party of Mauritania, 2019, 2022, 2024). Catches of elasmobranchs outside the property, while showing a significant decrease, still remain high (from 13,000 tonnes in 2019 to less than 2,000 tonnes in 2023) (State Party of Mauritania, 2024). Fisheries also affect the Mediterranean Monk Seal (outside the site), reduce habitat, and abandoned nets cause seal and turtle mortality (IUCN, 2008; Hama et al., 2019). Increasing fishing practices and the still important catches of sharks and rays remain a real concern (UNESCO / IUCN Mission Report, 2014; Trégarot et al., 2018; Dia et al. 2023). The overexploitation of top predators can have serious impact on the trophic web, including on birds (Trégarot et al., 2018).

Fishing outside the PNBA further increases pressure on the marine resources around and inside the site. There are strong pressures from international (including European) fleets – in 2012, 334 foreign trawlers were licensed to fish in waters surrounding PNBA (UNEP-WCMC, 2012) and have continuously increased since then (Global Fishing Watch, 2020). Artisanal fishing catch in the immediate vicinity of the property has also increased by more than a factor of ten between 1994 and 2010. In addition the development of commercial fishing ports at Nouadhibou and Tanit (respectively 20 km NW and 50 km south of the PNBA), further accentuates pressure on the marine resources around and inside the site. The pollution of water by boats and the fishing gear wastes impact negatively the PNBA, leading for instance to sea turtles stranding events in the PNBA (Hama et al., 2019).

The external fishing effects on PNBA's food webs and ecosystems remain unclear as the importance of areas outside park for lifecycle stages of most fish is not known, however, significant impacts on the OUV of the property are likely according to the strong dependence of fisheries to the PNBA (UNESCO/IUCN, 2010; Meissa et al. 2018).
Water-borne & other effluent Pollution, Garbage & Solid Waste
(Plastic and cadmium pollution)
High Threat
Inside site
, Scattered(5-15%)
Outside site
Agricultural runoff from the Senegal River only slightly affects the property given the distance and currents (UNESCO, 2008). The Taziast gold mine located 60 km from the site uses water from important underground watersheds connected to the park. Although water pollution may be limited as the mine is reported to use a closed water loop (State Party of Mauritania, 2019), there are concerns over the transport of mercury by wind (IUCN Consultation, 2025). Significant water pollution with high concentrations of cadmium as well as an unacceptable amount of plastic and other waste have been confirmed (UNESCO & IUCN, 2014; Salim & Abdulhalim, 2016; Trégarot et al., 2018). Plastic waste has increased due to the development of Chami, as well as coming from Mamghar and Nouadhibou. However, the most significant source of plastic pollution comes from the sea due to discarded fishing gear, bottles and buoys (IUCN Consultation, 2025). The disintegration into microplastics, when ingested by marine organisms, cause chemical and physical damage to a wide range of marine organisms representing different trophic levels (Hollman et al., 2013; Setälä et al., 2016). Between the villages of Teichott and R'Gueiba there is an enormous amount of plastic waste, coming from land sources as well as brought in directly from the ocean, which extends over several kilometres (Serrao, 2018; IUCN Consultation, 2025).
Recreational Activities
(Unsustainable tourism)
Low Threat
Inside site
, Scattered(5-15%)
The 2014 UNESCO / IUCN mission encountered two rallies during its 7-day visit to the park, noting that the property is riddled with off-road tracks with no signage informing drivers that they are in a National Park. Tourism-related trash was also observed, and concern for increased beach tourism demand as the new city of Chami developed was also a concern (UNESCO & IUCN, 2014). The 2016 technical mission to PNBA provided updated information on ecotourism in the Park, and developed a set of recommendations to support local livelihoods through encouraging local infrastructure and training of women in the field of ecotourism (Salim and Abdulhalim, 2016). Between 2017 and 2018, the CSBA examined two requests for the installation of tourist infrastructure inside the PNBA: one concerning the construction of an airfield and the other the construction of a beach (Chami Beach). The CSBA issued an unfavorable opinion each time. This means that the PNBA is under strong pressure from tourism operators. Since tourism is still poorly developed in the PNBA, its impact on the local environment is therefore limited (Boide et al., 2018). However, over-frequentation during week-ends; additional pressure on fish populations by amateur fishing; degradation of coastal dunes due to non-organized 4x4 traffic and noise pollution affecting the avifauna; degradation of coastal vegetation; over-consumption of freshwater and the management of tourism waste (inexistant in the PNBA) are all additional pressures on the site that need to be controlled.
Invasive Non-Native/ Alien Species
(Invasive species in marine ecosystems)
Other invasive species names
Caulerpa taxifolia; Botrylloides diegensis
High Threat
Inside site
, Localised(<5%)
Outside site
Three marine alien species were identified during a scientific survey around Ejewir (Serrao, 2018). The green alga Caulerpa taxifolia, a highly invasive species that could compete with local seagrass, was collected and fishermen reported finding it in their fishing nets, together with an invasive ascidian tunicate (Botrylloides diegensis). An unidentified red alga were also observed.
Changes in Physical & Chemical Regimes, Changes in Temperature Regimes, Changes in Precipitation & Hydrological Regime
(Climate change and extreme weather events (flooding, storms, erosion, etc.))
High Threat
Inside site
, Throughout(>50%)
Outside site
Ongoing climate change already impacts the PNBA (CSE, 2024). Landscape changes triggered by climate change may affect food webs and ecosystem functioning (IPCC, 2019). Sea level rise and erosion are modifying the flat and sandy coastlines and impact marine and terrestrial ecosystems (e.g. El-Hacen et al., 2018). Up to 70m of recent coastal retreat has been observed near Iwik (Trégarot et al., 2018). Areas rarely flooded before are at present flooded, frequently destroying breeding colonies of seabirds. A number of bird species, certain herbaceous species such as Stipagrostis and Heliothropium, as well as reptiles are highly sensitive to climatic hazards (CSE, 2024). For the local subspecies of Eurasian spoonbill, the threat is very high and park management has artificially raised their nesting sites on the island of Nair to provide refuge. Some areas, for example Neroumi island, have been flooded almost permanently. Submersion of islands and islets leads to the loss of suitable habitat areas for some species (IUCN Consultation, 2025). A decline in the reproductive success of the Eurasian spoonbill has been recorded in the past, which may be related to a rising sea level (UNESCO & IUCN, 2014), although in recent years a stabilisation has been observed (State Party of Mauritania, 2024). Climate change also impacts staging sites of migratory birds outside the PNBA (in the Arctic for instance), modifying their displacements and thus their presence in the PNBA (Rakhimberdiev et al., 2018). Worryingly and partially due to climate change, the total number of birds within the PNBA decreased from 2.3 to 2 million since 1980 (PNBA, 2018; Oudman et al. 2020). PNBA marine ecosystems crucially depend on climate-sensitive East Atlantic upwelling, wind and marine currents and water temperature, but the exact response of these parameters to future climate change is unknown. Coastal ecosystems play an important role of protection from marine storms and cyclones that could be limited in the future (Trégarot et al., 2018, Vousdoukas et al., 2020). In contrast, sea level rise creates new intertidal ecosystems on low-lying lands, that could be future hotspots of biodiversity (Trégarot et al., 2018). A breach made by the ocean in the dune cord has been observed at Bellaât (Cap Sainte-Anne) since 2013. This breach has created an important permanent lagoon which hosts a great biodiversity (reports by the Scientific Council of Banc d 'Arguin in State Party of Mauritania, 2019).
High Threat
Intensifying climate change will very likely have major and unprecedented - at least considering modern times - consequences on PNBA ecosystems. Whereas their magnitudes will depend on greenhouse gas emissions over the 21st century; sea level rise, ocean and air temperature increase will be in any case noticeable in future, affecting marine and terrestrial ecosystems. Among other processes, climate change could also modify the ocean currents, the marine biomass or the occurrence of extreme weather events. Accidental oil spills from oil platforms or tankers near PNBA are an increasing potential threat. The same is true for planned extensions of mining/quarrying operations and exploration. Ongoing and planned development projects which are contributing to the site becoming less isolated and more easily accessible, are likely to increase human pressures on the site, and the coming years will be decisive to ensure that its OUV will not be compromised.
Oil & Gas exploration/development
(Pollution from oil exploration/exploitation and shipping)
Very High Threat
Inside site
, Throughout(>50%)
Outside site
Although oil exploration is banned within PNBA and no oil exploration concessions overlap with the property and there is a buffer zone of 5 km around it; a number of exploration areas are located in its surroundings (State Party of Mauritania, 2019). Oil/gas exploration and exploitation to the west and south-west of PNBA is ongoing, without appropriate safeguards in place. Increased tanker traffic is an additional threat. Insufficient oil spill risk management capacity in place (UNESCO, 2009, 2013). Explorations were carried out in 2017 and 2019 in area important for biodiversity (breeding zones, cold-water corals, etc.) with potential impacts on marine mammals, due to noise pollution (Williams et al., 2015). Increasing offshore oil exploration and exploitation increases the risks of an oil spill which would have catastrophic impacts on the property and on the fisheries in the region (UNESCO & IUCN, 2014). While two exploration activities for off-shore oil (Block C-19 and c-7) have been suspended (State Party of Mauritania, 2022, 2024), an offshore liquified natural gas project (Greater Tortue Ahmeyim – GTA) has been developed on the Senegal-Mauritania border by bp and its partners Kosmos Energy, Société Mauritanienne des Hydrocarbures (SMH) and Société des Pétroles du Sénégal (PETROSEN). Exploitation of the gas reserves of the GTA project is scheduled to begin in early 2025 (State Party of Mauritania, 2024). Potential impacts of this project on the property remain unknown and might require an EIA.
Mining & Quarrying
(Mining)
High Threat
Inside site
, Extent of threat not known
Outside site
The expansion of industrial mining and artisanal small-scale gold mining (ASGM) in the Tasiast and Chami regions poses increasing risks of pollution, primarily through the use of mercury and cyanide. These contaminants can disperse via oued water flows, soil, and dust carried by the harmattan winds, threatening the fragile ecosystems of the PNBA.
Although current monitoring (ONISPA, 2024) indicates that mercury levels in fish products and sediments remain below health and safety limits, continued surveillance—especially near Chami—is essential. The study by Maha et al. (2024) found elevated mercury concentrations in soils within ASGM hotspots and identified favorable conditions for mercury methylation, increasing potential risks to health and biodiversity. Mercury infiltration into groundwater appears limited for now, but soil contamination remains significant. Contaminated waste from ASGM sites is also transported to other areas, compounding the pollution spread (Maha et al., 2024).
The 2023 expansion of the Tasiast mine by Tasiast Mauritanie Limited S.A. (a Kinross Gold subsidiary) increased production capacity by 50% (Ecofin Agency, 2024). Although mining is reportedly regulated (State Party of Mauritania, 2023), concerns remain over the use of seawater treated with biocides, which could harm marine ecosystems in the Baie du Lévrier (UNESCO/IUCN, 2014), and indirectly affect the PNBA’s hydrological balance.
In 2023, a scientific research workshop on the Risks of Pollution to the Ecosystems of the Banc d’Arguin from Human Activities was held from June 20 to 22 in Iwik. The objective of the workshop was to formulate strong recommendations to national authorities, aimed at integrating the PNBA into national environmental policies, based on several presentations related to this issue. Recommendations include monitoring cyanide in water and soil near Chami, planting a vegetation corridor to limit contaminant spread, and using phytoremediation (PNBA, 2023) to detoxify soils. To monitor trace metal levels, particularly mercury, several actions have been undertaken (ONISPA, 2024). For example, the RESILAO Project, led by the PNBA in partnership with ISSM and ONISPA for the 2024–2025 period, aims to use phytoremediation to remove toxic pollutants and ensure detoxification.
Residential Areas
(Infrastructure development)
High Threat
Inside site
, Extent of threat not known
Outside site
There is an increasing number of development projects within the park and its wider area, all of which will have to be subject to Environmental Impact Assessment prior to their implementation, including an assessment of their cumulative impacts. The planned construction of a high-voltage electricity line along the Nouakchott-Nouadhibou road could have negative impacts on the park’s bird populations (resident and migratory) (UNESCO & IUCN, 2014). The recent development of Chami, and the extension of Mamghar put further pressure on the Park, with increased traffic and waste. An Urban Development Master Plan has been established to address these issues (State Party of Mauritania, 2022), however the rapidly growing town represents a serious potential threat (pers. comm.).
Marine & Freshwater Aquaculture
(Aquaculture development)
Data Deficient
Inside site
, Extent of threat not known
Aquaculture development was identified as a potential threat for Cap Blanc area and the Mediterranean Monk Seal in 2008 (UNESCO, 2008), but impact not assessed yet. No recent information is available as of 2025.
Water-borne & other effluent Pollution
(Gold panning )
High Threat
Outside site
The installation, since 2016, of a gold ore processing center in Chami constitutes a real threat to the PNBA coastline. This center treats the poriferous mineral with mercury. The treatment is done under the open sky. The treatment sludge is stored on site. After drying, they are transported by wind to the coast which is less than 75 km away. There is a real risk of contamination of the food chain of the PNBA reserve (Gagnol et al., 2020). Following requests from the World Heritage Committee (2021), the gold processing centre in Chami has been relocated 30 km to the east (State Party of Mauritania, 2022). However, analysis on the heavy metal contaminations in the property need to continue and the instalment of monitoring equipment is required in order to assess the management effectiveness of mining waste in Chami (World Heritage Committee, 2023).
Changes in Physical & Chemical Regimes, Changes in Temperature Regimes, Changes in Precipitation & Hydrological Regime
(Climate change)
High Threat
Inside site
, Throughout(>50%)
Outside site
Increasing effects of climate change are anticipated over the 21st century, as the submersion of at least 5% of the PNBA area and locally more than 100m of sandy coast retreat due to sea level rise (ClimateCentral, 2021; Vousdoukas et al., 2020), loss of seagrass beds and other vegetated habitats due to extreme climatic events, high seawater temperatures and stress of desiccation at low tide caused by strong evaporation during a drought (IPCC, 2019; CSE, 2024). Consequently, climate change could have a negative impact on the primary production, animal biomass, fisheries catch in marine ecosystems, and on the health and well-being of local communities (IPCC, 2019; CSE, 2024).
Pathogens
(Avian influenza)
Low Threat
Outside site
Outbreaks of avian influenza in the Diawling National Park (Mauritania) and the Djoudj National Bird Sanctuary (Senegal) occurred in 2021. Monitoring for avian influenza in the PNBA has been undertaken since 2021 to contain any outbreaks in the property, but has not been observed (State Party of Mauritania, 2022; 2024). However the risk of disease outbreaks in the PNBA exists.
Involvement of stakeholders and rightsholders, including indigenous peoples and local communities, in decision-making processes
Some Concern
Relations with Imraguen communities, which have exclusive fisheries access since 1976, were considered good in the past (UNESCO, 2008; Abulhawa et al., 2014). However, concerns have been raised by the communities over the lack of tangible benefits from the park reaching the local population (IUCN consultation, 2025). Annual consultation meetings are supposed to be held with communities to discuss management measures and conditions of access to resources, although no meetings took place in 2013 and strains between local people and park administration were noted (UNESCO & IUCN, 2014). Since then several stakeholder meetings were organised by the park managers (State Party of Mauritania, 2019), although the involvement of youth and women in the management system is recognised as needing improvement (State Party of Mauritania, 2021). An important issue remains the shark and ray catches by Imraguen. The State Party banned this activity as of 2020 which could lead to conflict with local people. Promises to improve health services to villages within the property have also not materialised (IUCN Consultation, 2025). A village relocation project has been abandoned, and instead a project to improve the resilience of ecosystems and local communities has been initiated (State Party of Mauritania, 2022; 2024).
Legal framework
Mostly Effective
Important progress has been made with the establishment of a legal framework for the site since its inscription. A special law on PNBA (2000) and two government decrees (2006) are very important for the sustainable development and conservation of the site (UNESCO & IUCN, 2014). Additional measures, including expansion of the National Committee, revision of the local management structure, expansion of the list of local stakeholders, and signing of two important agreements (AEWA and MoU with the Wadden Sea) were made to reinforce the legal framework (State Party of Mauritania, 2015).
Governance arrangements
Mostly Effective
The property falls under Nouadhibou and Inchiri provinces. It is administered by the Banc d'Arguin National Park Authority under the Office of the Prime Minister. In the past the property was managed in collaboration with the FIBA (Fondation internationale du Banc d'Arguin) which was merged with MAVA in 2014. Participatory governance is considered effective, and local communities are represented on the board of directors and in all decision-making bodies concerning the park, although issues with benefit sharing need to be resolved (see above).
Integration into local, regional and national planning systems (including sea/landscape connectivity)
Some Concern
PNBA is well supported by national legislation and reportedly also by national plans on artisanal fishing development. However, there is concern about the consideration of the parks interests in infrastructure and other development projects, including mining (UNESCO, 2013). A number of developments have been completed inside and in close vicinity of the site without having been subject to an EIA. The continued increasing development of gold and oil extraction in the region and the related building of infrastructures should be better planned and regulated, in order to limit the threats to the OUV. No progress has been achieved yet with the inscription of the site as a Particularly Sensitive Sea Area (World Heritage Committee, 2021, 2023).
Boundaries
Some Concern
Recent offshore oil exploration and deep water pumping respectively a few kilometres towards the west and east of the property raises concerns about potential impacts on its integrity (State Party of Mauritania, 2019; UNESCO, 2021, 2023). The proximity of fishing camps to the park's southern boundary requires, as a precaution, the establishment of a buffer zone (State Party of Mauritania, 2021)
Overlapping international designations
Mostly Effective
Banc d'Arguin National is also a Ramsar site. Communication between focal points is occasional (State Party of Mauritania, 2021). The Management plan (2020-2024) of the PNBA addresses the obligations to both designations (PNBA, 2020). For the management of selachians, a specific recommendation was made to carry out awareness-raising campaigns for the Imraguen people, noting that the PNBA is designated as both a Ramsar site and a UNESCO World Heritage site, thus with a moral and legal obligation to participate in its conservation and resources.
Implementation of World Heritage Committee decisions and recommendations
Mostly Effective
Most but not all recommendations were followed by the State Party in the past: request to adopt two decrees to implement Special Law for PNBA at 30.COM (2006) fulfilled by 31.COM (UNESCO, 2007); requests for provision of EIA reports and mitigation measures and precautions for road construction and oil exploration from 27.COM (2003) not followed by SP until 33.COM (UNESCO, 2009); PSSA status designation recommended since 28.COM (2004) not yet fulfilled, but preparations are underway (UNESCO & IUCN, 2014); request to apply Law 2000/25 at 29.COM not followed by 32.COM (UNESCO, 2008); invitation to establish Biosphere Reserve at 29.COM not followed until 37.COM. Request to implement MEC and MARPOL at 30.COM not implemented by 32.COM (UNESCO, 2008). Request to establish Oil Spill Emergency Response Plan at 31.COM apparently not followed until 2011 (Conf. pers. comm., 2011). Request to report on the monitoring of the state of values of PNBA at 31.COM not fully met by 34.COM (but see State Party of Mauritania, 2009). Recommendation to finalize PNBA zoning at 32.COM not implemented until 2011 (Conf. pers. comm., 2011). In the most recent State of Conservation reports, the State Party has addressed most of the requests expressed by the Committee at its 42nd, 44th and 45th Sessions (State Party of Mauritania, 2019, 2022, 2024). However, no progress has been achieved yet with the inscription of the site as a Particularly Sensitive Sea Area.
Climate action
Highly Effective
The PNBA has co-constructed with a Canadian partner ‘CEGEP de la Gaspegie et des îles’ a regional project entitled ‘Solutions Ecosystémiques de D'Adapation Durable - SEDAD’, financed by Canadian cooperation for the period August 2023 to December 2025 (State Party of Mauritania, 2024). The project is implemented in three sites in the sub-region, including the PNBA in Mauritania. One of the components of this project aims to ‘improve people's adaptation to climate change by implementing nature-based solutions under the leadership of women, young women and Indigenous people’. Within the project’s implementation an assessment of the vulnerability, risk analysis and capacity to adapt to climate change in the Banc d'Arguin National Park has been published by the Centre de Suivi Ecologique (Senegal) (CSE, 2024).
Additionally, the 3-year project ‘Strengthening accountability in Marine Protected Areas science and management through climate vulnerability assessment and adaptation measures in World Heritage sites’, developed by UNESCO's Marine Programme and the Intergovernmental Oceanographic Commission (IOC) and recently funded by the Velux Foundation (Denmark), started beginning of 2025 and will address the issue of the vulnerability of the ecosystems of the PNBA and the Wadden Sea to the effects of climate change and the adaptation measures approved (State Party of Mauritania, 2024)
Management plan and overall management system
Highly Effective
A management plan is drawn up every 5 years. The latest 2020-2024 development and management plan (PNBA, 2020) is currently under external evaluation to assess the extent to which its objectives and expected results have been achieved (State Party of Mauritania, 2024). The results of the external evaluation will guide the development of the 5th management plan for the period 2025-2029 .
Law enforcement
Mostly Effective
Management authorities and the GCM (Garde Côtes Mauritanienne) are in charge of the surveillance of the waters of the PNBA and the Cap Blanc Satellite Reserve, control and boarding of industrial, artisanal and coastal fishing vessels (pirogues and lanches) in breach of the PNBA, collection of prohibited fishing nets, and execution of missions. Annual reports on patrolling efforts record a high maritime surveillance and effective enforcement (2022: 491 patrols, leading to the boarding of 192 pirogues and the rerouting of 23 boats; 2023: 468 patrols resulting in the boarding of 214 pirogues, 15 of which were found fishing within the limits of the Cap Blanc-RSCB Satellite Reserve, and 36 lanches diverted; 2024 first semester: 257 patrols) (State Party of Mauritania, 2024). Limiting factors in the past years have been fuel shortages in the field and the poor technical condition of the PNBA's surveillance boats. However, new boats have been acquired and the patrolling system is expected to be reinforced starting from January or February 2025 (State Party of Mauritania, 2024).
Sustainable finance
Mostly Effective
The 2020-2024 management plan provided an overall budget estimate of MRU 760,300,000, equivalent to 19 million euros (PNBA, 2020). Funding predominantly comes from the state budget (mobilized through fishing agreements with the EU), the contribution of the Trust Fund "Banc d'Arguin Coastal and Marine Biodiversity" (BACoMaB) which covers project and running costs corresponding to 8% and 4% respectively (State Party of Mauritania, 2021), and conservation and development partners who have signed financing agreements (PNBA, 2020). The available budget was considered acceptable, but with room for improvement to fully meet the management needs (State Party of Mauritania, 2021). Financial support from the European Union, German and Canadian cooperation, and other donors are also mentioned (State Party of Mauritania, 2021, 2022, 2024).
Staff capacity, training and development
Some Concern
Human resources partly meet management needs. In particular, the areas of environmental sustainability, capacity development and education, interpretation and visitor management, and the availability of professionals were considered poor (State Party pof Mauritania, 2021). The site-based capacity building programme has not been implemented yet. Many training courses for PNBA staff have reportedly been conducted but an overall vision and strategy has been missing, and the proficiency of staff to perform their tasks has reportedly not risen in spite of training efforts.
Education and interpretation programmes
Some Concern
"Environmental education has not become a coherent program, with regular activities in schools and green class field trips", according to the results of the evaluation of the 2015-2019 management plan (PNBA, 2020). Education and awareness programs addressing youth and women have noted to be lacking (State Party of Mauritania, 2021). However, education goals with schools are outlined in the 2020-2024 Management Plan (PNBA, 2020), and a good PNBA interpretation centre in Chami exists.
Tourism and visitation management
Some Concern
Tourism camps built in 2008 to promote ecotourism are in disrepair due to a lack of maintenance (IUCN Consultation, 2025). Also due to perceived security issues in the region, the number of visitors remains very limited, even if ecotourism is considered as having a large potential to create alternative livelihoods for local people and to limit fisheries pressure (Trégarot et al., 2018, State Party of Mauritania, 2019). A report on ecotourism and its perspectives of development has been proposed in 2018 (State Party of Mauritania, 2019) and a strategy on ecotourism in PNBA has been developed (State Party of Mauritania, 2022). The Nouakchott-Nouadhibou road now facilitates access to the Park, even if access within the Park requires a 4x4 vehicle and a guide (IUCN Consultation, 2025).
Sustainable use
Serious Concern
The traditional use agreements with Imraguen fishers are an example of a generally successful reconciliation of traditional use interests inside the property and conservation objectives (UNEP-WCMC, 2012). However, it should be noted that the rules agreed concerning fishing inside the park are not adequately implemented. Artisanal fishing is becoming increasingly commercial, and many Imraguen employ non-Imraguen Mauritanians on their fishing vessels. The use of mono-filament fishing nets is also reported, and targeted fishing of sharks and rays is increasing (UNESCO & IUCN, 2014; Lemrabott et al. 2024). There are concerns about the sustainability of fisheries outside the property and of terrestrial resource use and a strategy to address these was under preparation in 2009 (UNESCO, 2009). Access to the resource has become increasingly commercial, attracting non-Imraguen mareyeurs (fish merchant or middle men). Added to this situation, unauthorized incursions into the park's enclosure are worrying, despite the surveillance system in place. There is a need to strengthen the implementation of the shark management plan by a strict application of the prohibition of gear targeting these species (Dia et al. 2023).
Monitoring
Mostly Effective
Fisheries monitoring methodology developed with the Mauritanian Institute of Oceanographic Research and Fisheries (IMROP) is effective and continues at the park since 1997, providing data on the resource and guiding the management system. The creation in 2016 and the first assessment in 2018 of a Dashboard on the effectiveness of the Management Plan recently improved the monitoring process in the PNBA (State Party of Mauritania, 2019). Although it still needs to be perfected, the system is functional and contributes to the monitoring of the indicators. An increase in human and financial resources is recommended to improve the monitoring of the various dashboard indicators, as well as providing ongoing training for monitoring staff (State Party of Mauritania, 2021).
Research
Mostly Effective
Contributing to research is one of the key missions outlined in the 2020-2024 management plan (PNBA, 2020). A scientific observatory was established at PNBA in 2007. Research on fish stocks and fisheries’ impact continues. The Scientific Council of the Banc d’Arguin has been created and meets once a year since 2014. This Scientific Council appears to be very active and independent. In addition to discussions during annual meetings and field missions, several scientific reports were produced recently and especially analysis of the EIA and the related documents produced on oil exploration and gold exploitation (State Party of Mauritania, 2019). In situ data on bird populations, fish stocks or climate change (etc.) has also been provided through the latest State of Conservation reports (State Party of Mauritania, 2022, 2024).
Effectiveness of management system and governance in addressing threats outside the site
Serious Concern
The development of fisheries, gold and groundwater exploitations, oil exploration and other infrastructure in the close vicinity of the site raise serious concerns about potential impacts on its integrity. Indeed, whereas the national park itself remains overall well protected and managed, it becomes an increasingly isolated natural area in a developing region. These recent socio-economic developments are partly uncontrolled and do not always take into consideration the World Heritage status of the site. In a changing climate, these developments need to be planned and carefully controlled at the regional scale. Apart from the Baie de l'Etoile, recently designated an MPA, and the Cap Blanc satellite reserve, which is part of the PNBA, no effective management measures have been implemented to limit the negative external influences on the park. In order to preserve the site’s values in the future, the management authority of the PNBA should be considered and consulted on these socio-economical developments.
Effectiveness of management system and governance in addressing threats inside the site
Mostly Effective
Management effectiveness has improved (UNESCO, 2008). A management effectiveness evaluation carried out with IUCN in 2013 rated management effectiveness between “good” and “medium”, depending on the management aspect evaluated, but that the management plan suffered from a low level of implementation (UNESCO & IUCN, 2014). Now that the management authority is located in Chami closer to the Park, management and especially the relation with all stakeholders should be improved (Salim and Abdulhalim, 2016; State Party of Mauritania, 2019). Since 2016, a Management Plan Dashboard has been created to assess its effectiveness (State Party of Mauritania, 2019). In 2018, 20 indicators on natural values, socio-economical dynamics and governance have been assessed for the first time, showing both improvement and worsening among these specific indicators. This dashboard still needs to be further developed, but it constitutes a relevant and useful tool to assess and improve the effectiveness of the management system. The management plan developed for the 2020-2024 is now under assessment. The results of the evaluation will form the base to the development of the updated 2025-2029 management plan.
The legislative, institutional and financial framework for the protection and management of PNBA is strong, but the wider protection of the surrounding seas needs to be developed further in order to meet emerging challenges to the site, principally from unsustainable fisheries and exploration and increasing shipping of hydrocarbons. The management effectiveness and capacity of the Park to raise sustainable funding are also in need of further improvement. The PNBA also needs to address the issue of increasing solid waste accumulation in the site. The banning of shark and ray fishing in 2020 continues to constitute an important issue to manage with regards to the relationships with local people. The relocation of the PNBA headquarters to Chami should develop these relationships and provide additional support to local communities and field work activities. Unfortunately, many staff still spend more time in Nouakchott than in Chami, and the refurbished field stations within the property tend to be empty apart from on special occasions.
Good practice examples
The PNBA Trust Fund (BACoMaB) is a useful example for sustainable financing of natural World Heritage Properties. The maritime surveillance scheme is the most effective in the region. The Scientific Council of the Banc d’Arguin has an increasing activity and provides useful inputs for the site management.

Intertidal ecosystems

Low Concern
Trend
Data Deficient
Intertidal ecosystems are threatened by potential accidental oil spills from hydrocarbon extraction/transport (State Party of Mauritania, 2009), illegal overfishing and the increasing presence of solid waste. Changes in the air and water temperatures or ocean currents could also strongly affect these ecosystems (IPCC, 2019). Sea level rise and erosion are modifying the flat and sandy coastlines and up to 70m of recent coastal retreat has been observed near Iwik (Trégarot et al., 2018, El-Hacen et al., 2018). Areas rarely flooded before are at present flooded frequently threatening breeding bird colonies. A general decline was especially observed in bird species that depend on the intertidal mudflats. However, sea level rise also creates new intertidal ecosystems on low-lying lands, that could be future hotspots of biodiversity (Trégarot et al., 2018). Since 2018, quarterly monitoring of the intertidal benthos has been carried out to follow the dynamic of benthos density, biomass, and composition, as benthos variations are closely linked with those of Palaearctic migratory birds, which use intertidal sites as a feeding area for a good part of the year. Monitoring of abundant mollusks such as Loripes lucinalis, Senilia senilis and Dosinia isocaria will be used as bioindicators to assess the productivity of the intertidal environment.(State Party of Mauritania, 2024).

Subtidal ecosystems

Good
Trend
Stable
Significant progress in estimating and mapping subtidal seagrass beds and habitats has been made by the project funded by Royal Dutch Shell (Shell), coordinated by The Biodiversity Consultancy Ltd (TBC) and carried out by the PNBA in collaboration with TCarta (El-Hacen, 2023). The mapping exercise of the subtidal habitats of Banc d'Arguin including seagrasses and macroalgae revealed that PNBA subtidal ecosystem contains in total 2379 km2 of seagrass and 708 km2 of algae. Taking into account the known cover of intertidal seagrass (~350-400 km2), the results demonstrate that the actual total cover of seagrass beds in Banc d’Arguin (> 2700 km2) is at least double the previous estimates (772 km2 by Pottier et al., 2021). Thus, the total area of the subtidal key foundation habitats (seagrass and algae) in PNBA is more than 3000 km2. Subtidal ecosystems were previously considered generally intact, but threatened by potential accidental oil spills (UNEP-WCMC, 2012), as well as overfishing and the increasing presence of solid waste. PNBA marine ecosystems crucially depend on climate sensitive East Atlantic upwelling, wind and marine currents and water temperature, but the exact response of these parameters to ongoing climate change is unknown. Increasing effects of climate change are expected to decrease primary production, animal biomass and fisheries' catch potential (IPCC, 2019).

Terrestrial ecosystems

High Concern
Trend
Deteriorating
The terrestrial area has suffered from degradation, reduced vegetation cover and falling wildlife populations, due in part to climatic conditions in the late twentieth century, decreasing rainfall, as well as due to poaching and wood gathering (UNESCO, 2009). The situation does not appear to be improving (IUCN Consultation, 2025). Solid waste continues to accumulate in terrestrial areas, particularly near villages, and a solution to trash disposal is urgently needed.

Migratory and breeding shorebirds

High Concern
Trend
Deteriorating
Bird populations have been generally decreasing since 1980, especially due to the effect of climate change and other pressures in the PNBA and along the East Atlantic Flyway (PNBA, 2018, Rakhimberdiev et al., 2018). The total number of birds within the PNBA decreased from 2.3 to 2 million since 1980 (PNBA, 2018). Abundance of some fish-eating bird species declined as a result of decline in fish stocks (BirdLife International, 2021). A recent analysis suggests a decline in species that depend on the intertidal ecosystems and an increase in species depending on fish and crustaceans in the subtidal ecosystems (Oudman et al., 2020). The local Spoonbill is vulnerable due to flooding of nest sites as a result of climate change, and is reported to have shown a decline in reproductive success (UNESCO & IUCN, 2014). Monthly monitoring carried by the PNBA in 2018 and 2019 showed an average of 400 breeding pairs of Spoonbill per year, whereas the average for the period 2020 to 2023 was 1000 breeding pairs per year (State Party of Mauritania, 2024). However, this positive trend recorded in terms of nesting sites could be explained by the extension of the coverage of the monitoring system to two new sites from 2020 (the islands of Toufatt and Cheddid) and a good regularity in the monitoring schedule. It seems, numbers have returned to their historical levels of 80 years ago.
In the case of of Mauritanian Grey Heron (Ardea cinerea monicae) colonies, the situation appears to be at least stable, if not increasing slightly, with very regular and comprehensive monitoring (400-500 breeding pairs per year in 2018-2019 [incomplete survey]; more than 800 breeding pairs per year between 2020-2023) (State Party of Mauritania, 2024). While these results are encouraging, the apparent positive trends might be explained with the increased monitoring effort.

Fish fauna

High Concern
Trend
Deteriorating
No monitoring data on trends in fish populations inside the property are available. Signs of overfishing outside the property along the Mauritanian coast (Gascuel et al., 2007) and probably also inside PNBA for some species. The fishing monitoring program set up by IMROP in 1997 shows that fishing effort within PNBA increased threefold in recent years. While selachian catches have not exceeded 1,000 t/year since 2014, fishing is intensifying in the property (State Party of Mauritania, 2022, 2024). The prohibition of selachian fishing, the control of boats and the limitation of transformation wells remain objectives. On the other hand, the description of a new genus and species of fish within the marine shallow waters of PNBA (Seret & Naylor, 2016) is considered to be a good indicator of the richness of the marine fauna diversity, with the possibility of discovering more species in the region.

Marine mammals and turtles

High Concern
Trend
Stable
The 2014 UNESCO & IUCN reactive monitoring mission to the property observed a large number of turtle shells on the beach, and there was no sign of any nesting activity. Almost 1000 cases of dead sea turtles strangled by solid waste were observed recently in the PNBA (Hama et al., 2019). Data collected by Catry et al. (2023) show, however, that Banc D’Arguin is still one of the main feeding sites for green turtles nesting in the Bijagós and probably a site of critical importance for immature and adult green turtles in a global context. The property remains an important sanctuary also for dolphins, thanks to the strict implementation of the ban on motorised boats within the property. The breeding colony of Monk Seals is now established in Guerguerat area, North of Nouadhibou, and outside the World Heritage Site at Cap Blanc. The Monk Seal is probably decreasing due to external factors outside the site, including habitat disturbance and food competition from shore-based fisheries (UNESCO, 2008). Recently, the population of the Monk Seal has been estimated at 330 individuals and was assessed to be in good condition (State Party of Mauritania, 2019).

Terrestrial mammals

Low Concern
Trend
Data Deficient
There is no information on the status of terrestrial mammals, but this is probably not deteriorating due to good rainy seasons in recent years which has resulted in a positive shifting in terrestrial habitats. Striped hyena may still be present, as are fennec fox and jackal, the latter of which has an increasing population (UNESCO & IUCN, 2014). The population of Dorcas Gazelle is now restricted to Tidra island as a combined result of hunting pressure and drought (UNESCO & IUCN, 2014). There is a concern that the population of the Dorcas Gazelle has suffered genetic impoverishment due to its geographic isolation and its reduction to about 80 individuals, although this figure has recently remained stable (IUCN Consultation, 2017). There continues to be extensive grazing of dromedaries and goats in the property (UNESCO & IUCN, 2014).
Assessment of the current state and trend of World Heritage values
Deteriorating
The values of PNBA were nearly undisturbed until the late 20th century, but are increasingly under pressure and some values have begun to deteriorate. While there is a good follow up of fish landing in the park, fish stocks are not evaluated and the importance of the park as a nursery zone is not well documented. Knowledge on this subject requires updating with new surveys, at least in regard to species of commercial value, and assessments of the effective contribution of the PNBA nursery to adult stock. The status of terrestrial ecosystems and their fauna remains of low concern but signs of degradation appear despite management efforts. The property continues to host significant numbers of migratory and breeding shorebirds and although overall the population seems to be decreasing, some species populations have stabilised. Increasing effects of climate change are observed, especially on intertidal ecosystems, and need to be monitored to anticipate their influence on the values of the PNBA. Regular monitoring effort conducted by the PNBA will allow to better assess trends in the future.
Assessment of the current state and trend of other important values
Low Concern
Deteriorating
Once restricted to the artisanal fishing of the Imraguen, the park is under pressure from a growing fleet and incursions from non-Imraguen fishermen, putting local artisanal fisheries at risk.

Additional information

Fishing areas and conservation of fish stocks,
Livestock grazing areas
PNBA protects not only local artisanal fisheries, but is also a key spawning and nursery area for a wide range of fish, which supplies recruitment to stocks in the wider upwelling area. These are a crucial global fisheries resource, including and particularly for EU countries. The PNBA contribution to fisheries has recently been evaluated as ~70 millions €/yr (Trégarot et al., 2018).
In addition to fishing, camel herding is widely practised within the Park's boundaries, taking advantage of grazing areas, notably in the Jeffiyat Chami region (Diagana, 2005; Correra, 2006).
Factors negatively affecting provision of this benefit
Overexploitation
Impact level - High
Trend - Increasing
Habitat change
Impact level - High
Trend - Increasing
Once dedicated to the artisanal fishing of the Imraguen, the park is under pressure from a growing fleet and incursions from non-Imraguen fishermen. The park is also threatened by industrial fishing operations not far from its boundaries. Fishing zones are shifting in response to the scarcity of fish stocks, but also to changes in habitat and rising sea levels due to the warming of waters as a result of climate change.
Outdoor recreation and tourism
The property has a considerable, as yet strongly underused potential for nature based tourism, such as birding tours. There is also accepted level of infrastructure to receive the tourists from inside and outside the country after rehabilitating the sustainable tourism industry in PNBA (Salim and Abdulhalim, 2016).
Factors negatively affecting provision of this benefit
Climate change
Impact level - High
Trend - Increasing
Pollution
Impact level - Moderate
Trend - Increasing
Overexploitation
Impact level - High
Trend - Continuing
Habitat change
Impact level - Moderate
Trend - Continuing
Under current circumstances, the PNBA is “naturally protected” from a massive invasion of tourists. Even if the Nouakchott-Nouadhibou Road has made access less difficult, because of the ramps, the fact remains that the lack of adequate infrastructure limits mass tourism. It is also a policy of the management authorities to limit pressure on resources and disturbance of the environment.
Importance for research,
Contribution to education
The National Park comprises a wide range of phenomena, which in turn support global knowledge generation on bird migration, ichthyology, coastal ecology and oceanography. It also supports long-lasting traditional knowledge system, such as those of the Imraguen. A new genus and species of fish within the marine shallow waters of PNBA has been discovered, and this discovery is considered as a good indicator of the richness of the marine fauna, and the possibility of discovering more species in the region (Seret & Naylor, 2016). Additionally, the Environmental Educational Center in Chami will play a key role in shading more light on the values of PNBA and raising long-term awareness.
Carbon sequestration,
Coastal protection
Carbon sequestration by intertidal vegetation is important. The areas occupied by this type of habitat extend some 450 km2 (IUCN Consultation, 2017). The PNBA contribution to carbon sequestration has recently been evaluated as ~80 millions €/yr and corresponds to 22% of the annual sequestration goal proposed by Mauritania during the Paris Agreement in 2015 (Trégarot et al., 2018). 
Factors negatively affecting provision of this benefit
Climate change
Impact level - Moderate
Pollution
Impact level - High
Trend - Continuing
Overexploitation
Impact level - High
Trend - Increasing
Habitat change
Impact level - Moderate
Trend - Continuing
Carbon sequestration,
Coastal protection
Seagrass beds, mudflats, salt marshes and mangroves of PNBA attenuate wave's energy and height and therefore contribute to the protection of the coast and villages particularly in the face of climate change (sea-level rise, extreme climatic events) (Trégarot et al. 2018). They also protect low-elevated islands, Nair and Zira, which supports breeding colonies of birds, including the endemic Mauritanian Spoonbill, Platalea leucorodia balsaci. The coastal protection provided by marine coastal ecosystems include the stabilisation of soil and flood prevention.
Factors negatively affecting provision of this benefit
Habitat change
Impact level - Moderate
Trend - Continuing
The vast expanse of seagrass is a real carbon sink. As for the mangroves, they are virtually stable or even in slight retreat. It is a relict formation that is destined to disappear.
Pollination
Beyond ecosystems, birds also provide a wide range of services to people. They contribute to the recycling of nutrients, carcass removal, biological control of harmful species, seed dispersal, sentinel to environmental changes, and cultural services such as bird-watching and a object of study for research and education. Nutrients input and carcasses removal were valued at 1.8 to 133.7 million €/year and 2,900 to 4,800 € respectively (Cornet et al. 2018, 2020).
The conservation and socio-economic benefits of the property reach far beyond its boundaries, as illustrated by its crucial role in carbon sequestration, its pivotal role in bird migration and as a spawning and nursery area for commercially exploited fish. There are also significant potential benefits, which could be developed further, such as those related to tourism and the ones related to the cultural and heritage value of the PNBA (but see Trégarot et al. 2018 for a broader vision of the benefits rendered by PNBA).

References

References
1
Abulhawa, T., Abdulhalim, H., Osipova, E. & Cummings, T. (2014). TABE’A II Report: Enhancing Regional Capacities for World Heritage. Amman, Jordan: IUCN. ii + 74pp.
2
BirdLife International (2019) Site factsheet: Banc d'Arguin National Park. Downloaded from https://datazone.birdlife.org/site/factsheet/banc-d'arguin-… on 16/05/2025
3
Boide C.C., Cornet C., Trégarot E. & Failler P. (2018). Evaluation de la valeur économique du tourisme au PNBA. In Trégarot et al. (2018). Evaluation des services écosystémiques du Banc d'Arguin, Mauritanie. pp. 213-224.
4
CSE (2024). Rapport d’évaluation de la vulnérabilité, d’analyse du risque et des capacités d’adaptation aux Changements Climatiques du Parc National du Banc-d’Arguin. Initiative Solutions écosystémiques d’adaptation durable (SEDAD). Centre de Suivi Ecologique (CSE). In: State Party of Mauritania (2024). Rapport sur l’état de conservation du Parc National du Banc d’Arguin et de la mise en œuvre des recommandations du Comité du Patrimoine Mondial. Available at: https://whc.unesco.org/document/218271 [Accessed on 16 April 2025]
5
Catry, P., Senhoury, C., Sidina, E., El Bar, N., Bilal, A. S., Ventura, F., Godley, B.J., Pires, A.J., Regalla, A., & Patrício, A.R. (2023). Satellite tracking and field assessment highlight major foraging site for green turtles in the Banc d'Arguin, Mauritania. Biological Conservation 277: 109823. https://doi.org/10.1016/j.biocon.2022.109823
6
Cornet C., Trégarot E. & Failler P. (2023). Birds of the National Park of Banc d’Arguin, Mauritania: A Panel on Ecosystem Services. Journal of Sustainability Research DOI: 10.20900/jsr20230009
7
Cornet C., Trégarot E., Failler P. (2018). Les oiseaux du Parc National du Banc d'Arguin: Services écosystémiques et potentiel économique. In Trégarot et al. (2018). Evaluation des services écosystémiques du Banc d'Arguin, Mauritanie. pp. 275-292.

Cornet C., Trégarot E., Failler P. (2020). Birds of the National Park of Banc d'Arguin, Mauritania: a panel on ecosystem services. (submitted) Condor.
8
Correra A. (2006). Dynamique de l'utilisation des ressources fourragères par les dromadaires des pasteurs nomades du Parc national du Banc d'Arguin (Mauritanie). Thesis, PNHN, Paris.
9
Dia, M., El Vally, Y., Meissa, B., Abdallahi, I. C., Diop, M., Bouzouma, M. M., ... & Jabado, R. W. (2023). Evolution of catches and specific composition of elasmobranchs in Mauritanian artisanal, coastal and offshore fisheries. Fisheries Research, 267, 106810.
10
Diagana, M. (2005). Approche spatiale de la biodiversité (flore et végétation) dans une aire protégée saharienne: le parc national du Banc d'Arguin (Mauritanie): développement d'un outil de gestion (Doctoral dissertation). Université d'Angers, 333p
11
Ecofin Agency (2023). Kinross Gold's Tasiast mine in Mauritania hits record gold production following expansion. Article news. [online]Available at: https://www.ecofinagency.com/mining/2702-45223-kinross-gold… [Accessed on 22 May 2025]
12
El-Hacen, E.H.M., Bouma, T.J., Fivash, G.S., Sall, A.A., Piersma, T., Olff, H. & Govers, L.L. (2018). Evidence for ‘critical slowing down’ in seagrass: a stress gradient experiment at the southern limit of its range. Nature, Scientific reports 8(1): 1-11.
13
El-Hacen, M. (2023). Mapping subtidal habitats in the Parc National du Banc d’Arguin (PNBA), Mauritania: Final Report. Prepared for PNBA Mauritania and The Biodiversity Consultancy Ltd (TBC), UK.
14
Gagnol, L., Magrin, G. & Chevrillon-Guibert, R. (2020). Chami, ville nouvelle et ville de l’or. Une trajectoire urbaine insolite en Mauritanie. L’Espace Politique 38: Revue en ligne de géographie politique et de géopolitique. https://journals.openedition.org/espacepolitique/6562?lang=… (Accessed 16 May 2025).
15
Gascuel, D., Labrosse, P., Meissa, B., Sidl, M.O.T. & Guenette, S. (2007). Decline of demersal resources in North-West Africa: an analysis of Mauritanian trawl-survey data over the past 25 years. African Journal of Marine Science 29: 331-345.
16
Global Fishing Watch (2020). Interactive map with global fishing data. Global Fishing Watch. Available at: https://globalfishingwatch.org/map/. Accessed 2 March 2020.
17
Hama, F. L., Karaica, D., Dyc, C., Bilal, A.S.O., Wagne, M.M., Bâ, O.Y., Mullié, W. & Fretey, J. (2019). Sea turtle stranding events along the Mauritanian coast. Salamandra 55(3): 199-210.
18
Hollman, P. C., Bouwmeester, H., Peters, R.J.B. (2013). Microplastics in aquatic food chain: sources, measurement, occurrence and potential health risks. RIKILT Re- port 2013.003. RIKILT Wageningen UR (University & Research Centre), Wageningen.
19
IPCC (2019). IPCC Special Report on the Ocean and Cryosphere in a Changing Climate. H.-O. Pörtner, D.C. Roberts, V. Masson-Delmotte, P. Zhai, M. Tignor, E. Poloczanska, K. Mintenbeck, A. Alegría, M. Nicolai, A. Okem, J. Petzold, B. Rama, N.M. Weyer (eds.). Cambridge University Press, Cambridge, UK and New York, NY, USA, 755 pp. https://doi.org/10.1017/9781009157964.
20
IUCN Consultation (2025). IUCN Conservation Outlook Assessment pers. comm.: Parc National du Banc d'Arguin (Mauritanie).
21
Lemrabott, S. Y. C., van Leeuwen, A., Leurs, G., El‐Hacen, E. H. M., Piersma, T., Sall, A. A., ... & Olff, H. (2024). Overfishing of Threatened Bycatch Species in a Marine Protected Area: The Elasmobranchs of Banc d'Arguin, Mauritania. Fisheries Management and Ecology, e12786.
22
Maha, M.M., Matsuyama, A., Arima, T., Sainoki, A. (2023). Assessment of Total Mercury Levels Emitted from ASGM into Soil and Groundwater in Chami Town, Mauritania. Sustainability 2024, 16, 7992.
23
Meissa B., Gascuel D. (2018). Contribution du PNBA aux pêcheries du plateau continental Mauritanien. In Trégarot et al. (2018). Evaluation des services écosystémiques du Banc d'Arguin, Mauritanie. pp. 139-149.
24
ONISPA (2024). Note sur le niveau de mercure en Mauritanie (zone littorale et ville de Chami). Office National d’Inspection Sanitaire des Produits de la Pêche et de l’Aquaculture. In : State of Conservation Report by the State Party: Parc National du Banc d’Arguin (Mauritania), pp. 191-193 [online]. Available at: https://whc.unesco.org/document/218271 [Accessed on 16 April 2025]
25
Oudman, T., Schekkerman, H., Kidee, A., van Roomen, M., Camara, M., Smit, C., ten Horn, J., Piersma, T. & El-Hacen, M.E.-H. (2017). Changes in the waterbird community of the Parc National du Banc d’Arguin, Mauritania, 1980-2017. Bird Conserv. Int. 30(4): 618-633. 10.1017/S0959270919000431
26
PNBA (2018). Rapport de l’atelier scientifique international d’Iwik-PNBA : Communications 2 et 3 de Theunis Piersma et Jan Van Gils (NIOZ) in: State Party of Mauritania (2019). Rapport de l’État de Conservation du Parc National du Banc d’Arguin (PNBA) et la mise en œuvre des recommandations du Comité du Patrimoine de L’UNESCO. https://whc.unesco.org/en/list/506/documents/
27
PNBA (2020). Plan d’Aménagement et de Gestion 2020-2024. Published March 2020. Available at : https://rsis.ramsar.org/RISapp/files/41361735/documents/MR2… [Accessed on 22 April 2025]
28
PNBA (2023). Rapport de l’atelier «Risques de pollution des écosystèmes du banc d’Arguin par les activités anthropiques ». Résumé des présentations – Iwik 20-22 juin 2023. In : State of Conservation Report by the State Party: Parc National du Banc d’Arguin (Mauritania), pp. 194-269. [online]. Available at: https://whc.unesco.org/document/218271 [Accessed on 16 April 2025]
29
Pottier, A., Catry, T., Trégarot, E., Maréchal, J. P., Fayad, V., David, G., ... & Failler, P. (2021). Mapping coastal marine ecosystems of the National Park of Banc d’Arguin (PNBA) in Mauritania using Sentinel-2 imagery. International Journal of Applied Earth Observation and Geoinformation, 102, 102419.
30
Rakhimberdiev, E., Duijns, S., Karagicheva, J., Camphuysen, C. J., Dekinga, A., Dekker, R., ... & Soloviev, M. (2018). Fuelling conditions at staging sites can mitigate Arctic warming effects in a migratory bird. Nature communications, 9(1), 1-10.
31
Ramsar (2023). Parc National du Banc d'Arguin. Ramsar Sites Information Service. https://rsis.ramsar.org/ris/250 Accessed 15 May 2025.
32
Salim, M.A., and Abdulhalim, H.S. (2016) Technical Report on a mission to Mauritania 25th of March - 2nd of April, 2016. The Arab Regional Center for World Heritage and International Union for Conservation of Nature. Internal technical report.
33
Seret. B, Naylor, G.J., (2016) Rhynchorhina mauritaniensis, a new genus and species of wedgefish from the eastern central Atlantic (Elasmobranchii: Batoidea: Rhinidae). Zootaxa. 2016 Jul 15; 4138(2):291-308. doi: 10.11646/zootaxa.4138.2.4.
34
Serrao, E. (2018). Rapport d'Ester Serrao (Université de l'Algarve, Portugal) sur les activités menées après la réunion du Conseil scientifique du PNBA (8-9 mai 2018). Annexe IV in State Party of Mauritania (2019). Rapport de l’État de Conservation du Parc National du Banc d’Arguin (PNBA) et la mise en œuvre des recommandations du Comité du Patrimoine de L’UNESCO. https://whc.unesco.org/en/list/506/documents/
35
Setälä, O., Norkko, J. & Lehtiniemi, M. (2016). Feeding type affects microplastic ingestion in a coastal invertebrate community. Marine Pollution Bulletin 102: 95-101.
36
State Party of Mauritania (2009). Parc National du Banc d’Arguin: Etat de Conservation. Ministère délégué auprès du Premier Ministère chargé de L’environnement et développement durable. 16 pp.
37
State Party of Mauritania (2015) Rapport de l’Etat de Conservation du Parc National du Banc d’Arguin (PNBA) et la mise en œuvre des recommandations du Comité du Patrimoine de L’UNESCO. https://whc.unesco.org/en/list/506/documents/ [Accessed 25 May 2025].
38
State Party of Mauritania (2019). Rapport de l’état de conservation du Parc National du Banc d’Arguin (PNBA) et la mise en œuvre des recommandations du Comité du Patrimoine de L’UNESCO. 20pp + annexes. https://whc.unesco.org/en/list/506/documents
39
State Party of Mauritania (2021). Rapport Périodique Cycle 3, Section II: Parc National du Banc d’Arguin (Mauritania). [online]. Available at: https://whc.unesco.org/document/216854 [Accessed on 16 April 2025]
40
State Party of Mauritania (2022). State of Conservation Report by the State Party: Parc National du Banc d’Arguin (Mauritania). [online]. Available at: https://whc.unesco.org/document/191574 [Accessed on 16 April 2025]
41
State Party of Mauritania (2024). State of Conservation Report by the State Party: Parc National du Banc d’Arguin (Mauritania). [online]. Available at: https://whc.unesco.org/document/218271 [Accessed on 16 April 2025]
42
Trégarot E., Catry T., Pottier A., Cornet C., Maréchal J.-P., Fayad V., Sidi Cheick M.A., David G., Dia A.D., Fall A.D., Sarr O., El Valy Y., Wagne O.H., Meissa, B., Kane E.A., Ball A.C., Haidallah M.S., Braham C.B., Dia M., Abdel Hamid M.L., Rey-Valette H., Salles J.-M., Ly D., Cissé C.B. et Failler P. (2018). Évaluation des services écosystémiques du Banc d’Arguin, Mauritanie. Rapport final pour le Parc National du Banc d’Arguin. 366 pp.
43
UNEP-WCMC (2012). Banc d’Arguin National Park, Mauritania. UNEP-WCMC World Heritage Information Sheets. http://world-heritage-datasheets.unep-wcmc.org/datasheet/ou… Accessed 15 May 2025.
44
UNESCO & IUCN (2014). Mission de suivi réactif Parc national du Banc d’Arguin (Mauritanie) 6 - 13 janvier 2014. 43pp + annexes. https://whc.unesco.org/en/list/506/documents/
45
UNESCO (2007). State of Conservation Report: Banc d’Arguin National Park (N 506). https://whc.unesco.org/en/soc/974 [Accessed 15 May 2025].
46
UNESCO (2008). State of Conservation Report: Banc d’Arguin National Park (N 506). https://whc.unesco.org/en/soc/891. Accessed 15 May 2025.
47
UNESCO (2009). State of Conservation Report: Banc d’Arguin National Park (N 506). https://whc.unesco.org/en/soc/634 Accessed 15 May 2025.
48
UNESCO (2013). State of Conservation Report: Banc d’Arguin National Park (Mauritania) (N506). https://whc.unesco.org/en/soc/1924. Accessed 15 May 2025.
49
Vousdoukas, M.I., Ranasinghe, R., Mentaschi, L. et al. (2020). Sandy coastlines under threat of erosion. Nature Climate Change 10: 260–263. https://doi.org/10.1038/s41558-020-0697-0
50
WWF (2013). ‘List of Priority Global 200 Ecoregions: Canary Current’. [Electronic reference] World Wildlife Fund. Accessed 3 June 2013.
51
Williams R., Wright A. J., Ashe E., Blight L., Bruintjes R., Canessa R., Clark C., Cullis-Suzuki S., Dakin D., Erbe C. (2015). Impacts of anthropogenic noise on marine life: publication patterns, new discoveries, and future directions in research and management. Ocean & Coastal Management, 115, 17-24.
52
World Heritage Committee (2010). Statement of Outstanding Universal Value: Banc d'Arguin National Park. World Heritage Committee https://whc.unesco.org/en/decisions/4261
53
World Heritage Committee (2021). Decision 44 COM 7B.87. [online]. UNESCO World Heritage Centre. Available at: https://whc.unesco.org/en/decisions/7802 [Accessed on 22 April 2025]
54
World Heritage Committee (2023). Decision 45 COM 7B.11. [online]. UNESCO World Heritage Centre. Available at: https://whc.unesco.org/en/decisions/8276 [Accessed on 22 April 2025]

Indigenous Heritage values

Would you like to share feedback to support the accuracy of information for this site? If so, send your comments below.

CAPTCHA
This question is for testing whether or not you are a human visitor and to prevent automated spam submissions.