Sanganeb Marine National Park and Dungonab Bay – Mukkawar Island Marine National Park
Country
Sudan
Inscribed in
2016
Criteria
(vii)
(ix)
(x)
The conservation outlook for this site has been assessed as "good with some concerns" 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.
The property consists of two separate areas: Sanganeb is an isolated, coral reef structure in the central Red Sea and the only atoll, 25 km off the shoreline of Sudan. The second component of the property is made up of Dungonab Bay and Mukkawar Island, situated 125 km north of Port Sudan. It includes a highly diverse system of coral reefs, mangroves, seagrass beds, beaches and islets. The site provides a habitat for populations of seabirds, marine mammals, fish, sharks, turtles and manta rays. Dungonab Bay also has a globally significant population of dugongs. © UNESCO
Summary
2025 Conservation Outlook
Finalised on
11 Oct 2025
Good with some concerns
Current state and trend of VALUES
Low Concern
Overall THREATS
Overall PROTECTION and MANAGEMENT
Full assessment
Description of values
An outstanding example of the northernmost tropical coral reef systems on earth
Criterion
(ix)
The property including Sanganeb Marine National Park (SMNP) and Dungonab Marine National Park (DMNP) lies on the western shore of the north-central Red Sea and is located in an ecologically and globally outstanding region (World Heritage Committee, 2016). It is within the world’s northernmost tropical sea and is a Global 200 priority biogeographic region (State Party of Sudan, 2013). The habitats of the property are diverse and mostly undisturbed, representing the transition between northern and southern Red Sea biogeographic zones. The property and its surrounding area include a wide variety of different bio-physiographic reef zones with beaches, lagoons, islets, mud and sand flats, seagrass beds and mangrove habitats and a huge diversity of coral reefs, from living to ancient fossil reefs, and one of the largest and best known atoll-like features in the Red Sea (State Party of Sudan, 2013; IUCN, 2014; World Heritage Committee, 2016).
Exceptional level of Biodiversity
Criterion
(x)
The site hosts an exceptional diversity of species from both the northern and southern Red Sea including endemic and rare species. The site hosts populations of corals (260 species), fish (361 species), seabirds (20 species), marine turtles (5 species) and marine mammals (11 species). The site provides important nursery and spawning grounds for threatened and endangered species and there are healthy populations of sharks, manta rays and dugong. The seasonal aggregation of manta rays in DMNP is one of the few known sites within the western Indian Ocean. The site is also an important feeding ground for what is now perhaps the most northerly population of endangered dugong in the Red Sea (State Party of Sudan, 2013; World Heritage Committee, 2016; IUCN Consultation, 2020). DMNP and SMNP lies in a regional hotspot for reef fish endemism (IUCN, 2014). The property generally supports a higher than average subset of endemics than found elsewhere in the Red Sea, including a rich diversity of coral and a number of coral species that are at the limits of their global range (World Heritage Committee, 2016).
Impressive natural phenomena, formations and areas of great natural beauty
Criterion
(vii)
The property contains impressive natural phenomena, formations and areas of great natural beauty and is a relatively undisturbed area that serves as a standard to assess the health of the central Red Sea’s regional ecosystems (World Heritage Committee, 2016). As a prime example of a deep-water offshore coral reef, Sanganeb provides an outstanding opportunity for comparative studies with similar systems in other regions including the Indian and Pacific Oceans and a place to understand the interactions of biota and the environment (IUCN, 2014). Located within the Red Sea’s centre of biodiversity the remarkable clarity of the water makes it one of the best diving sites in the Red Sea and indeed the world.
Assessment information
Threats to the property are limited in both number and magnitude as a result of its relative isolation and the fact that both the property and the surrounding buffer zone are currently exposed to minimal, low intensity human activity. The most concerning current threats include damage to corals by tourist liveaboard vessels through wild-anchoring directly on the reefs, and rising sea surface temperatures leading to localised coral bleaching. Although previous surveys have indicated that reefs in the property were relatively healthy, supporting a diverse fish population, and bleached corals covered relatively small areas, repeat surveys at Sanganeb atoll have found a long-term reduction in accretion rate and changes in community composition reflecting rising sea surface temperatures and bleaching events. Overall, whilst the onset of recurrent severe bleaching heat stress events is relatively low in comparison to other World Heritage coral reefs, the threat itself remains high, given the potential severity of coral bleaching on the values of the site.
Fishing, Harvesting & Controlling Aquatic Species
(Small-scale commercial and subsistence fishing by local communities)
Inside site
, Scattered(5-15%)
Outside site
Human activities have until very recently remained at relatively low levels with small-scale commercial fishing and subsistence fishing being the key direct human impact on the property (IUCN, 2014). Small-scale commercial fishing and subsistence fishing is generally permitted inside the site except for no-take zones, which includes SMNP, where all types of fishing are prohibited. Previous surveys have indicated that reefs were relatively healthy and support a diverse fish population (APF 2006, Cousteau Society, 2013). More recent surveys have been conducted to assess the fisheries in the area by staff and students from the Red Sea University, Port Sudan working in partnership with scientists from the Institute of Marine Research, Norway, under a project supported by UNIDO (Olsen et al. 2021). The grouper fishery is of particular concern, as this fishery targets spawning aggregations known to occur within the site (Elanaeim 2012). There have been intermittent accounts of illegal fishing on SMNP, particularly for Trochus. The continued use of monofilament nets within the small-scale commercial fisheries poses a particular threat to marine mega-fauna (Adam 2013), especially where these gear are used within known feeding grounds of the endangered dugong and manta rays (Klaus, 2017). Threat from the local communities in Dungonab Bay to the fish resource is spearfishing (powered speargun and Harpoons) (IUCN Consultation, 2020). Other threats are gill net fishing for mullet in the lagoons by fishers from outside the Dungonab community. The fishers fish on foot (do not possess boats) and transfer the catch by lorries to the Port Sudan fish market. Increased shell collection from Dungonab Bay by collectors from Port Sudan for making souvenirs is another issue. In most cases, sea turtle (two species in Dungonab) is not returned to the sea when the fisher caught it incidentally. Management on the ground, enforcement, and awareness among fishers are lacking.
Fishing, Harvesting & Controlling Aquatic Species
(Illegal, unregulated, unlicenced commercial fishing)
Inside site
, Scattered(5-15%)
Outside site
There were historical occurrences of large scale commercial fishing inside the property, involving the use of destructive fishing gear such as trawling. More recently new trawling licences were issued but it remains unclear if these fisheries commenced and the location of their operations. The clarified marine boundaries of the reserves which comprise the site (Klaus, 2017) mitigate this threat to some extent.
Recreational Activities
(Wild-anchoring)
Inside site
, Localised(<5%)
There is an increasing number of large tourist liveaboard vessels (motor sailing yachts) that have been visiting the site in recent years, most of which originate from Egypt. The liveaboard vessels are causing damage to sensitive coral habitats when they deploy and recover their anchors (Cousteau Society 2013; IUCN Consultation, 2017). To mitigate the damage caused by these large boats anchoring within the site, there is an urgent need to prohibit wild-anchoring, to install fixed mooring buoys and to educate the tourism operators in the proper use of these moorings (Klaus, 2017). It was found that some coral reefs are degraded as a result of coral destruction from dumping of anchor (Abdelhamid et al. 2024).
Marine & Freshwater Aquaculture
(Mariculture of shrimp and pearl oyster)
Inside site
, Localised(<5%)
There is a pearl oyster farm within Dungonab Bay. The farm has ceased operations for nearly a decade. Some of the infrastructure remains. There are various other prawn farms along the mainland coast at the southern end of the site. Many of these sites are no longer operational.
Commercial & Industrial Areas
(Saltworks)
Inside site
, Localised(<5%)
There is an evaporative saltworks on the tip of the peninsular within DMNP, which is a pre-existing operation of potential historical interest that has limited impact on the site values. The extracted salt is transported by truck to Port Sudan along the main coastal road.
Problematic Native Species
(Crown of Thorns starfish and other marine species)
Invasive/problematic species
Acanthaster planci
Inside site
, Localised(<5%)
Outside site
Coral predators such as the Crown of Thorns starfish (Acanthaster plancii) and Drupella, a small gastropod snail, occur naturally on many reefs worldwide and they have been recorded within the property in high abundances at some sites (PERSGA 2004; Cousteau Society 2013). The Crown of Thorns can pose a potentially serious threat if there are outbreaks. In other regions outbreaks have been linked to increased nutrient input (Brodie et al. 2005). Monitoring of impacts from species such as these is required to assess the level of impact and threat, although it is thought that outbreaks have never been as significant as those elsewhere in the region such as in Egypt (State Party of Sudan, 2018). This pattern is likely driven by low nutrient input, reflective of the current limited coastal development.
Changes in Physical & Chemical Regimes, Changes in Temperature Regimes
(Increase in coral bleaching from increased severity and frequency of temperature extremes)
Inside site
, Widespread(15-50%)
Outside site
Coral bleaching is considered to be the most significant threat for the corals present in the property (IUCN, 2014). Previous surveys have indicated that reefs in the property were relatively healthy, supporting a diverse fish population, and bleached corals covered relatively small areas (PERSGA 2004; Cousteau Society 2013). However, repeat surveys at Sanganeb atoll have found a long-term reduction in accretion rate and changes in community composition reflecting rising sea surface temperatures and bleaching events (Abdelhamid et al. 2024). Overall, whilst the onset of recurrent severe bleaching heat stress events is relatively low in comparison to other World Heritage coral reefs (Heron et al., 2018), the threat remains high, given the potential severity of coral bleaching on the values of the site. A field survey of coral reefs in Dungonab showed that there is no thermal bleaching in the reefs (Saad et al. 2024).
The main potential threats to the site arise from issues such as increased tourism and associated development, coastal development in general, biological impacts, increased shipping activity, the expected consequences of climate change and increased activity from local residents. Currently the property is largely unaffected by threats, partly due to its isolation and limited visitation, however the operation of foreign tourism ventures causing damage to the reef within the site is a growing cause for concern. Limited management presence and virtually no available data on the baseline values of the property will make it difficult to not only respond but detect any impacts to the site.
Recreation & Tourism Areas
(Increase in visitation from tourism)
Inside site
, Localised(<5%)
Outside site
Despite limited infrastructure to support tourism there is growing interest in the site as a result of overcrowding in other similar locations within the Red Sea (IUCN, 2014). The resulting increases in recreational vessels, including live aboard dive vessels, could potentially impact on the property through pollution from tourism activities, anchor damage from an increase in the number of vessels and direct damage to reef ecosystems from diving related activities including boat damage. There is some concern over increasing interest by investors to start development projects both outside and within the property, and there is a lack of regulations to manage development activities in the area.
Fishing, Harvesting & Controlling Aquatic Species
(Increase in fishing within the property.)
Inside site
, Scattered(5-15%)
There are currently two local communities residing within the buffer zone of the property and utilizing the area for subsistence fishing. Given the harsh conditions in the area and an expressed interest from the communities to move away from livelihoods dependant on fishing it is unlikely the communities will expand in number significantly. However, increased monitoring of impacts from fishing should be conducted to ensure no adverse impacts on the values of the property and further awareness of the natural values of the site and the boundaries of the Marine Park are needed.
Commercial & Industrial Areas
(Spread of coastal development)
Inside site
, Extent of threat not known
Outside site
It has been noted that there is growth of coastal development along the Sudanese Red Sea coastline, especially focussed in the 70kms of coastline south of Port Sudan to Suakin, where there are two major ports, oil refineries, a desalination plant, saltworks, power station, a shrimp farm and the new Red Sea Economy Free Trade Zone (IUCN, 2014). Increased development has also begun to spread northwards from Port Sudan, but communities around the property remain small due to poor living conditions and little infrastructure (Osman and Ibrahim 2022) . Whilst the property remains in good condition this context reinforces the need to protect landward areas which are integral to the values of the marine areas and to upscale resources and management capacity.
Water-borne & other effluent Pollution
(Oil spill from an oil tanker)
Inside site
, Extent of threat not known
Outside site
The Red Sea experiences high shipping volumes, including vessels carrying almost five million barrels of oil on a daily basis (Kleinhaus et al. 2020). There is thus a potential threat of oil spills from tankers. The fate of spilled oil will depend on the point of release and weather and oceanographic conditions, with oil likely to reach the property from a spill in the northern or central Red Sea in most seasons (Mittal et al. 2021). The negative ecological impacts of oil spills along the Egyptian Red Sea coast highlight the high risk to the important coral reefs and associated biodiversity within the property.
Garbage & Solid Waste
(Beach litter)
Inside site
, Widespread(15-50%)
Outside site
Beach litter is a common global phenomenon and can be of terrestrial or ocean origin. While beaches within the property are considered clean by global standards, beach litter occurs year-round, with plastic litter most common (Ibrahim et al. 2020). Recreational users are thought to be the primary source of litter, highlighting that awareness campaigns could help to prevent the escalation of this risk.
Shipping Lanes
(Damage from ships or shipping accidents)
Inside site
, Extent of threat not known
Outside site
While there is little to no evidence of impacts from shipping traffic within the property at the moment, the threat remains given the increase in shipping globally and within the vicinity of the site. Increasing levels of shipping traffic increases the potential for accidents and impacts resulting from spills and physical damage caused by collisions. In 2024 political unrest in the middle east saw seen a decline in ship traffic through the Red Sea (Notteboom et al. 2024). Should this trend persist, this threat will decrease.
Involvement of stakeholders and rightsholders, including indigenous peoples and local communities, in decision-making processes
The MNP boundaries and inscription on the World Heritage List is likely to have had little impact on the activities of local people within the area. Local communities are allowed to fish within the Marine Park as well as the buffer zone with restrictions on fishing activities related to the kind of fishing gear used. The local communities living within DMNP were consulted about the creation of the national park during the PERSGA MPA-SAP project and no-take zones before the area was gazetted in 2004. There also appear to be no significant or ongoing cultural rights issues with the local communities. However, the IUCN evaluation mission to the property indicated there was limited evidence of consultation or awareness raising efforts with local communities (IUCN, 2014). In 2016, an IUCN / Arab Regional Centre for World Heritage (ARC-WH) mission to the property found that progress is being made by the local authorities engaging with local communities and involving them in certain aspects of management, and this is consolidated in the Integrated Management Plan (Klaus, 2017), which was informed by a series of training and planning workshops involving local communities to discuss the vision, goals and objectives for inclusion in the plan (State Party of Sudan, 2018). This work was continued through four workshops held in 2021, that targeted woman (State Party of Sudan 2022). A UK-Aid Darwin Initiative funded project supported a national communication campaign which used social media to raise awareness about the site and organised events and outreach activities around the country and in Port Sudan and in the villages in DMNP (Cousteau Society 2016). In 2022 community beach clean ups were held (State Party of Sudan 2022) while in 2023 students from villages near the property were co-opted into a project using eDNA to collect biodiversity data. Such collaborative work strengths relationships with local communities.
Legal framework
There is a commitment from the Government of Sudan at both the national and state level towards the protection and conservation of resources within its coastal waters, including the property. Several laws and regulations are in place and Sudan has signed and abides to regional and international protocols and conventions. Both SMNP (1990) and DMNP (2004) have been declared as marine protected areas. SMNP was declared as a marine national park in 1990 by the Secretary General of the Council of Ministers, under the Federal Wildlife and Hunting Law of 1986, by the order “Approval to Declare the Area of Sanganeb in the Red Sea a National Park”, which was signed on on 1st April 1990. DMNP was legally declared as a national park in 2004, following the World Bank GEF funded PERSGA Marine Protected Area Strategic Action Programme (MPA-SAP). The national park was legally declared by the President of Sudan as ‘Dungonab Federal Reserve’ under the Federal Wildlife and Hunting Law of 1986, “Order to Designate the Dunqonab Area of the Red Sea a Federal Reserve for the Year 2004”, which was signed on 13th October 2004. As such both SMNP and DMNP are protected under the Federal Government of Sudan and covered by various other pieces of national legislation. The buffer zone is not legally protected (IUCN Consultation, 2020).
Governance arrangements
The governance of the property has been formally entrenched since its declaration as a WH site. The management of the property spans both national and state level Government with the main responsibility for management assigned to the Wildlife Conservation General Administration (WCGA), under the Ministry of Tourism and Wildlife at the National Level. The state level is also involved in the management through the Ministry of Agriculture and Natural Resources, which is responsible for all environmental matters in the Red Sea State. However, it is not clear if and to what degree good collaboration occurs between the different levels of government and the relative strength of different pieces of legislation.
Many stakeholders (communities, fishermen, markets traders, divers, officers of related government departments, researchers, Red Sea University, research centers, Security Departments, others) have participated in the training workshops implemented in Port Sudan in 2021 during phase two (2019-2024) of the UNIDO Project.
There is a potential risk that the protection of the property may be compromised given the strongly growing regional push for increased coastal development, commercial fishing, aquaculture and oil exploration. In the early 2020s local communities had increasingly been drawn into the management of the property (State Party of Sudan 2022), but this has been negatively affected by the war and political unrest. There is currently no IMP in place as it expired in 2021, and it has not been possible to develop a new IMP due to unrest and turnover in government (State Party of Sudan 2024).
Many stakeholders (communities, fishermen, markets traders, divers, officers of related government departments, researchers, Red Sea University, research centers, Security Departments, others) have participated in the training workshops implemented in Port Sudan in 2021 during phase two (2019-2024) of the UNIDO Project.
There is a potential risk that the protection of the property may be compromised given the strongly growing regional push for increased coastal development, commercial fishing, aquaculture and oil exploration. In the early 2020s local communities had increasingly been drawn into the management of the property (State Party of Sudan 2022), but this has been negatively affected by the war and political unrest. There is currently no IMP in place as it expired in 2021, and it has not been possible to develop a new IMP due to unrest and turnover in government (State Party of Sudan 2024).
Integration into local, regional and national planning systems (including sea/landscape connectivity)
A greater level of coordination and communication with neighbouring countries is needed to ensure the site is included in regional planning and this is also true in regards to national level planning systems. In particular, coordination at both the national and state level is needed in order to regulate the level of tourism with many live-aboard vessels now moving into the area during the peak tourism season. In addition, threats from mineral exploration and pollution from neighbouring countries will require greater coordination if they are to be assessed and planned for and the role of the site in supporting resilience in other similar locations should be considered within the wider Red Sea environment. At a national level, the Council is representative of a number of different sectors and ensures effective involvement of all stakeholders in the management of the property (State Party of Sudan, 2018). War and political unrest in Sudan has hampered these efforts.
PERSGA has started via Sustainable Fishery Development in Red Sea and Gulf of Aden (SFISH) project (2023-2025), to promote collaboration and coordination among PERSGA countries (Djibouti, Egypt, Jordan, Saudi Arabia, Somalia, Sudan, and Yemen).
PERSGA has started via Sustainable Fishery Development in Red Sea and Gulf of Aden (SFISH) project (2023-2025), to promote collaboration and coordination among PERSGA countries (Djibouti, Egypt, Jordan, Saudi Arabia, Somalia, Sudan, and Yemen).
Boundaries
At inscription, the World Heritage Committee provided specific recommendations to the State authorities that included a request to provide additional information about the boundaries of the property and an updated map (Decision WHC/16/40.COM/19), with reference to the information submitted prior to the 40th Session of the World Heritage Committee (WHC/16/40.COM/8B.Add) and the IUCN Evaluation Report (WHC/16/40.COM/INF.8B2). The Arab Regional Centre for World Heritage (ARC-WH) requested assistance, on behalf of the State party, in addressing the WHC Decision (WHC/16/40.COM/19). The boundary file for the property submitted by the Sudanese UNESCO MAB Committee was reviewed and an updated map prepared (Klaus 2018). The World Heritage core sites partially align with the boundaries of the two marine national parks, SMNP and DMNP, which both appear to be quite intact at the moment, both in terms of habitats and species and the boundaries are sufficient to include all the necessary conditions to protect the values for which it has been inscribed. The property covers a wide range of habitats that are ecologically and functionally interconnected and are necessary to maintain viable plant and animal populations, including shallow coastal areas, reef formations and deep-sea areas. In response to the World Heritage Committee's Decision, 2016, the 2018 State Party report stipulated that the process for declaration of Sha'ab Rumi as Sudan's third MPA was in progress (UNESCO 2023). However, due to war and political unrest this has not occurred. Given its clear potential to contribute significantly to the integrity and OUV of the existing site, should this area be included in the site in future (State Party of Sudan, 2018).
Overlapping international designations
Dongonab Bay-Marsa Waiai was designated as a Ramsar Site in 2005. Regular communication exists between management authorities of the Ramsar site and the World Heritage property (State Party of Sudan, 2021), however the extent to which the overlapping designations are effectively managed is not clear.
The MAB National Committee preparing to propose Dongonab MPA a Biosphere reserve focusing on the sustainable development of the local communities towards enhancing their integration in the proper conservation of the heritage property.
The MAB National Committee preparing to propose Dongonab MPA a Biosphere reserve focusing on the sustainable development of the local communities towards enhancing their integration in the proper conservation of the heritage property.
Implementation of World Heritage Committee decisions and recommendations
SMNP was first presented for inscription on the World Heritage list in the 1980s with the subsequent recommendation requesting the formal gazetting of the Marine Parks before inscription would be considered. As a result it was resubmitted and inscribed in 2016, with a number of requests imposed on inscription. As such, the State Party submitted a State of Conservation report (State Party of Sudan, 2018), which was considered by the World Heritage Committee in 2018. The actions of the State Party in the development of high quality maps and a draft Integrated Management Plan (IMP), the recruitment of additional staff, and the increase in resources were welcomed alongside the identification of additional areas of potential Outstanding Universal Value (OUV) for inclusion as part of the World Heritage site (World Heritage Committee, 2018). However, the State Party was also requested or encouraged to make increased resources for effective management, and address the growing potential threats related to growing tourism in and around the site. While progress was made on some requests (e.g. the Party State developed collaborations with international funders (British council and Czech Republic Development Cooperation) that contributed to implementation of the IMP (State Paty of Sudan, 2022)), the ability of the State Party to respond to WHC decisions and recommendations has been limited by the economic and political situation in the country (State Party of Sudan, 2024).
Climate action
While the threat of climate change to the property is recognised to some extent, especially the threat posed to the coral reefs (Abdelhamid et al. 2024), climate is currently not specifically provided for in the management approach. The property is important in terms of the ability of the Red Sea marine protected area network's ability to respond to climate change (Gajdzik et al. 2021).
Management plan and overall management system
The management system has been guided by the 2017-2021 Integrated Management Plan (IMP) (Klaus, 2017). The plan was well prepared with a management framework directly related to the OUV of the site. The management authorities of SMNP and DMNP established a management committee for the World Heritage property to improve coordination and communication between the agencies at the Federal and State Level given the shared mandate for the management of environmental issues. This committee also included other key stakeholders in the management of the property (IUCN Consultation, 2020). Unfortunately, the IMP expired in 2021 and the unstable political and socio-economic situation in the country have prevented the development of an IMP for the next five years period (State Party of Sudan, 2024). However, despite its expiry, most of the actions in the IMP remain valid and efforts continue to implement the plan. Some success has resulted from partnering with non-governmental, academic and research organisations (State Party of Sudan 2024).
Law enforcement
There is a potential risk that the protection of the property may be compromised given the strongly growing regional push for increased coastal development, commercial fishing, aquaculture and oil exploration. The MPA Division of the WCGA is located in Port Sudan, the capital of the Red Sea State. The WCGA has an operational base within DMNP, south of Mohammed Qol, one of the villages within the park. On SNMP, WCGA staff stationed on the atoll share the Sea Port Corporation facilities. The WCGA MPA staff are deployed to the MPAs from Port Sudan on a two-week rotation. Generally, each rotation consists of one MPA Manager and 10 rangers in DMNP and one staff member who is stationed on SMNP, who resides there with a staff member from the Sea Port Corporation. However, staffing levels were evaluated as very poor during the IUCN mission and capacity remains low, hamepring implementation of key management actions. No formal staffing changes have taken place as of 2024, but due to financial constraints no salaries are being paid (State Party of Sudan, 2024). To address these capacity gaps, various capacity building programmes are being developed by different institutions, including PERSGA, Cousteau, ARC-WH and IUCN Tabe'a Programme. However, these too have been disrupted by the war. Although the level of threats remain low, increasing potential threats, such as tourism, are such that the current resources and capacity of management staff may not be sufficient for ongoing effective management of the property.
Sustainable finance
There is currently no detail available in regard to the level of financing for the property and in particular future prospects for conservation financing. The source of financing for management is from the Federal Ministry of Finance through the support provided to the Wildlife Conservation General Administration (IUCN, 2014). While no detailed information is available, the Evaluation mission noted that very limited budgets are made available to the management agencies and there is a need to investigate and secure sustainable financing for the property. However, during a coordination meeting between different key institutions supporting Sudan, convened by IUCN Tabe'a Programme and ARC-WH, the State Party reported that it has increased the management budget by 500%. Nevertheless, the adequacy of the level of funding available to the property needs to be confirmed further, and indeed the World Heritage Committee has encouraged the State Party to make more resources available for the management of the site (World Heritage Committee, 2018). In response the State Party secured funds from a variety of sources towards implementation of various aims embedded in the 2017-2021 IMP. These include a nationally funded project (by the HCENR), and funding from the Czech Republic Development Cooperation (mangrove restoration) and British Council (offering micro loans in response to social challenges in local communities) (State Party of Sudan, 2022). It is currently unclear to what extent this has been achieved due to the war. In the latest Periodic Report, the State Party stated available fundings are inadequate for basic management needs and presents a serious constraint to the capacity to manage (State Party of Sudan, 2021).
Staff capacity, training and development
At the time the Integrated Management Plan was prepared (Klaus, 2017), the MPA Division of the WCGA staffing included: the General Manager for MPAs, four MPA Managers, all of whom have Bachelor degrees in Marine Biology and 35 rangers, many of whom were recruited from the local community, as well as other administrative personnel. Given the extent of its area and the potential for infringements, staffing levels are very poor and capacity incredibly low (IUCN Consultation, 2017). While the level and degree of threats remains low, the resources and capacity of management staff is such that it hinders effective management of the property, particularly in the face of increasing tourism and other threats (IUCN Consultation, 2020). While the management authority had established 5 ranger stations for monitoring and patrolling by 2017, the small staff numbers lack even basic equipment and transport and there is no information available on staff training or development (IUCN Consultation, 2017). This situation has not improved and salaries have not been paid to the WCGA officers and rangers due to limited resources (State Party of Sudan, 2024). To address these capacity gaps, various capacity building programmes are being developed by different institutions, including PERSGA, Cousteau, ARC-WH and IUCN Tabe'a Programme. However, these too have been disrupted by the war. Although the level of threats remain low, increasing potential threats, such as tourism, are such that the current resources and capacity of management staff may not be sufficient to ensure ongoing effective management of the property.
Some efforts with the objectives of increasing the capacity of the officers had been reached via the participation of the Director of the property, in the Regional Workshop on Community and Stakeholder Engagement in Comprehensive Planning for Interpretation and Presentation of World Heritage Sites, Doha, Qatar, 17-19 June 2025, organized by the UNESCO Regional Centre for the Gulf States and Yemen within the framework of cooperation between UNESCO and the Royal Commission for AL Aula Development.
Some efforts with the objectives of increasing the capacity of the officers had been reached via the participation of the Director of the property, in the Regional Workshop on Community and Stakeholder Engagement in Comprehensive Planning for Interpretation and Presentation of World Heritage Sites, Doha, Qatar, 17-19 June 2025, organized by the UNESCO Regional Centre for the Gulf States and Yemen within the framework of cooperation between UNESCO and the Royal Commission for AL Aula Development.
Education and interpretation programmes
There is an aquarium based in Port Sudan with some information around the marine ecosystem but the majority of visitation is currently based on live aboard vessels and as such opportunities for education and awareness are limited. However, the 2017-2021 IMP was informed by a number of workshops involving local communities. Such stakeholder engagement in the management of the property has likely fostered greater opportunities for better local awareness of the values of the site. Guidelines on Ecotourism in Marine Areas of Outstanding Value in the Red Sea and Indian Ocean were produced, and provide tour operators and guests information about diving and ecosystems within the property (State Party of Sudan, 2022). Additionally, in 2022 a training workshop was hosted by UNESCO and the Red Sea State to foster awareness among school teachers from the local community (State Party of Sudan, 2024). Inclusion of students in activities within the property (e.g. eDNA collection with scientists in 2023) provides additional educational opportunities. An educational program and awareness campaign was carried out in April 2025, for the communities of Dongunab Village and Mohammed Qol village. The aim was to foster local stewardship and support for manta conservation. The campaigns involved primary and secondary school students in Dongunab village, promoting awareness from a young age.
Awareness activities during phase one of UNIDO Project also included several workshops in Port-Sudan for all stakeholders and training abroad for researchers including training workshops in fish statistics (regular and systematic data from commercial markets) and fish identification (IUCN Consultation, 2025).
Awareness activities during phase one of UNIDO Project also included several workshops in Port-Sudan for all stakeholders and training abroad for researchers including training workshops in fish statistics (regular and systematic data from commercial markets) and fish identification (IUCN Consultation, 2025).
Tourism and visitation management
Even before the war the property had almost no on-ground management presence with most management actions linked to tourism and visitation during the busiest season when live aboard dive vessels visit from other parts of the Red Sea. A general increase in tourism to the site and associated pressures has occurred, following World Heritage inscription (IUCN Consultation, 2020). Monitoring of impacts from tourism activities should be conducted to detect any impact on key habitat types and species in anticipation of increased visitation, but currently appears not to occur. Residential and resort/tourism development in terrestrial areas both within the buffer zones and areas adjoining the property should be closely monitored to ensure population size and tourist numbers do not exceed the limits of infrastructure and ecosystems. There have been efforts by the State Party to encourage the gradual development of low impact tourism (State Party of Sudan, 2024). In recognition of the threat posed by elevated visitation to the reefs by live aboard dive tours the State Party had planned a workshop to discuss the development of a code of conduct for dive operations in the property. This had to be postponed due to the war (State Party of Sudan, 2024).
Sustainable use
Human impact, including that from the communities situated within the buffer zone is relatively low. There is private ownership of land within the buffer zone but this is strictly controlled through the legal framework controlling the area. Sustainable use activities are only allowed in the buffer zone and concentrate on artisanal fishing (IUCN Consultation, 2017). However, the extent to which use is monitored remains unclear.
Monitoring
A coral reef monitoring programme was established for both SMNP and DMNP with support from the African Parks Foundation (APF 2006). Maintaining regular monitoring proved challenging due to access issues and financial constraints. More recently, the staff from the Red Sea University re-started monitoring with support from PERSGA. The Integrated Management Plan for the site (Klaus, 2017) proposed the maintenance and expansion of the monitoring programmes, with the support of the Red Sea University in recognition of the fact that there are capacity constraints in terms of staff numbers within the WCGA. Monitoring of turtles took place in 2022 (State Party of Sudan, 2022) while coral communities have been monitored in 2022, 2023 and 2024 (State Party of Sudan, 2022, 2023). Further research and monitoring will need to be conducted within the property to address gaps in the baseline data. Increased monitoring of the impacts from fishing and tourism should be conducted to ensure no adverse impacts on the values of the property and to increase knowledge about the natural values of the site and the boundaries of the Marine Park are needed (IUCN, 2014). The impacts of increasing tourism in the area, especially and potential damage to the reefs from recreational diving, is also a growing requirement for monitoring (IUCN Consultation, 2020). Despite the war and severe financial constraints some monitoring of vessels in the property still takes place (State Party of Sudan, 2022) but it is unclear how sustainable this is. Some monitoring activities are ongoing through the implementation of Fish Statistic and Stock Assessment component of UNIDO PROJECT, that continued during 2019-2024.
Research
There is currently limited research being conducted within the property mainly due to difficulties with access, cost constraints and the war. The Red Sea University has established a research base in DMNP from which staff and students can conduct studies using small local fisher boats. However, due to the size of the property and the distances offshore, much of the property is only safely accessible from a larger vessel, such as a liveaboard dive boat. Despite these challenges studies of charismatic and endangered species including dugong, manta rays and sharks, have been conducted as well as studies of bird populations, and monitoring the status of the coral reefs and seagrass beds and local fisheries. The results of several of these studies have been published in scientific journals: manta rays (Kessel et al., 2017; Knochel et al. 2022), green sawfish (Elhassan et al., 2018), fisheries (Olsen et al. 2021), seagrass (Gaiballa and Ali 2023). The IUCN Consultation (2017) recommended that research and monitoring projects being conducted by the Red Sea University and collaborating researchers should be linked to the management of the property and the results used to inform management planning and actions. While this approach has shown promise, it has been disrupted by the war.
Effectiveness of management system and governance in addressing threats outside the site
The management of the property falls with a national legal framework with both portions of the property having been declared as marine protected areas by Presidential Decrees. While the Wildlife Conservation and National Park Act, (1987); National Parks, Sanctuaries and Reserves Regulation, (1939); and the Game Protection and Federal Parks Act (1986) govern the property itself, Federal Environmental Law (2001) and State Environmental Law (2006), together with legislation around fisheries, shipping and water quality speak to threats from outside the property. The current war has limited the formal enforcement of these instruments.
Effectiveness of management system and governance in addressing threats inside the site
The on the ground management of the property follows a complex structure. Responsibility for management of the property sits with the Wildlife Conservation General Administration (WCGA) under the National Government, however the state level government is also involved. The multi-agency and National and State level involvement in management results in somewhat complex procedures. For example, rangers from the National agency aware of infringements are required to report these to the relevant state level authority and then these incidents, if serious enough to warrant further action, are reported to the police. Staffing capacity was significantly increased during a PERSGA project and in response to concerns expressed by IUCN during a 2014 evaluation mission (State Party of Sudan, 2018). However, despite this, the World Heritage Committee encouraged further resources to be made available for the management of the site (World Heritage Committee, 2018). Due to the war, resources have become even more limited and no staff changes have taken place within the property (State Party of Sudan, 2024). The lack of a revised IMP and scare resources limit development and implementation of many management tasks within the property (e.g. routine monitoring in Dongonab Bay and on Mukkawar Island (State Party of Sudan, 2022) and the development of a code of conduct for diving operations (State Party of Sudan 2024)).
The 2017-2021 integrated Management Plan for the site provided a good framework for the management of the site. Although this has expired, many of the aims are still being pursued, although actions have been negatively affected by the war. Capacity and resource needs are not currently met. So far, human impact, including that from the communities situated within the buffer zone is relatively low. There is private ownership of land within the buffer zone but this is strictly controlled through the legal framework controlling the area. The laws defining and affecting the property provide for a complementary and generally harmonized suite of protection including to some degree instruments for co-management of the areas within the buffer zone of the property. Progress has been made in relation to the integration of stakeholders in the management in areas surrounding the property. Laws and regulations exist to control development within the buffer zone of the property and are consistent in their objectives to protect the key values of the site, however the increasing tourism market may bring challenges in this regard in the near future. As such, greater monitoring of any impact from these activities is needed and guidelines need to be developed to support sustainable ecotourism within the property.
An outstanding example of the northernmost tropical coral reef systems on earth
Low Concern
Trend
Stable
The site has remained relatively isolated from human interference and species have adjusted to the unique conditions found within the locality (World Heritage Committee, 2016). The site is in a relatively pristine state with limited impacts or threats and therefore likely to be stable. Previously established monitoring programmes (Mergner and Schumacher 1985, Reinicke et al. 2003, PERSGA 2003, AFP 2006, Cousteau Society 2013, Abdelhamid et al. 2024) have confirmed this trend but access issues have meant these programmes are difficult to maintain. More comprehensive and regular monitoring, as set out in the previous integrated management plan (Klaus, 2017), would help keep track of this trend with more certainty, especially considering the increasing threat from climate change.
An assessment survey of coral reefs in Dungonab Reserve conducted by the Faculty of Marine Sciences/Red Sea University and the Officers of D&S Heritage Property, during October 24-26, 2024 showed that some coral reefs are degraded as a result of coral destruction from dumping of anchors (Abdelhamid et al. 2024).
An assessment survey of coral reefs in Dungonab Reserve conducted by the Faculty of Marine Sciences/Red Sea University and the Officers of D&S Heritage Property, during October 24-26, 2024 showed that some coral reefs are degraded as a result of coral destruction from dumping of anchors (Abdelhamid et al. 2024).
Exceptional level of Biodiversity
Good
Trend
Stable
The property contains a high level of endemism and represents a complete and relatively intact marine ecosystem, in a significant biogeographic region of the Red Sea (World Heritage Committee, 2016). It is home to a rich reef ecosystem, containing over 300 fish species and includes some of the most expansive regional seagrass beds representing at least 9 of the 10 regional species. It remains home to significant populations of globally important and endangered species including sharks, cetaceans, and marine turtles (World Heritage Committee, 2016; Elhassan, 2018).
Impressive natural phenomena, formations and areas of great natural beauty
Good
Trend
Stable
Sanganeb is an isolated, atoll-shaped coral reef structure in the central Red Sea, surrounded by 800 m deep water, the atoll is a largely pristine marine ecosystem and provides some of the most impressive dive sites on earth resulting from the very high diversity of physiographic zones and reefs characterised by an extraordinary structural complexity (World Heritage Committee, 2016). The Dungonab Bay and Mukkawar Island areas of the property include highly diverse systems of coral reefs, mangroves, seagrass beds, beaches, intertidal areas, islands and islets. The clear visibility of the water, coral diversity, marine species and pristine habitats and colourful coral reef communities against a backdrop of the Red Sea Hills, rising over 1500 m, creates a scene of immense natural beauty (World Heritage Committee, 2016).
Assessment of the current state and trend of World Heritage values
Stable
The Sanganeb Marine National Park and Dungonab Bay – Mukkawar Island Marine National Park World Heritage site, set within the wider Sudanese Red Sea Coast, continues to exhibit high levels of endemism in marine fish and invertebrate species. A number of ecological and socio-economic characteristics of the area mean that the property is of national, regional and international importance for biodiversity conservation, reef resilience studies, interconnectivity, and for sustainable use of living marine resources. The relative isolation and low number of visitors to the site has aided its conservation and the near pristine status of its world heritage values. While the current state and trend of the property is good, the lack of an integrated management plan for the site and challenges associated with the current war, raise concern about the future trend in the state of the property.
Additional information
Importance for research,
Contribution to education,
Collection of genetic material
The site provides an outstanding opportunity for research and education and awareness for the local, national and international communities, about regional biodiversity. It also provides an important site for research as a prime example of a deep water offshore coral reef, providing an outstanding opportunity for comparative studies with similar systems in other regions including the Indian and Pacific Oceans. It also provides a place to understand the interactions of biota with the environment in an almost pristine system.
Fishing areas and conservation of fish stocks
Hosting at least 361 fish species with numerous endemic and rare species the property provides important nurseries and spawning grounds for key species.
History and tradition,
Cultural identity and sense of belonging
The property is home to a number of local communities, many of which have inhabited the area for many generations. These communities were present prior to the designation of the National Park and World Heritage Property and continue to undertake a relatively traditional way of life with many of them reliant on artisanal fisheries supported by the property.
Outdoor recreation and tourism,
Natural beauty and scenery
The site offers tourism activities which are significant to local, regional and international communities. Tourism is increasing in the area with local and regional tourists contributing to this increase and provides an opportunity for recreation and time in nature.
Coastal protection
The complex reef systems contained with the property, mirroring the Red Sea Coast of Sudan provide protection from extreme weather conditions and protect the fragile coast line from the impacts of such events.
The benefits from the SMNP/DMNP are largely in the conservation value of the ecosystem, including the relatively pristine reef systems and the unique biodiversity found within the site. The reefs and other associated marine habitats provide a productive environment for a number of species of global conservation concern, as well as in providing food to local communities, and protection of local infrastructure and populations from extreme weather events, the frequency of which may increase under climate change. There are also economic benefits in terms of job creation and tourism.
| № | Organization | Brief description of Active Projects | Website |
|---|---|---|---|
| 1 | University of the Red Sea | Various projects monitoring endangered species and conducting species surveys. | |
| 2 | Shark Conservation Fund (SCF), Igbal Elhassan, Jesse Cochran and Ryan Charles | The Important Shark and Ray Areas (ISRA) project supported by the Shark Conservation Fund (SCF), held two workshops in 2023 focused on the Mediterranean and Black Seas and Western Indian Ocean (https://www.iucnssg.org). During the workshop, the proposal (written by Igbal Elhassan, Jesse Cochran and Ryan Charles) to designate Dongunab Bay as an Important Area for Reef Manta Rays (Alfred manta) was accepted. | |
| 3 | Fisheries Research Centre/ Red Sea State and others, funding from World Bank Group | The project is currently implemented in PERSGA countries (Djibouti, Egypt, Jordan, Saudi Arabia, Somalia, Sudan, and Yemen). The project aims to promote collaboration and coordination among PERSGA countries, Eliminate IUU Fishing, reduce by catch, and protect Spawning Aggregations and Establish national and regional database. Status assessment report for five themes (legal, shore facility, spawning aggregation, stakeholders ND vessel), was carried out in February-March 2024 through survey along Sudan Red Sea Coast including Sudan world heritage site (Dongonab and Mohamed Quoll). | |
| 4 | PERSGA Individual National Consultancy | PERSGA Individual National Consultancy, is tasked with assisting in the assessment, updating, development, and support of the implementation of National Action Plans for the conservation of sharks, marine turtles, seabirds, and marine mammals affected by fishing activities in PERSGA Member State under the Sustainable Fishery Development Project in the Red Sea and Gulf of Aden (SFISH). The Proposed National Action Plans for sharks, marine turtles, marine mammals and sea birds have been developed. These plans include clearly defined goals, objectives, and indicators to guide conservation and management efforts. The Dongonab Bay area has been specifically addressed within the plans due to its ecological importance. |
References
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| 1 |
Abdelhamid, S., Reinicke, G.B., Klaus, R., Hohn, J., Saad, O.S. and Grenzdorffer, G. (2024). Red Sea coral reef monitoring site in Sudan after 39 years reveals stagnant reef growth, continuity and change. Diversity, 16, 379. https://doi.org/10.3390/d16070379
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| 2 |
Adam, B.E.K.A. (2013). Current Status and Distribution of Dugongs (Dugong dugon) in Sudan. Presentation and Abstract. RIHN 8th International Symposium “Risk Societies, Edge Environments: Ecosystems and Livelihoods in the Balance” October 23 - 25, 2013 Research Institute for Humanity and Nature. http://www.chikyu.ac.jp/rihn_e/events/2013/131023-25abstrac…
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| 13 |
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| 14 |
Kessel, S.T., Elamin, N.A., Yurkowski, D.J., Chekchak, T., Walter, R.P., Klaus, R., Hill, G. and Hussey, N.E. (2017). Conservation of reef manta rays (Manta alfredi) in a UNESCO World Heritage Site: Large-scale island development or sustainable tourism?. PloS one, 12(10), p.e0185419.
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| 15 |
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| 16 |
Klaus, R. (2018) Updating the Map for the Sanganeb Marine National Park and Dungonab Bay - Mukkawar Island Marine National Park UNESCO World Heritage Site. Report to Arab Regional Centre for World Heritage (ARC-WH) under the auspices of UNESCO 62p.
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| 18 |
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| 19 |
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| 23 |
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| 25 |
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