Ibiza, biodiversité et culture
Country
Spain
Inscribed in
1999
Criteria
(ii)
(iii)
(iv)
(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.
Ibiza offre un excellent exemple d'interaction entre les écosystèmes marins et côtiers. Les prairies denses de posidonies (herbe des fonds marins), espèce endémique que l'on trouve uniquement dans le bassin méditerranéen, contiennent et entretiennent une vie marine diverse. Ibiza conserve des témoignages considérables de sa longue histoire. Les sites archéologiques de Sa Caleta (habitat) et de Puig des Molins (nécropole) témoignent de l'importance du rôle joué par l'île dans l'économie méditerranéenne de la protohistoire et, tout particulièrement, au cours de la période phénicienne-carthaginoise. La ville haute fortifiée (Alta Vila) est un exemple exceptionnel d'architecture militaire de la Renaissance. Elle a eu une profonde influence sur le développement des fortifications dans les établissements espagnols du Nouveau Monde. © UNESCO
Summary
2025 Conservation Outlook
Finalised on
11 oct 2025
Significant concern
Current state and trend of VALUES
High Concern
Overall THREATS
Overall PROTECTION and MANAGEMENT
Full assessment
Description of values
Exceptionally dense and well-preserved Posidonia seagrass meadows
Criterion
(x)
Exceptionally dense and well-preserved Posidonia seagrass meadows in coastal waters between Ibiza and Formentera (IUCN, 1999; SoOUV, 2023) provide important spawning and nursery habitats for Mediterranean fauna (Boudouresque, 2004), including many endemic, threatened and economically important species (Reñones et al., 1995). Posidonia oceanica seagrass meadows are a priority habitat type under the Habitats Directive 92/43/EEC.
Influence of Posidonia on the evolution of coastal and marine ecosystems
Criterion
(ix)
The evolution of Ibiza's shoreline is one of the best examples of the influence of Posidonia on the interaction of coastal and marine ecosystems (IUCN, 1999; Ballesteros & Cebrián, 2004; UNEP/WCMC, 2011), and Posidonia protects sandy beaches (Chessa et al., 2000). Las Salinas de Ibiza y Formentera, as well as the islands of Penjats, Espardell and Espalmador, include important coastal lagoon and wetland ecosystems as well as halophyte communities (UNEP-WCMC, 2011; SoOUV, 2023). Clones of Posidonia between Ibiza and Formentera are estimated to be hundreds to thousands of years old (Arnaud-Haond et al., 2012).
Exceptionally well-preserved "Pillow Coral" Cladocora caespitosa communities
Criterion
(x)
The property is home to exceptionally well-preserved "Pillow Coral" Cladocora caespitosa communities (Kersting et al., 2017), supporting 220 species, the highest record for a marine community in the Mediterranean basin (IUCN, 1999; SoOUV, 2023). Cladocora caespitosa reefs are a priority habitat type under the Habitats Directive 92/43/EEC.
Exceptional marine biodiversity
Criterion
(x)
The Posidonia seagrass meadows and Pillow Coral habitats support a diverse fauna of invertebrates and fish (36 species in 15 families), and may be visited by Mediterranean Monk Seal Monachus monachus (CR), Loggerhead Turtle Caretta caretta (VU) and Bottlenose Dolphin Tursiops truncatus (LC), all of which are considered as priority species under the Habitats Directive. A noteworthy marine invertebrate is the colonial sea squirt Ecteinascidia turbinata, which produces a chemical valuable in the treatment of cancer (UNEP-WCMC, 2011; SoOUV, 2023).
Endemic and threatened terrestrial flora
Criterion
(x)
The coastal and terrestrial parts of the property house at least 11 endemic plants, including rare and vulnerable species (IUCN, 1999; SoOUV, 2023). The area is part of a global Centre of Plant Diversity (UNEP-WCMC, 2011).
Endemic and threatened terrestrial fauna
Criterion
(x)
The property supports 205 species of birds (including 171 migratory species), 5 species of mammals, 11 of terrestrial reptiles, and at least 56 species of invertebrates (UNEP/WCMC, 2011). The salt-pans of Ibiza and Formentera and Freus Isles are an internationally recognized Important Bird Area, particularly because of its waterfowl. This includes the Balearic Shearwater Puffinus mauretanicus (CR) and Audouin's Gull Larus audouinii (VU) (BirdLife International, 2025). Seven species of ducks frequently winter there, including the near-threatened Ferrugineous Duck Aythya nyroca (UNEP-WCMC, 2011). Akis bremeri, an endemic tenebrionid beetle, is restricted to the dune systems of Formentera within the area (Viñolas, 2011). Furthermore, this area has historically been a zone where Pinna nobilis has been present, now in dangerous decline (Sobrado and Sáez, 2024).
Assessment information
The natural values of the site remain under very high threat from excessive mass tourism, including a high density of recreational boats and yachts visiting the site and anchoring on the sensitive Posidonia meadows illegally, ship and ferry traffic, and high visitation pressure. Increasing population pressure includes pollution (untreated effluents and plastics) from Ibiza City and nearby urban areas. Invasive alien species, including cats, rats, snakes and marine algae present major threats to a highly threatened fauna. Rising temperatures caused by climate change have already had demonstrated impact on a number of values, and may exacerbate other threatening processes such as invasive algae.
Recreation & Tourism Areas
(Excessive boat traffic)
Inside site
, Throughout(>50%)
Outside site
The oceanic Posidonia meadows are protected by the Ses Salines Natural Park, however the significant maritime traffic in the area, especially in summer, presents the main threat for the natural component of the World Heritage site. The area between Ibiza and Formentera, known as Es Freus, has high boat traffic. In addition, in summer, there is a strong presence of pleasure boats that anchor in the area. Although buoys have been installed to allow anchoring without damaging the meadows, the small number of buoys and the fact that they do not allow lengths greater than 35 m, which are very common today, does not solve the problem (Ramón-Cardona et al. 2021). Satellite imagery has shown that ships continue to anchor on the Posidonia despite this being prohibited (Ferrer, 2024). Ses Illetes, the area near the port of La Savina, and the island of S’Espalmador are the most problematic areas (Ramón-Cardona et al., 2021).
In 2021 the Balearic Environment Commission called on the State to “regulate and reduce” the berthing of cruise ships in the port of Ibiza and the traffic of regular boats between the Pitiusas in order to ensure the protection of the Natural Park of Ses Salines. The environmental body of the Autonomous Community has reported in favour of the Plan de Ordenación del Espacio Marítimo of the Levantine-Balearic coast that the central government is processing as long as it fulfils this, along with other conditions. In its report, which is not binding, the Balearic Environment Commission considers that, given the risk of fuel spills and other damage caused to the environment, actions should be coordinated between the State, the Autonomous Community and the local administrations of the island “aimed at reducing maritime frequencies between the Pitiusas”, a demand that the Consell de Formentera has also made to the Balearic Govern. Another request is that the central government “reduces” the berthing of regular line boats, shipping companies and cruise ships in the ports of Ibiza and La Savina. Thus, it is proposed that the Maritime Space Management Plan should organise and regulate the relevant activities and uses of the port areas according to “the potential of each area, as well as its load capacity and its environmental status”. With this, it is proposed to limit the number of cruise ships that can be found in a destination, their size or other measures to “minimise the impact of this activity” (Martos, 2021).
The environmental body of the Autonomous Community warns that, in the case of the Pitiusas, "the suitability of this maritime space in relation to maritime transport and activities related to leisure and boat tourism has already been exceeded". In fact, the plan being processed by the State points out that the demarcation of the Levantine-Balearic area shows "high densities of ships at several points", including "the route that connects Ibiza with Formentera". In addition, the data used are from 2016, when the Balearic Islands warned that since that year, at least until 2019, before the health crisis, "the annual evolution of the activity [of maritime traffic between the Pitiusas] has increased" (Martos, 2021).
In 2024 an image from the Sentinel satellite of the Copernicus program, recorded that between the ships that are in full navigation and those that remain anchored off the coast (small white dots can be seen, especially in front of ses Illetes de Formentera, s’Espalmador and ses Salines de Eivissa), the figure is around 400 boats. Although most of the anchored vessels appear to be on sandy ground, it is also apparent that many others do so on Posidonia (especially visible in ses Salines de Eivissa), despite this being totally prohibited and subject to heavy fines. In fact, these uncontrolled anchorages on the seagrass meadows are one of the main causes of their progressive disappearance. According to a study made public in December 2018 and prepared by the Natural Park’s management team, es Freus supports per year an average of 1,960 boat trips per day during the summer. Although this is the summer average, there are peaks of up to 2,494 transits (Ferrer, 2024).
That means that during that time of year there are no less than 82 to 104 ships per hour traveling through the strait. Of all these boats, 10% are regular traffic ferries, while the rest are recreational vessels of all sizes. Of these, only 8% were sailing vessels, while the rest were motorboats, according to the report, which analysed the traffic recorded that year and the previous year (Ferrer, 2024).
Turbulence and turbidity from ferries and boats negatively affects Posidonia. Underwater noise is also quite significant and proved through measurements to have negative impacts on the seagrass ecosystem. The extent of the cumulative impacts on the values of the site is being analysed. Beginning in 2018, five coastal boats patrol the Natural Park, informing the people on boats and yachts of the rules, including the interdiction to anchor on seagrass and dropping waste; however, they do not have the power to fine. Despite this, the total number of boats and yachts sailing through or visiting the site has not declined, although this action has resulted in a substantial reduction of the negative impacts these recreational activities have had in the site prior to 2018. However, this impact has been displaced to surrounding areas, including Talamanca (IUCN Consultation, 2020).
In 2021 the Balearic Environment Commission called on the State to “regulate and reduce” the berthing of cruise ships in the port of Ibiza and the traffic of regular boats between the Pitiusas in order to ensure the protection of the Natural Park of Ses Salines. The environmental body of the Autonomous Community has reported in favour of the Plan de Ordenación del Espacio Marítimo of the Levantine-Balearic coast that the central government is processing as long as it fulfils this, along with other conditions. In its report, which is not binding, the Balearic Environment Commission considers that, given the risk of fuel spills and other damage caused to the environment, actions should be coordinated between the State, the Autonomous Community and the local administrations of the island “aimed at reducing maritime frequencies between the Pitiusas”, a demand that the Consell de Formentera has also made to the Balearic Govern. Another request is that the central government “reduces” the berthing of regular line boats, shipping companies and cruise ships in the ports of Ibiza and La Savina. Thus, it is proposed that the Maritime Space Management Plan should organise and regulate the relevant activities and uses of the port areas according to “the potential of each area, as well as its load capacity and its environmental status”. With this, it is proposed to limit the number of cruise ships that can be found in a destination, their size or other measures to “minimise the impact of this activity” (Martos, 2021).
The environmental body of the Autonomous Community warns that, in the case of the Pitiusas, "the suitability of this maritime space in relation to maritime transport and activities related to leisure and boat tourism has already been exceeded". In fact, the plan being processed by the State points out that the demarcation of the Levantine-Balearic area shows "high densities of ships at several points", including "the route that connects Ibiza with Formentera". In addition, the data used are from 2016, when the Balearic Islands warned that since that year, at least until 2019, before the health crisis, "the annual evolution of the activity [of maritime traffic between the Pitiusas] has increased" (Martos, 2021).
In 2024 an image from the Sentinel satellite of the Copernicus program, recorded that between the ships that are in full navigation and those that remain anchored off the coast (small white dots can be seen, especially in front of ses Illetes de Formentera, s’Espalmador and ses Salines de Eivissa), the figure is around 400 boats. Although most of the anchored vessels appear to be on sandy ground, it is also apparent that many others do so on Posidonia (especially visible in ses Salines de Eivissa), despite this being totally prohibited and subject to heavy fines. In fact, these uncontrolled anchorages on the seagrass meadows are one of the main causes of their progressive disappearance. According to a study made public in December 2018 and prepared by the Natural Park’s management team, es Freus supports per year an average of 1,960 boat trips per day during the summer. Although this is the summer average, there are peaks of up to 2,494 transits (Ferrer, 2024).
That means that during that time of year there are no less than 82 to 104 ships per hour traveling through the strait. Of all these boats, 10% are regular traffic ferries, while the rest are recreational vessels of all sizes. Of these, only 8% were sailing vessels, while the rest were motorboats, according to the report, which analysed the traffic recorded that year and the previous year (Ferrer, 2024).
Turbulence and turbidity from ferries and boats negatively affects Posidonia. Underwater noise is also quite significant and proved through measurements to have negative impacts on the seagrass ecosystem. The extent of the cumulative impacts on the values of the site is being analysed. Beginning in 2018, five coastal boats patrol the Natural Park, informing the people on boats and yachts of the rules, including the interdiction to anchor on seagrass and dropping waste; however, they do not have the power to fine. Despite this, the total number of boats and yachts sailing through or visiting the site has not declined, although this action has resulted in a substantial reduction of the negative impacts these recreational activities have had in the site prior to 2018. However, this impact has been displaced to surrounding areas, including Talamanca (IUCN Consultation, 2020).
Invasive / Other Problematic Species, Genes & Pathogens, Invasive Non-Native/ Alien Species
(Invasive algae)
Invasive/problematic species
Caulerpa racemosa
Lophocladia lallemandii
Acrothamnion preissii
Womersleyella setacea
Other invasive species names
Batophora occindentalis
Inside site
, Extent of threat not known
Outside site
The most invasive macrophytes in the property are green algae Caulerpa racemosa, and red algae Lophocladia lallemandii, Acrothamnion preissii and Womersleyella setacea (Piazzi et al., 2001; Ballesteros and Cebrian, 2004; Cebrian and Ballesteros, 2010). Lophocladia lallemandii in particular has reportedly spread in past years, causing a direct negative impact on Posidonia oceanica habitats (Ballesteros et al., 2007). However, the impact of this species appears to have decreased, the reasons why are not known. Some experts think that it may be a transient effect (IUCN Consultation, 2020). A three year expansion of Batophora occindentalis has been observed in the coastal lagoon of Estany des Peix (Forteza et al., 2024).
Water-borne & other effluent Pollution
(Wastewater disposal)
Inside site
, Widespread(15-50%)
Outside site
Sewage input from recreational boats inside the area has been substantially reduced since 2018 in the site thanks to information by the coastal boat patrols. However, this has been displaced into the buffer zone and neighboring areas (IUCN Consultation, 2020). This impact has a cumulative effect with current eutrophication of coastal waters from urban wastewater and brine from desalination plants and climate change, enhancing phytoplankton growth, reducing water transparency and provoking macrophyte (including seagrass) decline (Sobrado et al., 2018).
Recreational Activities
(High tourist numbers)
Inside site
, Throughout(>50%)
Outside site
Although reduction in tourist numbers is recommended to reduce pressure on Posidonia meadows (Sobrado & Palomares, 2025), among many other impacts, it appears that tourism continues to increase, although figures for tourists solely visiting the property were not available. However, for Ibiza and Formentera, in 9 months 3.3 million tourists visited the islands in 2023, 242,407 more than the same period in 2022 (Makepeace, 2023). In 2024, the numbers appear to have even increased even more (TTW, 2025). The beaches of Ses Salines and Es Cavellet are among the most heavily used of Ibiza (IUCN Consultation, 2020). The dune, beach and coastal ecosystems are deteriorating both in the terrestrial part of Ibiza and that of Formentera due to excessive tourist use. Signs to prevent people from entering the dunes have been insufficient. In some places, e.g. Cavallet beach, these impacts are exacerbated by (illegal) parking of motor vehicles. In several places, such as Formentera, the trend of removing surface materials to create small land-art type of sculptures has become a problem (IUCN Consultation, 2020). The international popularity of Ibiza has created a "halo effect" that has intensified the commercialization of the protected area through media and promotional events. Examples include the advertisement of mass events (Periódico de Ibiza, 2024) and the execution of commercial activities without proper authorization, such as renting the area for private events (Cadena SER, 2025), and unauthorized filming of a music video for a major international artist (Diario de Ibiza, 2024).
Residential Areas, Recreation & Tourism Areas
(Tourism infrastructure)
Outside site
Marinas and other tourism infrastructure near the site (e.g. at Ibiza town) are adding to seagrass destruction, eutrophication and related disturbances. The urban plan of the Ibiza City municipality adopted in 1987 allowed for huge urban expansions, beyond water resources, despite that 85% of the municipal coast is already built (Murray, 2013). A new urban plan was approved in 2023 and should include significant growth reduction (Eivissa, 2023). However, the damage may already have been done, since the Balearic Islands as a whole have increased development in the first kilometre of coastline by 37.6%, mainly due to urban expansion and commercial activities related to tourism, with the consequent impacts on the environment (Vaquer-Sunyer et al., 2020).
The number of tourists and tourist accommodations has been increasing over time until 2018, with an increase of more than 16 million in 59 years. In 2019, it was slightly lower than the previous year, going from 16.56 million in 2018 to 16.44 million in 2019. This increase has been much more pronounced this century, as the number of tourists visiting the Balearic Islands has more than doubled. The number of legal tourist accommodations has continued to grow over time, reaching 607,522 in 2023. The number of tourist accommodations in holiday homes has increased since 2017, when it was legalized. By island, Formentera has the highest percentage, with 47% in 2021 and 2022; Ibiza has the lowest percentage, with 19.8% in 2022. The increase in both the number of tourist places and the number of tourists visiting the Balearic Islands has significant consequences for resource consumption and waste production (Vaquer-Sunyer et al. 2024).
The number of tourists and tourist accommodations has been increasing over time until 2018, with an increase of more than 16 million in 59 years. In 2019, it was slightly lower than the previous year, going from 16.56 million in 2018 to 16.44 million in 2019. This increase has been much more pronounced this century, as the number of tourists visiting the Balearic Islands has more than doubled. The number of legal tourist accommodations has continued to grow over time, reaching 607,522 in 2023. The number of tourist accommodations in holiday homes has increased since 2017, when it was legalized. By island, Formentera has the highest percentage, with 47% in 2021 and 2022; Ibiza has the lowest percentage, with 19.8% in 2022. The increase in both the number of tourist places and the number of tourists visiting the Balearic Islands has significant consequences for resource consumption and waste production (Vaquer-Sunyer et al. 2024).
Garbage & Solid Waste
(Plastic pollution)
Inside site
, Throughout(>50%)
Outside site
Plastic pollution is becoming increasingly documented as a high threat to marine biodiversity (Ruiz-Orejón, 2018; GEN-GOB, 2024a; Martinez et al., 2024). Additionally, ingestion of microplastics by species as the invasive Callinectes sapidus threaten potential predators of this species (Compa et al., 2023).
Changes in Physical & Chemical Regimes, Changes in Temperature Regimes, Changes in Precipitation & Hydrological Regime
(Climate change)
Inside site
, Throughout(>50%)
Outside site
Various effects of climate change on seagrass stands and ecosystems have already been documented (e.g. Marba and Duarte, 2010). Increased water temperature enhances the thermocline effect, increasing plankton density, reducing water transparency, creating cumulative impacts with water pollution to Posidonia seabeds, whilst favoring invasive alien macrophytes such as Caulerpa racemosa and Lophocladia lallemandii. The Oceanographic Centre of the Balears recently published a study showing that, if the current warming trend continues, the coastline of the islands would recede by 20 centimetres per year, meaning the loss of seven beaches in Ibiza and six in Formentera, while a good part of the rest would be reduced by half (Greenpeace, 2024). Another quantification of the future total water level and coastline retreat for 869 beaches across the Balearic Islands for the next decades as a function of greenhouse gases emission scenario shows that according to the most pessimistic scenario (RCP8.5) at the end of the century yields an averaged percentage of flooded area of 66% under mean conditions which increases up to 86% under extreme conditions. Moreover, 72 of the 869 beaches of the region would permanently disappear while 314 would be completely flooded during storm episodes (Agulles et al., 2021).
The increasing occurrence of Caretta caretta nesting in the area (GOIB, 2021), while perceived as a positive sign of ecological recovery, may generate new conservation challenges as potential increased management needs during the tourist season, and added pressure on dune systems.
The increasing occurrence of Caretta caretta nesting in the area (GOIB, 2021), while perceived as a positive sign of ecological recovery, may generate new conservation challenges as potential increased management needs during the tourist season, and added pressure on dune systems.
Invasive / Other Problematic Species, Genes & Pathogens, Invasive Non-Native/ Alien Species
(Invasive alien species (cats, rats, snakes, crabs, plants))
Invasive/problematic species
Zamenis scalaris
Felis catus
Rattus rattus
Carpobrotus edulis
Other invasive species names
Callinectes sapidus; Kalanchoe × houghtonii
Inside site
, Scattered(5-15%)
Outside site
Alien invasive ladder lnakes (Zamenis scalaris) threaten the Ibiza Wall Lizard Podarcis pityusensis (Montes et al., 2022; GEN-GOB, 2024b). There is an ongoing effort to trap invasive ladder snakes and prevent them for invading small islets (Picó et al., 2019; GOIB, 2025). Invasive feral cats and black rats threaten the Balearic Shearwater population breeding on Formentera (McMinn & Cooper, 2015). Invasive plant species are also present in the area, as Carpobrotus edulis and Kalanchoe × houghtonii (GOIB, 2021b; Serapio et al., 2023). The invasive blue crab, Callinectes sapidus, was also detected in the area in 2018 (Box et al., 2020).
Potential threats include the risk of shipping accidents and additional tourism and urban infrastructure in and around the site, as well as from potential gypsum exploration, related to oil and gas deposits.
Shipping Lanes
(Shipping accidents)
Inside site
, Throughout(>50%)
Outside site
There are reportedly several smaller ship accidents at and near the site each year, as a consequence of the intensive visitation by tourist boats and yachts. A notable larger accident was that of the MS Don Pedro in 2007 (Rössler et al., 2009). Although this accident happened outside the site and had reportedly no major effects on its integrity, it illustrates the high potential threat from shipping accidents to the marine and coastal natural values of the site.
Residential Areas, Recreation & Tourism Areas
(Additional infrastructure developments)
Inside site
, Extent of threat not known
Outside site
Proposed development of additional tourism infrastructure, including a new golf project near the site, has been cancelled. No new projects are currently known. However, the Ibiza City urban plan still allows for expansion. With an increasing local population as well as increasing numbers of tourists, the pressure on the property is set to increase (IUCN Consultation, 2020).
In 2022 the Governing Council approved a halt to urban growth of great importance throughout the territory of the Balearic Islands. As Diario de Mallorca and Diario de Ibiza advanced on October 22, municipalities will not be able to authorize new urbanizations if they have unbuilt urban land in their municipal area. The aim of this measure is to prevent the expansive growth of large villas on the outskirts when in urban centres there are unbuilt plots, land to develop or unrehabilitated buildings. It is a way of putting a stop to the expansive growth that the islands have experienced for decades. Likewise, if the municipality has an area equivalent to the proposed new growth in developable land, it cannot be developed either. Similarly, new urban growth may not be planned in flood risk prevention areas in order to avoid floods in the areas where people live. The only exception that the Government contemplates for urban growth is for public housing developments and public facilities. The regulation also promotes a whole series of measures aimed at saving water. The most powerful refers to the limitation of the construction of swimming pools on rural land, where only one pool per property will be allowed and with a maximum of 35 square meters throughout its extension (Adrover, 2022).
The measure was already approved in the urban planning decree 9/2020, but it left out some areas and the islands of Ibiza and Formentera. Now the scope of application will be for the entire Balearic territory without exception (Adrover, 2022).
In 2022 the Governing Council approved a halt to urban growth of great importance throughout the territory of the Balearic Islands. As Diario de Mallorca and Diario de Ibiza advanced on October 22, municipalities will not be able to authorize new urbanizations if they have unbuilt urban land in their municipal area. The aim of this measure is to prevent the expansive growth of large villas on the outskirts when in urban centres there are unbuilt plots, land to develop or unrehabilitated buildings. It is a way of putting a stop to the expansive growth that the islands have experienced for decades. Likewise, if the municipality has an area equivalent to the proposed new growth in developable land, it cannot be developed either. Similarly, new urban growth may not be planned in flood risk prevention areas in order to avoid floods in the areas where people live. The only exception that the Government contemplates for urban growth is for public housing developments and public facilities. The regulation also promotes a whole series of measures aimed at saving water. The most powerful refers to the limitation of the construction of swimming pools on rural land, where only one pool per property will be allowed and with a maximum of 35 square meters throughout its extension (Adrover, 2022).
The measure was already approved in the urban planning decree 9/2020, but it left out some areas and the islands of Ibiza and Formentera. Now the scope of application will be for the entire Balearic territory without exception (Adrover, 2022).
Oil & Gas exploration/development
(Oil and gas exploration)
Outside site
Possible implementation of COST Project Medsalt-2 devoted to the exploration of deep layers for gypsum exploration, and potentially related to oil and gas deposits, would have negative impacts if developed. The impacts could affect for example the Balearic shearwater (Puffinus mauritanicus), Bottlenose dolphin (Tursiops truncates), Loggerhead turtle (Caretta caretta) and many other species, as well as having an impact on the integrity of seagrass meadows (IUCN Consultation, 2020).
Involvement of stakeholders and rightsholders, including indigenous peoples and local communities, in decision-making processes
There is a “participation programme” of the Nature Park which constitutes the natural part of the World Heritage site. However, it is unclear to what extent the current stakeholder participation setup contributes to the effective conservation of the site and how effective it is in representing the interests of all stakeholders. Most people do not know that there is a natural part of the World Heritage site that almost coincides with the Natural Park. Economic benefits related to the intensive tourist use of the terrestrial (especially sandy beaches) and marine parts of the site are very significant for local municipalities, tourist companies and operators involved in tourist activities (IUCN Consultation, 2020).
Legal framework
The natural part of the property has more than 12 different local, regional, national and international laws and legal provisions (Rössler et al., 2009; Del Valle et al., 2017), with the main one being the Law 17/2001 of 19 December 2001 on the Environmental Protection of Ses Salines as a Natural Park. The Natural Resources Management Plan for Ses Salines de Ibiza and Formentera (BOIB no. 80, of 4 July 2002) was approved by the Governing Council, and Decree 132/2005, of 23 December, approved the Master Plan for the Use and Management of the Ses Salines Natural Park in Ibiza and Formentera (BOIB no. 196, of 31 December 2005). In 2018, the Balearic Government issued Decree 25/2018 to protect Posidonia oceanica meadows of the archipelago, which has had a positive impact in the site (IUCN Consultation, 2020).
Governance arrangements
Since 2007 the responsibility for managing the natural components of the property has been shared between the Ibiza and Formentera Councils, without a clear identification of the respective responsibilities and roles including resources allocation, monitoring and follow-up (Rössler et al., 2009). It is not clear how the autonomous Balearic government interacts with the municipal governments as well as with the State government of Spain.
Integration into local, regional and national planning systems (including sea/landscape connectivity)
Important regional planning frameworks relevant to the management of the site are the Infrastructure Master Plan and the Insular Regional Plan. These plans have so far not been effective in preventing such key threats to the values of the site, such as water pollution from sewage, nearby tourism developments and intensive visitation. The Government of the Balearic Islands has not yet approved its own regional Biodiversity Conservation Strategy, as is required by the Spanish legislation (IUCN Consultation, 2020). Therefore, the integration of conservation objectives into regional and national planning systems remains of concern.
Boundaries
The boundaries and buffer zone of the natural part of the site were considered adequate at the time of inscription (IUCN, 1999) but later high quality seagrass meadows were discovered outside, including an outstanding bed 7 km long with an estimated (clonal) age of c. 100,000 years (Arnaud-Haond et al., 2012). The boundaries of the World heritage site are not visible, and those of the Natural Park and Nature Reserves areas have never been clearly marked on site (e.g. by buoys in the marine part), so are not understood by all local stakeholders (Rössler et al., 2009), not to mention tourists. There is also a certain mismatch between the boundaries of the World Heritage site and its buffer zone and the Nature Park and Nature Reserve boundaries. Although it was recommended to extend the World Heritage site to include the outstanding Posidonia reef at Talamanca, as well as other Posidonia areas and the Archipelago de Cabrera National Park, and the unique wetland of Les Feixes del Prat de ses Monges (Rössler et al., 2009; World Heritage Committee, 2011), no action has been undertaken in this regard. The current boundaries are not effective in including some of the most valuable areas and excluding key threats from the site, and are also not easily identified.
Overlapping international designations
Ramsar site covers 1,640 ha, and includes coastal wetlands surrounding the islands and salt pans. It is also an EU Natura 2000 site. The extent to which the different designations interact in their management is unclear.
Implementation of World Heritage Committee decisions and recommendations
The World Heritage Committee (WHC) paid serious attention to the property when a major construction project (the extension of the port facility) was proposed with potential impact on the property. A request for a joint monitoring mission (done) and delay of the port extension until after the mission (not done) was made (WHC, 2009). WHC (2010) urged the State Party to immediately inform the World Heritage Centre of any unexpected or adverse impacts during the dredging and to undertake and report on appropriate mitigation and monitoring measures, and to provide a report on the state of conservation of the property (done). WHC (2011) requested more monitoring of dredged materials and mitigation measures for any negative impacts of the port construction, as well as management measures for the high number of recreational boats in the property, monitoring of threats including invasive species and discharge of insufficiently treated waste water, and a draft Management Plan. These requests were responded to (Ibiza Council, 2014). A suggestion to consider an extension of the property to include the Archipelago de Cabrera National Park and some other areas of high importance (see Rössler et al., 2009) has not been followed up. Since 2011 there have been no further decisions from the WHC concerning the state of conservation of the property.
Climate action
No information from the park management. The Mediterranean Institute for Advanced Studies (IMEDEA), with other partners, are sequencing the Posidonia genome to identify plants which are better adapted to warmer water temperatures (IMEDEA, n.d.) Furthermore some organisations like the Ibiza Preservation Society are carrying out various restoration and ecosystem services projects.
Management plan and overall management system
A Management Plan for the Natural Park, which covers the WH Site, was approved in 2005. In 2014 the entire site was included in the European Natura 2000 Network as a Special Area of Conservation (under the Habitats Directive) and a Special Protection Area (under the Birds Directive). The corresponding Management Plan was approved by the Balearic Government in 2015 (Decree 48/2015, BOIB no. 131). A Management Plan for the Natura 2000 property was published in 2020 (GOIB, 2020). Annual reports on activities in the Natural Park have not been written at least since 2020. In August 2024, the Balearic Government initiated the long-overdue revision of the Park’s management instruments, including the PRUG and PORN, which should have been updated nearly a decade ago. The process includes a public consultation phase and aims to address current conservation challenges such as invasive species and land use conflicts. Biosecurity protocols against invasive species, especially for islets, are largely lacking (IUCN Consultation, 2025).
Law enforcement
There is a great difficulty in applying the provisions of existing regulations due to the numerous national, regional and local agencies with different responsibilities, insufficient cooperation, and lack of surveillance staff, financial and other resources. Apart from controlling recreational boats and yachts from anchoring on Posidonia, which has substantially improved since 2018 (IUCN Consultation, 2020). However, the resolution procedures of the inspection acts by the Regional Environmental Department Legal Service are very slow, resulting is low enforcement of legal provisions (IUCN Consultation, 2020).
Sustainable finance
The property is financed half by the State and half by the municipality, and that finance is sufficient both inside and outside the property and is increasing (State Party of Spain, 2024). No public information on budgets is available, although it is reported that the Natural Park has suffered a structural lack of resources and staff since it was established, and that both budget and staff are clearly insufficient to deal with the complex management needs (IUCN Consultation, 2020). The government created in 2024 a Natural Heritage Fund.
Staff capacity, training and development
No official information on staff numbers, training or development programmes is available, although it is reported that only three staff (with two more during the summer season) are permanently devoted to the Park, the rest being shared with other protected areas (IUCN Consultation, 2020). The State Party reports that human resources for the property are positive (State Party of Spain, 2024).
Education and interpretation programmes
The Ses Salines Natural Park carries out an Annual Implementation Plan with numerous educational activities aimed at improving public and recreational use to encourage both locals and foreigners to visit the park (Ibiza Council, 2014). Two interpretation centres on Ibiza and Formentera are pictured on the park website. There is no information on the number of staff engaged in education and interpretation programmes for the property.
Tourism and visitation management
The site is mainly used for mass tourism, both marine and terrestrial. Although there has been a reduction of anchoring by recreational boats and yachts in Posidonia beds since 2018, the number of ferries and recreational boats and yachts crossing or visiting the site has not decreased (IUCN Consultation, 2020). After a record number of visitors from cruise ships in 2023 (Ibiza Preservation, 2024), a decision to limit cruise ships to two a day was undertaken in 2024 (Neath, 2024). There is serious concern that the ever-increasing tourism pressure in coastal areas with fragile ecosystems, like dunes, is unsustainable. An analysis of the socio-environmental carrying capacity of the island of Ibiza (Del Valle et al., 2017) and a tourist strategy for 2021-2023 (Braintrust, 2021) exists, although is not particularly focused on nature conservation.
Sustainable use
Apart from the main use of the property for tourism which includes boating and diving, limited fishing is allowed under license for artisanal and recreational fishing. Trawling, purse seine, surface longline, spearfishing and fishing competitions are prohibited in the property (GOIB, 2020).
Monitoring
Monitoring data is difficult to find. Some monitoring of threatened birds and water quality can be found but it is not associated with the property: an integrated monitoring system addressing key threats to the integrity of the OUV of the site is still missing (WHC, 2011). Monitoring of Posidonia is undertaken by IMEDEA, Marilles Foundation, and others (IUCN Consultation, 2020), but is not just directed to the property. Monitoring is poorly outlined in the Management Plan (GOIB, 2020). Monitoring of threatened flora has been undertaken by the Species Protection Services, including the area (2021-2023 reports on demand to the GOIB).
Research
Research is undertaken by many institutes including the Mediterranean Institute for Advanced Studies (IMEDEA), the Center for Advanced Studies in Blanes (CEAB), and many universities including Madrid, Barcelona and Valencia. The NGO GEN-GOB has been involved in monitoring and assessing pressures and impacts in the field and Ibiza Preservation Foundation is mapping seagrass. Foundation Marilles is undertaking numerous social and ecological studies in the Balearic Islands. Research areas include seagrass ecology, invasive alien macrophytes, water pollution, ornithology, and tourism pressures in both the marine and terrestrial parts. However, the Park has not been able to promote key research needed to monitor impacts, nor management-based research (IUCN Consultation, 2020).
Effectiveness of management system and governance in addressing threats outside the site
Economic interests, especially the importance of tourism to the local and national economy, indicate that managing threats from outside the site, even with a fairly recent Management Plan (GOIB, 2020), will be difficult at best. A catastrophic event such as an oil spill would greatly affect biodiversity and tourism values at the same time, thus would have a better chance of being managed at a high level due to shared interests (Vercher, 2022).
Effectiveness of management system and governance in addressing threats inside the site
The management effectiveness for the natural part of the site has never been formally assessed, and few positive conservation actions, apart from increasing awareness and building permanent moorings with a reservation system to stop recreational vessels from anchoring on seagrass beds (ATP, 2012; Technoambiente, 2017) are available. However, negative impacts related to mass tourism, poor management, lack of signposting, and insufficient administrative cooperation, funding, technical staff, rangers, and other key resources indicate poor management effectiveness (IUCN Consultation, 2020).
The site is under extremely high pressure, mainly from poorly controlled mass tourism, both in the marine and terrestrial parts. The threats have been growing during the last years and several cumulative impacts have crossed or are approaching a critical point. At the same time, management (in particular the effectiveness of the management system, identification of borders and enforcement of regulations within the site, visitor management and monitoring of key threats) has so far been insufficient. Despite significant improvement, protection and management has not been sufficiently effective to address the many pressures on the site’s values. The enormous conservation challenges that this property is facing since inscription, with the addition of some new ones, mean that protection and management of the property needs increased efforts if the values are to be conserved.
Exceptionally dense and well-preserved Posidonia seagrass meadows
High Concern
Trend
Deteriorating
Studies of Posidonia oceanica seagrass meadows in the Balearic Islands demonstrate a general trend of decline over the past 20 years, and water quality, affecting seagrass, has also declined (Álvarez et al., 2015). Quantitative information about the status and trends of Ibiza seagrass habitat is not available; however, the overall status of seagrass meadows in the Mediterranean has been assessed as poor (Losciale et al., 2022). While work to protect Posidonia within the property has been undertaken since 2018, in particular by preventing boats from anchoring on seagrass, the severity of previous negative impacts will last for decades, given the slow rate of regeneration of Posidonia. Moreover, since other negative impacts (e.g. waste and pollution) are either continuing or have increased, Posidonia will continue to decline, at least for some more years even after the negative impacts have been eliminated (IUCN Consultation, 2020). Climate change and invasive species of algae also continue to impact Posidonia populations (Álvarez et al., 2015).
In 2024, the results of the latest analysis by GEN-GOB, were announced reporting that the Posidonia oceanica meadows in Talamanca Bay are continuing to decline. The results confirm that the seagrass in Talamanca shows no sign of recovery. More than 50% of the Posidonia oceanica meadows in this area are already dead. The main cause of the decline has been linked to the high level of boat traffic in the area and illegal anchoring (IbizaPreservation, 2024).
Overall however, the total area occupied by Posidonia oceanica meadows in the Balearic Sea remains high. According to the cartography of the Posidonia Atlas of the Ministry of Environment and Territory of the Balearic Government, the total area is approximately 553.7 km2 for monospecific meadows, and 591.5 km2 for all habitats where it is present (meadows mixed with photophilous or hemi-sciophilous algae, reefs, with dead rhizomes, on stones with sand, or with other phanerogams). Posidonia oceanica meadows are widely distributed in the Balearic Islands, where they occupy 553.7 km2 in the form of monospecific meadows and 591.5 km2 when all habitats where they are present are considered (Vaquer-Sunyer et al., 2024).
In 2024, the results of the latest analysis by GEN-GOB, were announced reporting that the Posidonia oceanica meadows in Talamanca Bay are continuing to decline. The results confirm that the seagrass in Talamanca shows no sign of recovery. More than 50% of the Posidonia oceanica meadows in this area are already dead. The main cause of the decline has been linked to the high level of boat traffic in the area and illegal anchoring (IbizaPreservation, 2024).
Overall however, the total area occupied by Posidonia oceanica meadows in the Balearic Sea remains high. According to the cartography of the Posidonia Atlas of the Ministry of Environment and Territory of the Balearic Government, the total area is approximately 553.7 km2 for monospecific meadows, and 591.5 km2 for all habitats where it is present (meadows mixed with photophilous or hemi-sciophilous algae, reefs, with dead rhizomes, on stones with sand, or with other phanerogams). Posidonia oceanica meadows are widely distributed in the Balearic Islands, where they occupy 553.7 km2 in the form of monospecific meadows and 591.5 km2 when all habitats where they are present are considered (Vaquer-Sunyer et al., 2024).
Influence of Posidonia on the evolution of coastal and marine ecosystems
High Concern
Trend
Deteriorating
As above, despite conservation measures, Posidonia meadows have rapidly deteriorated over the last 20 years (IUCN Consultation, 2020) and even if the threats are removed, will take much time to recover.
Exceptionally well-preserved "Pillow Coral" Cladocora caespitosa communities
High Concern
Trend
Deteriorating
Climate change causing warming seas have had a demonstrated impact of coral bleaching on Cladocora caespitosa in the Mediterranean (Jimenez et al., 2014), although impacts vary.
Climate change is causing an increase in the frequency and intensity of marine heatwaves (MHWs) and mass mortality events (MMEs) of marine organisms are one of their main ecological impacts. Garrabou et al. (2022) show that during the 2015–2019 period, the Mediterranean Sea has experienced exceptional thermal conditions resulting in the onset of five consecutive years of widespread MMEs across the basin. These MMEs affected thousands of kilometres of coastline from the surface to 45 m, across a range of marine habitats and taxa (50 taxa across 8 phyla). Significant relationships were found between the incidence of MMEs and the heat exposure associated with MHWs observed both at the surface and across depths. Negative effects on Cladocora caespitosa were noted. The findings reveal that the Mediterranean Sea is experiencing an acceleration of the ecological impacts of MHWs which poses an unprecedented threat to its ecosystems' health and functioning (Garrabou et al., 2022).
In the last two years—2022 and 2023—more than half of the days in the Balearic Sea were marine heatwaves. Specifically, in 2023, 214 marine heatwave days were recorded, while in 2022, there were 202. In fact, the number of marine heatwave days has increased over time at a rate of 2.7 days per year. The average intensity of marine heatwaves in 2023 was 2.03°C higher than the average for the reference period 1982–2015. The average intensity has increased at a rate of 0.01°C per year over the period 1982–2023. The maximum intensity of marine heatwaves in 2023 was 4.31°C above the average for the 1982-2015 reference period. It has been increasing over time at a rate of 0.05°C/year. Marine heatwaves have multiple effects on marine organisms, habitats, and ecosystem functioning. Mass mortality events of corals, gorgonians, and sponges have been observed due to the effects of heatwaves. They have also been associated with mass blooms of Posidonia oceanica and pseudoviviparity (Vaquer-Sunyer et al., 2024).
According to the Balearic Sea Report (IMB) dozens of coral and gorgonian species (from 1 m to > 1,000 m depth) are in vulnerable status, but not all of them are protected by regulations. Cladocora caespitosa shows the highest coverage in Formentera, and in Menorca it has a wide presence around the island (Vaquer-Sunyer et al., 2024). At shallower depths (<40 m), C. caespitosa stands out as abundant on all the islands. This species cohabits with algae and is the only one that forms reefs in the Mediterranean. Colonies have been observed in many areas of Menorca, some with significant populations (maximum coverage of 12% in Fornells and 10% in Ciutadella and Cala Pedrera) and Formentera (maximum coverage of 33.7% in Punta Pedrera-Es Banc and 20% in S'Espardelló), which are of great importance in the Mediterranean. It is worth noting that on Formentera, on the islet of S'Espardelló, there are free-living nodules, a unique morphology for this species that has never before been observed in the Mediterranean. The main threat to this species is warming waters (Vaquer-Sunyer et al., 2024).
Climate change is causing an increase in the frequency and intensity of marine heatwaves (MHWs) and mass mortality events (MMEs) of marine organisms are one of their main ecological impacts. Garrabou et al. (2022) show that during the 2015–2019 period, the Mediterranean Sea has experienced exceptional thermal conditions resulting in the onset of five consecutive years of widespread MMEs across the basin. These MMEs affected thousands of kilometres of coastline from the surface to 45 m, across a range of marine habitats and taxa (50 taxa across 8 phyla). Significant relationships were found between the incidence of MMEs and the heat exposure associated with MHWs observed both at the surface and across depths. Negative effects on Cladocora caespitosa were noted. The findings reveal that the Mediterranean Sea is experiencing an acceleration of the ecological impacts of MHWs which poses an unprecedented threat to its ecosystems' health and functioning (Garrabou et al., 2022).
In the last two years—2022 and 2023—more than half of the days in the Balearic Sea were marine heatwaves. Specifically, in 2023, 214 marine heatwave days were recorded, while in 2022, there were 202. In fact, the number of marine heatwave days has increased over time at a rate of 2.7 days per year. The average intensity of marine heatwaves in 2023 was 2.03°C higher than the average for the reference period 1982–2015. The average intensity has increased at a rate of 0.01°C per year over the period 1982–2023. The maximum intensity of marine heatwaves in 2023 was 4.31°C above the average for the 1982-2015 reference period. It has been increasing over time at a rate of 0.05°C/year. Marine heatwaves have multiple effects on marine organisms, habitats, and ecosystem functioning. Mass mortality events of corals, gorgonians, and sponges have been observed due to the effects of heatwaves. They have also been associated with mass blooms of Posidonia oceanica and pseudoviviparity (Vaquer-Sunyer et al., 2024).
According to the Balearic Sea Report (IMB) dozens of coral and gorgonian species (from 1 m to > 1,000 m depth) are in vulnerable status, but not all of them are protected by regulations. Cladocora caespitosa shows the highest coverage in Formentera, and in Menorca it has a wide presence around the island (Vaquer-Sunyer et al., 2024). At shallower depths (<40 m), C. caespitosa stands out as abundant on all the islands. This species cohabits with algae and is the only one that forms reefs in the Mediterranean. Colonies have been observed in many areas of Menorca, some with significant populations (maximum coverage of 12% in Fornells and 10% in Ciutadella and Cala Pedrera) and Formentera (maximum coverage of 33.7% in Punta Pedrera-Es Banc and 20% in S'Espardelló), which are of great importance in the Mediterranean. It is worth noting that on Formentera, on the islet of S'Espardelló, there are free-living nodules, a unique morphology for this species that has never before been observed in the Mediterranean. The main threat to this species is warming waters (Vaquer-Sunyer et al., 2024).
Exceptional marine biodiversity
High Concern
Trend
Data Deficient
The conservation status of marine biodiversity of the site, although apparently not currently monitored in detail, is inferred to be of high concern because it largely depends on the conservation status of the Posidonia oceanica meadows and the increasing occurrence of marine heatwaves is also likely to impact marine biodiversity in general (IUCN Consultation, 2020; Vaquer-Sunyer et al., 2024). The Mediterranean Monk Seal, once found in Posidonia meadows of the Mediterranean, has disappeared and is unlikely to return given the high anthropogenic disturbance.
The occurrence and reproductive success of loggerhead turtles on beaches in the Balearic Islands appears stable. In 2019, two loggerhead sea turtle nests were located for the first time on beaches in the Balearic Islands, all on the island of Ibiza. In 2020, three nests were found: two in Menorca and one in Ibiza. In 2021 and 2022, none were found, only one attempt to lay eggs in each of those years in Formentera, both of which were unsuccessful. In 2023, a total of six nests were located: three in Mallorca and three in Ibiza. Additionally, three unsuccessful attempts were recorded on two beaches in Mallorca. In 2019, a total of 160 eggs were laid, while in 2020 there were 340 (180 eggs more than the previous year); in 2023 there were 428, the year in which the highest number of eggs was found. Reproductive success in 2019 was 0.23, while in 2020 it was 0.46, and in 2023 it was 0.47. Therefore, in 2019, 23% of the eggs hatched, in 2020 it was 46%, and in 2023 it was 47% of the eggs. Between 1993 and 2023, 1,288 common turtles were found stranded. The years in which the most (83) were found since records began were 2020 and 2023, with 30 dead turtles and 53 live ones in 2020, and 46 dead and 36 live ones in 2023. The main cause of strandings between 2015 and 2023 was entanglement in plastics or ghost fishing gear (Vaquer-Sunyer et al., 2024).
The sperm whale encounter rate in the Balearic Islands from 2003 to 2021 has been recorded, with a sampling gap (2009-2011), based on the sperm whale research and monitoring campaigns of the Balearic Sperm Whale Project. There is a significant increase in presence in the second period (2013-2022). The goal of good environmental status would be to maintain a rate above 0.01 or increase it. In 2022, the rate will be slightly above this point, maintaining the same level of presence. Regarding the sperm whale encounter rate indicator, the Balearic Sea is in good environmental status (Vaquer-Sunyer et al., 2024).
The occurrence and reproductive success of loggerhead turtles on beaches in the Balearic Islands appears stable. In 2019, two loggerhead sea turtle nests were located for the first time on beaches in the Balearic Islands, all on the island of Ibiza. In 2020, three nests were found: two in Menorca and one in Ibiza. In 2021 and 2022, none were found, only one attempt to lay eggs in each of those years in Formentera, both of which were unsuccessful. In 2023, a total of six nests were located: three in Mallorca and three in Ibiza. Additionally, three unsuccessful attempts were recorded on two beaches in Mallorca. In 2019, a total of 160 eggs were laid, while in 2020 there were 340 (180 eggs more than the previous year); in 2023 there were 428, the year in which the highest number of eggs was found. Reproductive success in 2019 was 0.23, while in 2020 it was 0.46, and in 2023 it was 0.47. Therefore, in 2019, 23% of the eggs hatched, in 2020 it was 46%, and in 2023 it was 47% of the eggs. Between 1993 and 2023, 1,288 common turtles were found stranded. The years in which the most (83) were found since records began were 2020 and 2023, with 30 dead turtles and 53 live ones in 2020, and 46 dead and 36 live ones in 2023. The main cause of strandings between 2015 and 2023 was entanglement in plastics or ghost fishing gear (Vaquer-Sunyer et al., 2024).
The sperm whale encounter rate in the Balearic Islands from 2003 to 2021 has been recorded, with a sampling gap (2009-2011), based on the sperm whale research and monitoring campaigns of the Balearic Sperm Whale Project. There is a significant increase in presence in the second period (2013-2022). The goal of good environmental status would be to maintain a rate above 0.01 or increase it. In 2022, the rate will be slightly above this point, maintaining the same level of presence. Regarding the sperm whale encounter rate indicator, the Balearic Sea is in good environmental status (Vaquer-Sunyer et al., 2024).
Endemic and threatened terrestrial flora
High Concern
Trend
Deteriorating
Degradation of the fragile dune ecosystems in the terrestrial/coastal part of both the Natural Park and the small Nature Reserves (e.g. Migjorn and Cavallet beaches (Ibiza) and also in Formentera) has been documented. Although information about the terrestrial and coastal flora is limited, important habitat has been lost. High tourist pressure and also the impact of some public works, such as the underground electricity cable linking Ibiza and Formentera, are the cause (IUCN Consultation, 2020).
Endemic and threatened terrestrial fauna
High Concern
Trend
Deteriorating
Colonies of the Critically Endangered Balearic Shearwater (Puffinus mauretanicus) on Formentera, which overlap with the property, have experienced a strong decline in recent years (ACAP, 2012; Louzao et al., 2016). Alien invasive predators such as feral cats (Felis catus) and black rats (Rattus rattus) have caused a great impact. Habitat destruction is an issue in some of the breeding areas, and a problem not yet evaluated is artificial pollution from new tourist facilities (McMinn and Cooper, 2015; Rodriguez et al., 2022). The Endangered Ibiza Wall Lizard (Podarcis pitiusa) is threatened by an introduced snake (Picó et al., 2019; Montes et al., 2022; GEN-GOB, 2024b; GOIB, 2025). New detections of invasive species have occurred since the last review.
Assessment of the current state and trend of World Heritage values
Deteriorating
Many key ecosystem and biodiversity values of the site continue to deteriorate, including Posidonia oceanica meadows and dune ecosystems with all their associated biodiversity, "Pillow Coral" Cladocora caespitosa, and highly threatened species such as Balearic Shearwater Puffinus mauretanicus and Ibiza Wall Lizard Podarcis pityusensis. However, impressive Posidonia oceanica meadows in the property conserving a wide range of important marine biodiversity and sequestering carbon still remain along with emblematic marine fauna. But further efforts are needed to conserve the current state of World Heritage values and to reverse the trend of those in decline.
Additional information
Outdoor recreation and tourism
For Ibiza and Formentera, in 9 months 3.3 million tourists visited the islands in 2023, 242,407 more than the same period in 2022 (Makepeace, 2023). In 2024, the numbers appear to have even increased even more (TTW, 2025). The beaches of Ses Salines and Escavellet are among the most heavily used of Ibiza (IUCN Consultation, 2020).Given the proximity of the site to Ibiza city and surrounding urban areas, mass tourism on land and at sea contributes significantly to income generation and economic development. Sustainable management is a very difficult challenge. If managed sustainably, the site would continue to offer a unique opportunity to experience an extraordinary coastal landscape and seascape with its associated biodiversity.
Importance for research
The site has contributed to the scientific understanding of coastal Mediterranean waters and seagrass meadows, and continues to support extensive scientific research and publications (UNEP-WCMC, 2011), from public and private organizations (IMEDEA, CEAB-CSIC, Fundació Marilles, etc). Some research is also undertaken around the impacts that heavy tourist use, noise, water pollution, etc. are having on the natural heritage.
Contribution to education
Based on the site’s significant importance for knowledge generation and its visitor and educational programmes and facilities, it also functions as a living museum, which gives people a direct impression of the coastal Mediterranean landscape and seascape (Dirección General de Medio Natural y Gestión Forestal, n.d.)
Fishing areas and conservation of fish stocks
The seagrass meadows of the site are important spawning and nursing areas for a wide range of fish species, including commercially important species that support fisheries throughout the Balearic Islands (Reñones et al., 1995; IUCN, 1999). Although this support function to sustainable fisheries has not been quantified in financial terms, these benefits are likely to be significant.
Carbon sequestration
Posidonia oceanica seagrass meadows are considered as “blue carbon” store: coastal vegetation that sequesters CO2 and store carbon more effectively than terrestrial forests (Fourqurean et al., 2012). Thus, posidonia meadows contribute to climate regulation being estimated that it stores 420 103 gC m-2 (Pergent et al., 2012). In the Heritage site was estimated to exist 4,580 ha of posidonia meadows (Ballesteros and Cebrián, 2004), so according on previous estimation for all the posidonia meadows in the Balearic Islands (MacCord and Mateo, 2010; Pergent et al., 2012), the carbon stock of the site may be estimated around 270 million € on the global carbon market.
The most obvious benefits provided by the site are connected to recreational activities of mass tourism and the industry that is based on it, as the main pillar of the local economy. However, the site and particularly its seagrass meadows have other equally important benefits, such as contribution to sustainable fisheries, climate change mitigation, knowledge and simply to the conservation of an endemic and uniquely well-represented ecosystem supporting a number of globally threatened species.
| № | Organization | Brief description of Active Projects | Website |
|---|---|---|---|
| 1 | Mediterranean Institute of Advanced Studies | Various research projects related to marine conservation, seagrass ecosystem ecology and global change. |
http://www.imedea.uib.es/
|
| 2 | GEN-GOB Eivissa | Various projects on ecological education, monitoring of conservation status. |
http://www.gengob.org/
|
| 3 | Oceana Europe | Campaign to enforce the preservation and conservation of posidonia meadows in Ibiza and Formentera |
http://oceana.org/es/eu/portada
|
| 4 | Ibiza Preservation | The main aim of Ibiza Preservation is to support local initiatives that contribute that the tourism-based economy can co-exist harmoniously with our unique cultural and environmental heritage. One of the projects is the Observatory of Sustainability of Ibiza & Formentera. |
https://ibizapreservation.org/
|
| 5 | Blanes Centre for Advanced Studies - CSIC | The Blanes Centre for Advanced Studies (CEAB) is a research institute belonging to the Higher Council of Scientific Investigations (CSIC) of Spain. The researches undertaken by CEAB in the Ibiza WHS include micro-plastic pollution evolution and impacts. |
http://www.ceab.csic.es/en/
|
| 6 | Marilles Foundation | Marilles (in Catalan = Sea islands) is a locally-based organisation with considerable regional expertise, working with a wide range of local organisations to tackle the challenges of marine environment of the Balearics, funding projects that improve the conservation of the Balearic Sea and its coast. Current priorities include: improve marine protected areas; secure sustainable fisheries; promote marine education, reduce the impact of the boating and tourism industries, and of plastics and pollution. |
https://marilles.org/en
|
| 7 | Balearic Government in collaboration with SEO/BirdLife | The ARES II projec was a four-year biodiversity initiative running until 2024. Building upon the previous ARES program (2017–2020), ARES-II focused on the conservation of the Balearic Islands' most vulnerable native species. Key actions included monitoring 39 threatened plant species (some of which present in the Ses Salines of Ibiza and Formentera Natural Park), developing ex-situ germination and cultivation protocols, conducting genetic studies to prioritize conservation efforts, and implementing urgent measures for species like the Formentera beetle (Akis bremeri) and the critically endangered marbled teal (Marmaronetta angustirostris). The project also involved drafting a new recovery plan for bats, conducting population censuses of the European bee-eater and European shag, assessing the impact of bycatch on shearwater species, evaluating available biomass for scavengers, and continuing public outreach and monitoring of power lines. |
www.seo.org
|
References
| № | References |
|---|---|
| 1 |
ACAP (2012). Species assessments: Balearic Shearwater Puffinus mauretanicus. Agreement on the Conservation of Albatrosses and Petrels. http://www.acap.aq
|
| 2 |
ATP (2012). Regulación de fondeo en la zona noroeste de la isla de Formentera dentro del ámbito del Parque Natural de Ses Salines d’Eivissa I Formentera. Estudio de repercusiones ambientales. Asesoría Técnica y Proyectos. Consell Insular de Formentera, Área de Medi Ambient. 55pp + annexes.
|
| 3 |
Adrover. M. (2022). Frenazo al crecimiento urbanístico: el Govern prohíbe a los municipios autorizar nuevas urbanizaciones. Dario de Ibiza. Published online 28 December 2022. Available at: https://www.diariodeibiza.es/ibiza/2022/12/28/govern-prohib…
|
| 4 |
Agulles, M., Jordà, G., & Lionello, P. (2021). Flooding of sandy beaches in a changing climate. The case of the Balearic Islands (NW Mediterranean). Frontiers in Marine Science, 8, 760725.
|
| 5 |
Arnaud-Haond, S., Duarte, C. M., Díaz-Almela, E., Marbà, M., Sintes, T., and Serrão, E. A. (2012). Implication of extreme life span in clonal organisms: millenary clones in meadows of the threatened seagrass Posidonia oceanica. PLoS ONE. DOI: 0030454.https://journals.plos.org/plosone/article?id=10.1371/journa…
|
| 6 |
Ballesteros, E. and Cebrian, E. (2004). Estudi sobre la bionomia bentònica, biodiversitat i cartografia de la reserva dels Freus entre Formentera i Eivissa. Informe Final – I. Centre d’Estudis Avançats de Blanes.
|
| 7 |
Ballesteros, E., Cebrian, E. and Alcoverro, T. (2007). Mortality of shoots of Posidonia oceanica following meadow invasion by the red alga Lophocladia lallemandii. Botanica Marina 50: 8–13.
|
| 8 |
BirdLife International (2025). Site factsheet: Salinas de Ibiza y Formentera e islas de los Freus. Downloaded from https://datazone.birdlife.org/site/factsheet/saltpans-of-ib… on 18/03/2025.
|
| 9 |
Boudouresque, C. (2004). Marine biodiversity in the Mediterranean: Status of species, populations and communities. Sci. Rep. Port-Cros natl. Park, Fr. 20: 97-146.
|
| 10 |
Box, A., Colomar, V., Sureda, A., Tejada, S., Nuñez-Reyes, V., Cohen-Sanchez, A., ... & Pinya, S. (2020). Next step of the colonization of the Balearic Islands (Spain) by invasive Atlantic blue crab, Callinectes sapidus Rathbun, 1896 (Crustacea: Decapoda: Portunidae). BioInvasions Rec, 9(2), 259-265.
|
| 11 |
Braintrust (2021). Plan estratégico de turismo Ciutat d’Eivissa. Versión 01. Document developed for the City Council of Ibiza by Braintrust. 124 pp.
|
| 12 |
Cadena SER (2025). Sancionada con 6001 euros la empresa que alquiló a Loewe un espacio en el Parque Natural de Ses Salines. Published online 3 March 2025. Available at: https://www.eldiario.es/illes-balears/sociedad/sancionada-e…
|
| 13 |
Cebrian, E. and Ballesteros, E. (2010). Invasion of Mediterranean benthic assemblages by red alga Lophocladia lallemandii (Montagne) F. Schmitz: Depth-related temporal variability in biomass and phenology. Aquatic Botany 92(2): 81-85.
|
| 14 |
Chessa, L.A., Fustier V., Fernandez, C., Mura, F., Pais, A., Pergent, G., Serra, S. and Vitale, L. (2000). Contribution to the knowledge of “banquettes” of Posidonia oceánica (L.) Delile in Sardinian island. Biol. Mar. Medit. T(2):35-38.
|
| 15 |
Compa, M., Perelló, E., Box, A., Colomar, V., Pinya, S., & Sureda, A. (2023). Environmental Science and Pollution Research, 30, 119329–119342
|
| 16 |
Del Valle, L., Murray, I., Pons, G.X. and Calvo, J. (2017). Capacidad de carga socioambiental de la isla de Eivissa. Estado de la cuestión. Monografies de la Societat d’Història Natural de les Balears. 206 pp.
|
| 17 |
Diario de Ibiza (2024). Productora grabó video de Katy Perry en Ses Salines sin permiso. Published online 13 August 2024. Available at: https://www.diariodeibiza.es/ibiza/2024/08/13/productora-gr…
|
| 18 |
Dirección General de Medio Natural y Gestión Forestal (n.d). Parque Natural de ses Salines de Ibiza y Formentera. Available at: https://www.caib.es/sites/espaisnaturalsprotegits/es/parque…
|
| 19 |
Eivissa (2023). Plan General de Ordenación Urbana 2023. Comisión Insular de Ordenación del Territorio, Urbanismo y Patrimonio Histórico-Artístico del Consell Insular de Eivissa. Available at: https://www.eivissa.es/portal/index.php/es/ciudad/urbanismo
|
| 20 |
Ferrer, J.L. (2024). La saturación de yates entre Ibiza y Formentera, vista desde el espacio. Dario de Ibiza. Published online 10 September 2024. Available at: https://www.diariodeibiza.es/medio-ambiente/2024/09/10/satu….
|
| 21 |
Forteza, V., Castelló, M. and Ballesteros, E. (2024). Invasion of Batophora J. Agardh, 1854 (Chlorophyta: Dasycladales) in Formentera, Balearic Islands. Boll. Soc. Hist. Nat. Balears, 67, pp. 67-74
|
| 22 |
Fourqurean, J. W., Duarte, C.M., Kennedy, H. et al. (2012). Seagrass ecosystems as a globally significant carbon stock. Nature Geoscience 5(7): 505-509.
|
| 23 |
GEN-GOB (2024a). El Grup d’Estudis de la Naturalesa de les Pitiüses (GEN) y Grupo de Ornitología Balear (GOB), Área marina https://gengob.org/es/area-marina/. See video about plastic pollution https://youtu.be/B7ojkfS0U58
|
| 24 |
GEN-GOB (2024b). Informe de seguiment de la Sargantiana pitiüsa : Parc Natural de Ses Salines 2023-2024 https://gengob.org/wp-content/uploads/2024/12/informe-sarga…
|
| 25 |
GOIB (2020). Plan de Gestión Natura 2000 Salines d’Eivissa i Formentera. Govern de les Illes Balears, Conselleria d’Agricultura, Medi Ambient i Territori. Direcció General de Medi Natural, Educació Ambiental i Canvi Climàtic. 176 pp. + annexes.
|
| 26 |
GOIB (2021). Fifteen sea turtles born in Ibiza in September 2020 released in the Ses Salines Natural Park. https://www.caib.es/pidip2front/jsp/es/ficha-convocatoria/s…
|
| 27 |
GOIB (2021b) El proyecto 'Prats Nets d'Invasores' inicia la eliminación de nueve especies invasoras en las principales zonas húmedas de las Illes Balears. https://www.caib.es/pidip2front/jsp/es/ficha-convocatoria/s…
|
| 28 |
GOIB (2025). El Govern captura más de 3.800 ejemplares de serpientes invasoras en las Pitiusas durante la campaña de 2024. Govern de les Illes Balears.
https://www.caib.es/webgoib/es/-/el-govern-captura-m%C3%A9s… |
| 29 |
Garrabou, J., Gómez‐Gras, D., Medrano, A., Cerrano, C., Ponti, M., Schlegel, R., ... & Harmelin, J. G. (2022). Marine heatwaves drive recurrent mass mortalities in the Mediterranean Sea. Global Change Biology, 28(19), 5708-5725.
|
| 30 |
Greenpeace (2024). Crisis a toda costa 2024. Análisis de la situación del litoral ante los riesgos de la emergencia climática. Greenpeace España. https://es.greenpeace.org/es/wp-content/uploads/sites/3/202…
|
| 31 |
IMEDEA n.d. Posidonia oceanica Genome Project. El Instituto Mediterráneo de Estudios Avanzados (IMEDEA). Available at: https://imedea.uib-csic.es/sites/posigenome/es/index_es-esp…
|
| 32 |
IUCN (1999). World Heritage Nomination – IUCN Technical Evaluation: Ibiza: Biodiversity and Culture, Balearic islands, Spain. Gland: IUCN. https://whc.unesco.org/en/list/417/documents/
|
| 33 |
IUCN Consultation (2020). IUCN World Heritage Confidential Consultation (pers. comm.). Ibiza: Biodiversity and Culture, Balearic Islands (Spain).
|
| 34 |
Ibiza Council (2014). Ibiza Biodiversity and Culture Volume 1 Conservation Report 1999-2014. Ajuntament d’Eivissa, Spain. 97 pp. + Volume 2 and Annexes.
|
| 35 |
Ibiza Preservation (2024). More than 50% of Talamanca’s Posidonia oceanica meadows are dead, according to study. IbizaPreservation Organisation. Published online 6 February 2024. Available at: https://ibizapreservation.org/en/more-than-50-of-talamancas…
|
| 36 |
Ibiza Preservation (2024). Record numbers of cruise ship passengers arrived in Ibiza in 2023, new analysis reveals. Published online 15 August 2024. Available at: https://ibizapreservation.org/en/record-numbers-of-cruise-s…
|
| 37 |
Jimenez, C., Hadjioannou, L., Petrou, A., Nikolaidis, A., Evriviadou, M. and Lange, M. (2014). Mortality of the scleractinian coral Cladocora caespitosa during a warming event in the Levantine Sea (Cyprus). Regional Environmental Change 16(7). DOI: 10.1007/s10113-014-0729-2
|
| 38 |
Kersting, D. K., Cebrian, E., Verdura, J., and Ballesteros, E. (2017). A new Cladocora caespitosa population with unique ecological traits. Mediterranean Marine Science 18(1): 38-42. https://www.researchgate.net/publication/313655536_A_new_Cl…
|
| 39 |
Losciale, R., Day, J., & Heron, S. (2022). Conservation status, research, and knowledge of seagrass habitats in World Heritage properties. Conservation Science and Practice, 4(12), e12830.
|
| 40 |
Louzao, M., García, D. and Arcos, J.M. (2016). Conservación Integral de la Pardela Balear Puffinus mauretanicus In: Pitiüses: uniendo puentes entre los ecosistemas marino y terrestre. SEO/BirdLife, IEO, AZTI-Tecnalia and IRBI. Informe de actualización 2013-2015.
|
| 41 |
MacCord F., Mateo, M.A. (2010). Estimating the size of the carbon sink represented by Posidonia oceanica meadows along the coasts of the Balearic Island. Proyecto final de investigación, Master en Cambio Global, UIMP-CSIC, Spain : 35 p.
|
| 42 |
Makepeace (2023). The Numbers Don’t Lie – Record Year for Ibiza. Blog post. Published online 9 November 2023. Available at: https://maninsanan.com/2023/11/09/the-numbers-dont-lie-reco…
|
| 43 |
Marba, N. and Duarte C. M. (2010). Mediterranean warming triggers seagrass (Posidonia oceanica) shoot mortality. Global Change Biology 16(8): 2366-2375. https://www.researchgate.net/publication/227509984_Mediterr…
|
| 44 |
Martinez, M., Minetti, R., La Marca, E.C., Montalto, V., Rinaldi, A., Costa, E., Badalamenti, F., Garaventa, R., Mirto, S. and Ape, F. (2024). The power of Posidonia oceanica meadows to retain microplastics and the consequences on associated macrofaunal benthic communities. Environ Pollut.1:348:123814.
|
| 45 |
Martos, E.R. (2021). El Govern reclama al Estado que reduzca los cruceros en Ibiza y el tráfico marítimo regular entre las Pitiusas. Dario de Ibiza. Published online 1 November 2021. Available at: https://www.diariodeibiza.es/ibiza/2021/11/01/govern-reclam…
|
| 46 |
McMinn, M. and Cooper, J. (2015). ACAP Breeding Site No. 77. Agreement on the Conservation of Albatrosses and Petrels. http://www.acap.aq
|
| 47 |
Montes, E., Kraus, F., Chergui, B., and Pleguezuelos, J.M. (2022). Collapse of the endemic lizard Podarcis pityusensis on the island of Ibiza mediated by an invasive snake. Current Zoology 68(3): 295–303.
|
| 48 |
Murray, I. (2013). Análisis por comunidades autónomas: Illes Balears In: Prieto, F. & Ruiz, J.B. Costas Inteligentes. Estudio realizado para Greenpeace España. Madrid.
|
| 49 |
Neath, A. (2024). Ibiza to limit cruise ship arrivals amid Spain’s overtourism crisis. The Independent. Published online 17 September 2024. Available at: https://www.independent.co.uk/travel/news-and-advice/ibiza-…
|
| 50 |
Pergent, G., Bazairi, H., Bianchi, C.N., Boudouresque, C.F., Buia, M.C., Clabaut, P., Harmelin-Vivien, M., Mateo, M.A., Montefalcone, M., Morri, C., Orfanidis, S., Pergent-Martini, C., Semroud, R., Serrano, O. and Verlaque, M. (2012). Mediterranean Seagrass Meadows : Resilience and Contribution to Climate Change Mitigation, A Short Summary. Gland, Suiza y Málaga, España: IUCN. 40 pages.
|
| 51 |
Periódico de Ibiza (2024). Habrá primer baño del año en Ses Salines de Ibiza. Published online 30 December 2024. Available at: https://www.periodicodeibiza.es/pitiusas/ibiza/2024/12/30/2…
|
| 52 |
Piazzi, L., Ceccherelli, G. and Cinelli, F. (2001). Threat to macroalgal diversity: Effects of the introduced green alga Caulerpa racemosa in the Mediterranean. Marine Ecology Progress Series 210: 149-159.
|
| 53 |
Picó, G., Fernández, M. J., Moreno, J. E., and Colomar, V. (2019). Control of the ladder snake (Rhinechis scalaris) on Formentera using experimental live-traps. In: C.R. Veitch, M.N. Clout, A.R. Martin, J.C. Russell and C.J. West (eds.) (2019). Island invasives: scaling up to meet the challenge.Occasional Paper SSC no. 62. Gland, Switzerland: IUCN. pp.332-336.
|
| 54 |
Ramón-Cardona, J., Peña-Miranda, D. D., & Sánchez-Fernández, M. D. (2021). Critical analysis of a World Heritage Site in terms of conservation and tourism promotion: The case of “Ibiza, Biodiversity and Culture”(Ibiza, Spain). Sustainability, 13(23), 13250.
|
| 55 |
Reñones, O., Massuti, E., Moranta, J. et al. (1995). Fish fauna of Posidonia oceanica seagrass meadows in Palma Bay (Balearic Islands). Cybium 19(2):201-206.
|
| 56 |
Ruiz-Orejón, L.F., Sardá, R. and Ramis-Pujol, J. (2018). Now, you see me: High concentrations of floating plastic debris in the coastal waters of the Balearic Islands (Spain). Marine Pollution Bulletin 133 : 636-646. https://www.sciencedirect.com/science/article/abs/pii/S0025…
|
| 57 |
Rössler, M., Niksic, G., and Pergent Martini, C. (2009). Mission report: Ibiza, Biodiversity and Culture (Spain) (417rev). Gland, Switzerland and Paris: IUCN and UNESCO World Heritage Centre.
|
| 58 |
Serapio, J., Laguna, E., Gómez-Bellver, C., Domínguez, L. A., Verloove, F., & Sáez, L. (2023). Contribution to the alien flora of the Balearic Islands. Butlletí de la Institució Catalana d’Història Natural, 87(1), 11-28.
|
| 59 |
SoOUV (2023). Statement of Outstanding Value: Ibiza, Biodiversity and Culture (Spain). https://whc.unesco.org/en/decisions/8343
|
| 60 |
Sobrado, F. & Palomares, A. (2025). Seguiment tècnic de les praderies de Posidonia oceanica a l’illa d’Eivissa. GEN-GOB. https://ibizapreservation.org/wp-content/uploads/2025/03/Se…
|
| 61 |
Sobrado, F. and Sáez, J. (2024) Inventory of historical remains located in the Balearic Islands. Internal Report, Conselleria d'Agricultura, Pesca y Medi Natural.
|
| 62 |
Sobrado, X., Marí, M. and Sáez, J. (2018). Situació ambiental de les depuradores i emissaris submarins a les Pitiüses 2013 - 2016. Gen-GOB Eivissa. https://lamar.gengob.org/wp-content/uploads/2018/04/Informe…
|
| 63 |
State Party (2024). Periodic Reporting Cycle 3, Section II. Ibiza, Biodiversity and Culture (Spain). https://whc.unesco.org/en/list/417/documents/
|
| 64 |
TTW (2025). Balearic Islands Tourism Reaches New Heights In 2024 With Mallorca, Ibiza, Menorca, And Formentera Leading The Way. Travel and Tour World. Published online 5 February 2025. Available at: https://www.travelandtourworld.com/news/article/balearic-is…
|
| 65 |
Technoambiente (2017). Estudio de los impactos provocados por las diferentes actividades sobre las praderas de fanerógamas marinas, el caso del litoral de las Islas Baleares. Associación Española de Grandes Yates (AEGY). 87 pp.
|
| 66 |
UNEP-WCMC (2011). Ibiza: Biodiversity and Culture, Balearic islands, Spain. UNEP-WCMC World Heritage Information Sheets.
http://world-heritage-datasheets.unep-wcmc.org/datasheet/ou… |
| 67 |
Vaquer-Sunyer, R., Barrientos, N. and Murray, I. (2020). Superficie de costa urbanizada. In: Vaquer-Sunyer, R.; Barrientos, N. (eds.). Informe Mar Balear 2020. Fundació Marilles. https://www.informemarbalear.org/es/presiones/imb-costa-urb…
|
| 68 |
Vaquer-Sunyer, R.; Barrientos, N.; Gouraguine, A. (ed.) (2024). Informe Mar Balear 2024. <https://www.informemarbalear.org/es/Informe-Mar-Balear-esp_…;. https://doi.org/10.62135/UHVL1020.
|
| 69 |
Vercher, N. (2022). Environmental Conflicts and Social Innovation on the Balearic Islands (Spain). Sustainability14: 4994. https://doi.org/10.3390/su14094994
|
| 70 |
Viñolas, A, 2011, Akis bremeri (Ardoin, 1979), pp 327- 329. In: Verdú, J. R., Numa, C. and Galante, E. (Eds). Atlas and Red Book of Threatened Invertebrates of Spain (Vulnerable Species). Directorate General of Natural Environment and Forest Policy, Ministry of Environment, Rural and Marine Affairs, Madrid.
|
| 71 |
WHC (2009). Decision 33 COM 7B.41. Ibiza, Biodiversity and Culture (Spain) (C/N 417rev). World Heritage Committee. Available at https://whc.unesco.org/en/list/417/documents/
|
| 72 |
WHC (2010). Decision 34 COM 7B.41. Ibiza, Biodiversity and Culture (Spain) (C/N 417rev). World Heritage Committee. Available at https://whc.unesco.org/en/list/417/documents/
|
| 73 |
WHC (2011). Decision 35 COM 7B.37. Ibiza, Biodiversity and Culture (Spain) (C/N 417rev). World Heritage Committee. Available at https://whc.unesco.org/en/list/417/documents/
|
| 74 |
Álvarez, E., Grau, A.M., Marbà, N. and Carreras, D. (2015). Islas Baleares. In: Ruiz, J.M., Guillén, J.E., Ramos Segura, A. & Otero, M.M. (Eds.). Atlas de las praderas marinas de España. IEO/IEL/UICN, Murcia-Alicante-Málaga: 179-219 pp.
|