Grottes du karst d'Aggtelek et du karst de Slovaquie
Country
Hungary,
Slovakia
Inscribed in
1995
Criterion
(viii)
The conservation outlook for this site has been assessed as "good" 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.
La variété de leurs formes et leur concentration dans une aire restreinte font des 712 grottes actuellement identifiées un système karstique typique de la zone tempérée. Présentant une combinaison extrêmement rare d'effets climatiques tropicaux et glaciaires, elles permettent d'étudier l'histoire géologique sur plusieurs dizaines de millions d'années. © UNESCO
Summary
2025 Conservation Outlook
Finalised on
11 oct 2025
Good
Current state and trend of VALUES
Good
Overall THREATS
Overall PROTECTION and MANAGEMENT
Full assessment
Description of values
Remarkable diversity of caves types and important evidence of geologic history
Criterion
(viii)
The site is distinctive in its great number (with 712 recorded at time of inscription) of different types of caves found in a concentrated area. Geological processes causing karst features to be buried by sediment and then later reactivated or exhumed provide evidence pertaining to the geologic history of the last tens of millions of years. Relicts of pre-Pleistocene karst (i.e. more than about 2 million years old) are very distinct in the area, and many of them show evidence for sub-tropical and tropical climate forms. These include rounded hills that are relicts of tropical karst later modified by Pleistocene periglacial weathering. This suite of paleokarst features, showing a combination of both tropical and glacial climates, is very unusual and is probably better documented in the Slovak Karst than anywhere else in the world. These caves are also noted for having the world's highest stalagmite, aragonite and sinter formations and an ice filled abyss, which considering the territory's height above sea level, is a unique phenomenon for central Europe (World Heritage Committee, 2013). The current number of registered caves on the Slovak side is 1184 and 280 on the Hungarian side (Bella et al., 2015).
Important cave biodiversity
Cave and subterranean water fauna are of particular scientific interest (IUCN, 1995). Beetles and other insects are abundant. Cave worms are often found in sand and clay deposits whereas molluscs are associated with underground streams, and crustaceans occur including an endemic species of primitive crab. A total of 21 bat species were recorded at the time of inscription (IUCN, 1995) and 28 are known at present (IUCN Consultation, 2020a). In total, about 500 animal species have been identified in the caves, many of them endemic (IUCN Consultation, 2020a). Although bats are the most abundant cave fauna, some other fauna is notable, some of which are endemics and troglobites, such as the shrew Eukoenenia spelaea, the cave shrew Niphargus aggtelekiensis, the beetle Duvalius bokor, the shrew Neobisium slovacum, and the springtail Pseudosinella aggtelekiensis (Kudla et al. 2024). The caves of the Aggtelek Karst are the home to fauna elements with southern origin like the aquatic annelid Helodrilus mozsaryorum (described as Allolo bophora mozsaryorum) and the palpigrade Eukoenenia spelaea vagvoelgyii the latter of which represents the northernmost occurrence of the genus. Other species such as the amphipod Niphargus aggetlekiensis or the coleopteran Duvalius hungaricus (Csiki 1903) are from Northern-Carpathian clades (Szinetár et al. 2022).
Above-ground biodiversity
A unique biotope arises where two floral sectors (Carpathian and Pannonian) overlap, and consequently many rare endemics can be found throughout the territory. Approximately 70% of the territory consists of deciduous woodland dominated by hornbeam and oak. Within Slovakia, several flora taxa occur only in the Slovak Karst, e.g., Sadler’s fern (Ferula sadleriana), the pisiform grass-pea (Latyhrus pisiformis), or the short–necked sedge (Carex brevicollis). The peculiarities of the territory also create specific conditions for animals, predominantly of the steppe and forest–steppe zones, such as the predatory bush cricket (Saga pedo), the European ground squirrel (Spermophillus cittelus), the praying mantis (Mantis religiosa), or the mollusk Pupilla triplicata. The occurrence of 217 species of birds has also been confirmed (Kudla et al. 2024). The rich birdlife includes rare species like Emberiza cia, Circaetus gallicus and the Hazel grouse, Bonasia bonasia, which is probably the highest value resident bird of this karst region. Nesting bird species include: rock bunting, black stork, corncrake, imperial eagle, dipper, Ural owl, saker falcon, short-toed eagle, honey buzzard (IUCN, 1995).
In Hungary two highly protected reptiles, Ablepharus kitaibelii and Dolichophis caspius, occur almost exclusively in the karst areas. The Aggtelek and Bükk Mountains karst regions also harbour strong populations of the country’s many highly protected predatory birds, providing a key breeding area (Szinetár et al. 2022).
Two large predators, Canis lupus and Lynx lynx have permanently recolonized the region since the 1980s and 1990s, respectively. Other fauna in the property includes red deer, roe deer, wild boar, wild cat and badger (IUCN, 1995).
In Hungary two highly protected reptiles, Ablepharus kitaibelii and Dolichophis caspius, occur almost exclusively in the karst areas. The Aggtelek and Bükk Mountains karst regions also harbour strong populations of the country’s many highly protected predatory birds, providing a key breeding area (Szinetár et al. 2022).
Two large predators, Canis lupus and Lynx lynx have permanently recolonized the region since the 1980s and 1990s, respectively. Other fauna in the property includes red deer, roe deer, wild boar, wild cat and badger (IUCN, 1995).
Assessment information
Despite the strict conservation activities, the fact that the caves are visited by such a large number of visitors might eventually lead to some damage and pilferage. This threat is managed by keeping the number of visitors within the carrying capacity and offering guided tours only. Other threats from solid waste and effluent pollution remain low and contained.
Water-borne & other effluent Pollution
(Pollution from human activities)
Inside site
, Scattered(5-15%)
Outside site
There was a pollution problem which contaminated cave waters and threatened the park's ecosystem. This arose from use of pesticides and fertilizers in the surrounding areas and from tourist's vehicles and nearby industry (IUCN, 2000). Now a substantial part of agricultural land consists of permanent grasslands with preference of ecological agriculture and a general shift towards pastoral activities becoming less intensive in the area (IUCN Consultation, 2020; Slámová et al. 2024).The protected water management area of the Slovak Karst (natural water accumulation) has also been declared on the territory, and the missing sewers and wastewater treatment plants have been built in several municipalities (e.g. Silica). Through the Interreg Programme 2021-2027 between Hungary and Slovakia, there is opportunity to improve coordinated water management (Interreg, 2023). Karst water is particularly vulnerable to pollution; therefore, its protection is primarily important for the sake of long-term water supply. Therefore, the coordinated protection of water quality is essential for preserving the purity of the water bases of cross-border significance.
Recreational Activities
(Large number of visitors in the caves)
Inside site
, Localised(<5%)
More than 99% of the Caves of Aggtelek Karst and Slovak Karst is preserved in its original natural condition and is well protected. The other 1% has been substantially modified as “show-caves” to allow human use, which includes 300,000 visitors annually (World Heritage Committee, 2013). Despite the strict conservation activities, the fact that the caves are visited by such a large number of visitors might eventually lead to some damage and pilferage. Tourism is dominated by one-day visits and strong seasonality (winter tourism is almost non-existent). In the ANP, six caves can be visited by tourists but the vast majority of visitors arrive in a single cave, Baradla. Currently, the annual number of visitors is around 120,000 (Telbisz et al. 2022).There are five show caves in the area of Slovak Karst, and the visitor numbers are more evenly distributed among these caves than in the ANP. In fact, Krásnohor ská Cave is leased from the state by a private operator and therefore it is not possible to obtain information on the number of visitors of this cave. As for the the total number of visitors to the other four caves, it was 97,198 in 2019 (i.e., before Covid-19 pandemic) and 61,765 in 2021. The most visited cave is Ochtinská Aragonit Cave (Telbisz et al. 2022). According to Telbisz et al. (2023) the current visitor numbers are significantly below the carrying capacity.
Garbage & Solid Waste
(Illegal garbage disposal)
Inside site
, Localised(<5%)
Outside site
Elimination of illegal garbage disposal and building debris in caves (Gaál & Gruber, 2015) and in the surrounding settlements is necessary to prevent pollution of the water in the caves system (World Heritage Committee, 2013). In the Hungarian part of the site, there is selective waste collection in the villages and illegal garbage disposal is rare (IUCN Consultation, 2020b). In the Slovak Karst National Park cleaning events in collaboration with the Ministry of Environment, park administration, municipalities and primary schools are also organised (e.g. Slovak Karst National Park, 2022).
There is a potential risk of pollution of the cave system from mining, agricultural and forestry activities on the land in the area. Protection of the unique geological features of the site requires integrated management of the entire water catchment. Infrastructure developments especially motorway and railway tunnels may negatively impact geological and hydrological processes of the site, if construction does not adequately protect the cave and karst features. The potential impact on the property's hydrological regime, ice occurrence and flora and fauna remains as yet data deficient, however some evidence points to decrease in ice, erosion of soil and deposition of sediments in caves and increased droughs.
Unknown Threats
(Surface activities)
Inside site
, Widespread(15-50%)
Outside site
The cave system is exceptionally sensitive to environmental changes, including mining (mining in quarries Včeláre or Gombasek is in operation and located outside protected areas), agricultural and forestry activities (inappropriate management in commercial forests). Maintenance of the integrity of active geological and hydrological processes (karst formation and the development or evolution of stalagmites and stalactites) requires integrated management of the entire water catchment area (World Heritage Committee, 2013). Expansion and modernization of transport infrastructure can affect particularly the caves structures and karst features. Two notable transport infrastructure projects are: R2 motorway tunnel Soroška - Zahorec, whose construction phase is reported to be 2020-2025 (Zahorec et al., 2019: Strukturas, 2025) and the new railway line Divača-Koper, which connects the only Slovenian port Luka Koper with the logistics railway hub in Divača. The route is 27.1 km long and overcomes a 400 m height difference between the Slovenian karst plateau and sea level. The design imperative for tunnel construction was not to deplete the water resources. The karst features had to be addressed in terms of tunnel construction both from the stability point of view and as a protentional loss of abundance of vital water supply for the region. Remediation measures, divided into temporary and permanent, were used to overcome karstic features along the tunnel route. Tunnel T1 was divided into drained and undrained variants, with an aim of preservation of water resources in the long-term (Jovičić et al. 2023).
Oil & Gas exploration/development
(Risk of oil leakage from the pipeline crossing the Slovak component of the property)
Inside site
, Scattered(5-15%)
Energy distribution network - oil and gas pipeline crosses the Slovak Karst national park with approximately 25 kilometres of the pipeline running through the national park territory. While the necessary monitoring and prevention measures are in place (Gaál & Gruber, 2015), a potential oil leakage would cause serious impacts on the property.
Changes in Temperature Regimes, Changes in Precipitation & Hydrological Regime
(Effects of rising temperature and extremes in precipitation)
Inside site
, Throughout(>50%)
Outside site
Climate change manifests through its effects on flora and fauna, as well as decreased ice in the ice caves Silica (Šupinský et al., 2019) and Dobšinská or disappearance of cave decoration, erosion of soil and deposition of sediments in caves and associated possible changes in hydrological regime. Water scarcity above the ground and droughts can also affect the hydrological regime of the caves (States Parties of Hungary and Slovakia, 2014; IUCN Consultation, 2020).
Involvement of stakeholders and rightsholders, including indigenous peoples and local communities, in decision-making processes
There is one sizeable settlement (Silica) and two hamlets within the Slovak protected area and two villages (Aggtelek and Jósvafő with approximately 1,100 inhabitants) inside the Aggtelek National Park's boundaries (World Heritage Committee, 2013). Some challenges remain related to ensuring better involvement of key stakeholders in site management, communications and benefits sharing. Socio-economic situation of the Aggtelek Karst microregion is relatively better than that of the neighbouring regions, and this relative welfare is due to the existence of the national park and Baradla Cave (Telbisz et al., 2020).
Conflicts between locals and tourists are negligible, and all actors agree to further increase tourism in the area. In both ANP and SKNP, the majority of tourists and locals alike have a rather positive view of the property. However, there is still a significant group of local residents who have a negative opinion. One reason for this may be that the locals feel they have only a marginal influence on national park decisions. The ANP plays a more important role in the lives of locals than in SKNP, because ANP has a larger organisational background and more resources for a smaller population (Telbisz et al. 2022).
Conflicts between locals and tourists are negligible, and all actors agree to further increase tourism in the area. In both ANP and SKNP, the majority of tourists and locals alike have a rather positive view of the property. However, there is still a significant group of local residents who have a negative opinion. One reason for this may be that the locals feel they have only a marginal influence on national park decisions. The ANP plays a more important role in the lives of locals than in SKNP, because ANP has a larger organisational background and more resources for a smaller population (Telbisz et al. 2022).
Legal framework
All of the caves are state-owned and their protection is guaranteed by the Act no. LIII. 1996 on nature protection in Hungary and by the Slovak Constitution no. 90/2001, and the Act of Nature Protection and Landscape no. 543/2002 in Slovakia, irrespective of ownership or protection status of the surface areas (World Heritage Committee, 2013). The Aggtelek Karst (Hungary) was first declared a protected landscape area in 1978 under decision No.8/1978 of the President of the National Authority for Environment and Nature Conservation (OKTH), and in 1985 was designated a national park by law-decree No.7/1984 (XII.29.) OKTH (IUCN, 2000). The Slovak Karst Landscape Protected Area was established in 1973 and in 2002 the Slovak Karst National Park was designated (Act No. 543/2002). The protection arrangements were considered highly effective in Hungary and sufficiently effective in Slovakia (States Parties of Hungary and Slovakia, 2006). Most recently, there has been a reform of the National Park, which states that the park administration is now an independent organization with direct ownership of the land.
In Hungary 335/2019 Government Decree on the National Procedure for Designation of the World Heritage Site, on the Content Requirements of World Heritage Management Plans and the Procedure for their Preparation, on the World Heritage Management Bodies, and on the Right of Pre-emption of the State in World Heritage Sites is another important legislative component.
The latest Periodic Report (States Parties of Hungary and Slovakia, 2024) stated that legal framework provided an adequate basis for effective management and protection. Protection of caves is, if necessary, also ensured by declaring protection zones on the surface (e.g. Milada Cave). The whole process is lengthy and demanding, includes participation of landowners and, as everything, has to be approved by the government regulation. The amendment to the Nature and Landscape Protection Act specifies the conditions for renting caves for a certain period (IUCN Consultation, 2020).
In Hungary 335/2019 Government Decree on the National Procedure for Designation of the World Heritage Site, on the Content Requirements of World Heritage Management Plans and the Procedure for their Preparation, on the World Heritage Management Bodies, and on the Right of Pre-emption of the State in World Heritage Sites is another important legislative component.
The latest Periodic Report (States Parties of Hungary and Slovakia, 2024) stated that legal framework provided an adequate basis for effective management and protection. Protection of caves is, if necessary, also ensured by declaring protection zones on the surface (e.g. Milada Cave). The whole process is lengthy and demanding, includes participation of landowners and, as everything, has to be approved by the government regulation. The amendment to the Nature and Landscape Protection Act specifies the conditions for renting caves for a certain period (IUCN Consultation, 2020).
Governance arrangements
The caves of the Slovak side are not managed by the SKNP but by the Slovak Caves Administration. However, this is expected to change due to new amendment to nature protection law in Slovakia (Telbisz et al., 2022). Most recently, there has been a reform of the National Park, which states that the park administration is now an independent organization with direct ownership of the land. Relations between the two national parks are good but could be further enhanced according to Telbisz et al., (2022). ABR (Aggtelek Biosphere Reserve) has a special agreement with the Slovak Karst Biosphere Reserve. The very active cooperation targets synchronized research and monitoring programs, as well as special management projects against the invasive alien plant species.
Integration into local, regional and national planning systems (including sea/landscape connectivity)
Both national parks are well integrated into the regional systems of protected areas and are also Multi-Internationally Designated Areas (Natura 2000, Ramsar site, Biosphere Reserve). In Slovakia the caves are located almost exclusively within the territory of the Slovak Karst National Park and the Slovak Paradise National Park (Dobsina Ice Cave within Stratena cave system).
Boundaries
The site's northern and southern boundaries are defined by the geological borderline between karstic and nonkarstic rocks, whilst the western and northeasternmost points comprise Jelšava town and Jasov village, respectively (IUCN, 2000). Boundaries are adequate to maintain the property's values. However, they are not well known by local residents, communities and landowners (States Parties of Hungary and Slovakia, 2014, 2024).
Overlapping international designations
The caves of Aggtelek Karst and Slovak Karst, were jointly inscribed on the UNESCO World Heritage List in 1995. The Baradla-Domica system, as a special underground wetland, was added to the “List of Wetlands of International importance of the Ramsar Convention” in 2001. Aggtelek Landscape Protection Area was established in 1978, and in 1979 some parts of the area were included in the UNESCO Man and Biosphere reserves (Telbisz et al., 2022). Slovak Karst National Park is the first Slovak biosphere reserve since March 1, 1977 (Bolechová et al. 2022). There is some evidence of integration between the different designations, for example the ABR management plan references the WH site values and promotes training of cave guides. Furthermore, it seems there is good collaboration between the BR themselves through a special agreement. The responsibility for management of the Ramsar site also lies with the Aggtelek National Park Directorate, which suggests some coordination between the designations on the administrative level. Management plans exist but are outdated for some designations (e.g. Ramsar). There is evidence of projects being implemented in the overlapping areas e.g. a major (3 million Euros) project took place in recent years to develop the Lake Vörös entrance of Baradla cave for tourism (RIS, 2017).
Implementation of World Heritage Committee decisions and recommendations
No recent Committee decisions.
Climate action
Adaptation to climate change and prevention and management of climate-related risks is a key component of the Interreg programme 2021-2027. This includes the conservation of forests and restoration of wetlands. However, the extent to which climate change considerations are integrated into the site management is unclear.
Management plan and overall management system
In Slovakia, management of the caves system is implemented by the Slovak Caves Administration in Liptovský Mikuláš as part of State Nature Conservancy of Slovak Republic. Management of terrestrial ecosystems is implemented by the Authority of the Slovak Karst National Park in Brzotín (with the exception of the surface part of the Dobšinská ice cave, which is under administration of the Slovak Paradise National Park). Aggtelek Karst is administered by the Aggtelek National Park Directorate. The administrative bodies in two countries carry out joint projects including research, protection and monitoring (World Heritage Committee, 2013). An Integrated Management Plan has been prepared for the transboundary site. However, it has not been approved. Coordination between different administrative bodies and levels has been noted as adequate (States Parties of Hungary and Slovakia, 2024). The countries have several cross-border projects and the overlapping international designations contribute to enhance monitoring, research and other educational activities. Nevertheless, there seems so be potential to better integrate management of the overlapping designations and streamline similar objectives, especially in the various management plans.
Law enforcement
Permanent monitoring and control of caves’ condition used to be carried out by Speleological Guardian Service, which due to lack of financial sources stopped this activity in 2010 (Gaál et al., 2015). Closing (gating) of some caves for public, camera systems, technical equipment and protective zones of caves have improved the situation.
Sustainable finance
In both countries the national parks receive budget from the state which appears adequate, particularly in Hungary. Yearly budget of Aggtelek NP is approx. 12,3 mil. Euro. On Slovak side, data on Protected Areas expenses is currently not comparable. State Nature Conservancy of the Slovak Republic does not record expenditures in a way that would allow to compare unit expenditure by national parks or protected landscape areas. However, just for comparison, the whole budget of the State Nature Conservancy of the Slovak Republic (9 National Parks, 14 Protected Landscape Areas including Slovak Cave Administration) in 2019 year was only 5,2 mil. Euro, excluding funding received from the EU (IUCN Consultation, 2020). Existing sources of funding coming from few sources are not secure in the long-term and could be improved to meet management needs (States Parties of Hungary and Slovakia, 2024). Additional financial resource are needed to support control and monitoring activities, as well as risk preparedness and contingency planning for potential accidents. Both parties use various grant schemes to improve the budget they have for financing the World Heritage site. The EU structural funds are used on a long term basis, with by now a used sum exceeding 2.5 million EUR on the Slovak side (IUCN Consultation, 2020c).
The managers of the national parks are mostly committed to nature conservation, but the current financial situation poses serious limitations. The main problem in the relationship between the state and the park managers is the decreasing budget, and thus there are often not enough jobs for the park to fulfil its required tasks (Telbisz et al. 2023).
The managers of the national parks are mostly committed to nature conservation, but the current financial situation poses serious limitations. The main problem in the relationship between the state and the park managers is the decreasing budget, and thus there are often not enough jobs for the park to fulfil its required tasks (Telbisz et al. 2023).
Staff capacity, training and development
In Slovakia, there are 20 administrative staff members of national park administration listed on the website (Slovak Karst National Park, 2025) and around 28 in the State Nature Conservancy of the Slovak Republic Slovak Caves Administration with additional staff listed for each show cave (State Nature Conservancy of the Slovak Republic, 2025). This demonstrates an increase to past staffing numbers. In Hungary, the Aggtelek National Park Directorate is comprised of 145 staff members (Telbisz et al., 2022; 2023), 16 of them are responsible for caves (IUCN Consultation, 2020a); however, there has been some decrease in the number of staff since 2018 (IUCN Consultation, 2020b). Speleological staff in both countries receive occasionally training.
ANP has a larger organizational background and more human resources for a smaller population and smaller area. On the Slovak side, the SKNP is small in terms of organization, however has increased human and financial resources to develop members (Telbisz et al., 2022).
The ABR management also organizes courses for local people, where experts train cave or field tour guides (ABR management plan, 2015).
ANP has a larger organizational background and more human resources for a smaller population and smaller area. On the Slovak side, the SKNP is small in terms of organization, however has increased human and financial resources to develop members (Telbisz et al., 2022).
The ABR management also organizes courses for local people, where experts train cave or field tour guides (ABR management plan, 2015).
Education and interpretation programmes
Both countries have good education and interpretation programmes in place (States Parties of Hungary and Slovakia, 2006). Interpretative trail (e.g. reconstruction of Domica trail supported by Interreg), exhibition, promotion materials including film and lectures have been developed for visitors (Gaál et al., 2015). However, education and awareness building activities could be still improved (States Parties of Hungary and Slovakia, 2014; 2024). Two journals (Aragonit and Slovenský kras) are published regularly in print. In Hungary, there are special programs for local elementary school pupils (IUCN Consultation, 2020b).
In Hungary today, the Tapolca Lake Cave, which is close to the popular Lake Balaton and has a high-quality karst exhibition, but is much smaller than Baradla, receives more visitors than Baradla. But as another international example, Postojna can also be mentioned. It is located close to busy international pathways and has a well-developed visitor infrastructure and marketing, thus, an enormous number of visitors. Naturally, this cave absolutely deserves the attention of visitors (Telbisz et al., 2022).
A lot of information is available on the internet about the karst attractions of this region, but while the ANP website is up-to-date and available in three languages, the SKNP website is not so easy to find and is only available in Slovak (Telbisz et al., 2022).
In Hungary today, the Tapolca Lake Cave, which is close to the popular Lake Balaton and has a high-quality karst exhibition, but is much smaller than Baradla, receives more visitors than Baradla. But as another international example, Postojna can also be mentioned. It is located close to busy international pathways and has a well-developed visitor infrastructure and marketing, thus, an enormous number of visitors. Naturally, this cave absolutely deserves the attention of visitors (Telbisz et al., 2022).
A lot of information is available on the internet about the karst attractions of this region, but while the ANP website is up-to-date and available in three languages, the SKNP website is not so easy to find and is only available in Slovak (Telbisz et al., 2022).
Tourism and visitation management
Interpretation of cave protection, cave values and cave benefit for local people is effective. There are materials available in both countries. Visitor rules for caves exist and are being applied. A tourism management plan is available in both countries (States Parties of Hungary and Slovakia, 2006) and there seems to be good collaboration between the tourism industry and property managers (State Parties of Hungary and Slovak Republic, 2024). Slovak Caves are well promoted in media, tourist guides, and directional signage. While visitor awareness is strong, there is a need for improvements in transportation and tourist infrastructure (Kudla et al. 2024).
The development of a Hungarian-Slovak interactive web-map is being prepared with the presentation of important sites for bird watching, tourist attractions such as caves, nature trails, various cultural monuments and important nature conservation areas (Kilík and Balážová, 2020).
The development of a Hungarian-Slovak interactive web-map is being prepared with the presentation of important sites for bird watching, tourist attractions such as caves, nature trails, various cultural monuments and important nature conservation areas (Kilík and Balážová, 2020).
Sustainable use
The current levels of visitation appear sustainable, however, careful monitoring is required to ensure conservation of the site’s values (IUCN Consultation, 2020).
Monitoring
Regular monitoring of the caves’ state and development is carried out by the Aggtelek National Park Directorate in Hungary and the Slovak Caves Administration (States Parties of Hungary and Slovakia, 2006; 2024). Because the site belongs to important underground sites for bats in Europe (Eurobats) there is a regular winter census of bats in cooperation with the Slovak Bat Conservation Society. Mapping of underground spaces by members of the Slovak Speleological Society continue. Monitoring is also focused on study of the environmental and hydrological processes in caves (Czuppon et al., 2018) and karst area (Gessert et al., 2019). The Slovak World Heritage show caves have installations of a permanent climatic and hydrological monitoring connected to the headquarters of the Slovak Caves Administration (IUCN Consultation, 2020c). Furthermore, there is collaboration between the biosphere reserves on monitoring and research.
Research
In Slovakia, different home and foreign institutions (e.g. Slovak and Czech Academy of Sciences, and Slovak, Czech and Polish universities) are involved in the research activities, mainly geological, geomorphological, hydrogeological, speleoclimatic, biospeleologic studies (Gaál et al., 2015). Research in Hungarian caves is undertaken by the Hungarian Academy of Science in collaboration with the Aggtelek National Park Directorate (Gruber, 2015). The scientific research is increasing, e.g. biological, archaeological and hydrogeological research of the caves (Gruber & Gaál, 2014).
The following examples of important work can be mentioned: study of endemic and relict cave fauna species (Derbák et al., 2018; Červená et al., 2019), biomass production and carbon stocks of above-and below-ground biomass in grassland (Kizeková et al., 2019), lower plants diversity in karstic streams (Czerwik-Marcinkowska et al., 2018; Ogórek et al. 2022), bacterial diversity in soils (Knáb et al., 2018) and geomorphology studies (Hofierka et al., 2018; Bella et al., 2019; Kudla et al. 2024; Gruber et al. 2022). Scientific papers with participation of the Slovak Caves Administration were published on karst morphological features of Aggtelek Karst and Jósva River valley (Bella et. al., 2016) and on geomorphology of the Moldava Cave (Bella et al., 2018). The 12th Scientific Conference on research, utilization and protection of caves at the occasion of the 25th anniversary of the inscription of the Caves of Aggtelek Karst and Slovak Karst on the World Heritage List was held in Slovakia in September, 2020, and there are regular scientific conferences focusing on the property. The possibilities provided by the fragmented karst areas of Hungary and the mosaic-like assembly of the cave fauna are already providing insights to better understand big questions of cave biology (Szinetár et al. 2022).
The following examples of important work can be mentioned: study of endemic and relict cave fauna species (Derbák et al., 2018; Červená et al., 2019), biomass production and carbon stocks of above-and below-ground biomass in grassland (Kizeková et al., 2019), lower plants diversity in karstic streams (Czerwik-Marcinkowska et al., 2018; Ogórek et al. 2022), bacterial diversity in soils (Knáb et al., 2018) and geomorphology studies (Hofierka et al., 2018; Bella et al., 2019; Kudla et al. 2024; Gruber et al. 2022). Scientific papers with participation of the Slovak Caves Administration were published on karst morphological features of Aggtelek Karst and Jósva River valley (Bella et. al., 2016) and on geomorphology of the Moldava Cave (Bella et al., 2018). The 12th Scientific Conference on research, utilization and protection of caves at the occasion of the 25th anniversary of the inscription of the Caves of Aggtelek Karst and Slovak Karst on the World Heritage List was held in Slovakia in September, 2020, and there are regular scientific conferences focusing on the property. The possibilities provided by the fragmented karst areas of Hungary and the mosaic-like assembly of the cave fauna are already providing insights to better understand big questions of cave biology (Szinetár et al. 2022).
Effectiveness of management system and governance in addressing threats outside the site
Management programs are mainly focused on the internal threats. The few threats from outside the site, such as water flow from arable agriculture lands, have not been addressed sufficiently (e.g. polders capturing flood waters) (IUCN Consultation, 2020). A project was prepared for improvement and wise use of the precipitation water including the increase of retention and water regime potential, both of surface and underground territories, however, this has still not been funded (IUCN Consultation, 2020c). Through the Interreg programme 2021-2027 between Hungary and Slovakia, there is opportunity to improve coordinated water management (Interreg, 2023).
Effectiveness of management system and governance in addressing threats inside the site
Protection of the caves appears effective. However, there is some room for improvement (management activities related to surface areas and the cave environment must be well connected). Sharing of economic benefits derived from tourism with local people in area and their involvement could also be improved. Results of management evaluation (Tomaškinová & Tomaškin, 2013) showed a need for more effective management and protection in the Slovak Karst national park area, including in such topics as zoning, cooperation, marketing and PR, communication and involvement of relevant stakeholders and regional development.
Protection and management of karst features is relatively effective in both countries. However, there is still no joint integrated management plan for the transboundary site. The administrative bodies in two countries carry out joint projects including research and monitoring. However, there are some concerns regarding the lack of resources, particularly in Slovakia where the staff numbers and funding are insufficient and remain significantly lower than in the Aggtelek National Park in Hungary. The overlap with other international designations may provide some further opportunities to enhance human and financial capacities and benefit from collaborations on research and monitoring activities. Furthermore, there is still a need to improve the relations with local communities. Reports indicate that local residents feel they have only a marginal influence on national park decisions.
Remarkable diversity of caves types and important evidence of geologic history
Good
Trend
Stable
More than 99% of the Caves of Aggtelek Karst and Slovak Karst is preserved in its original natural condition and is well protected. The other 1% has been substantially modified as “show-caves” to allow human use, which includes 300,000 visitors annually (World Heritage Committee, 2013). These caves also remain in good condition and monitoring programmes are in place. Overall, in terms of conservation, the karst regions in Hungary are in a relatively favourable situation (Szinetár et al. 2022).
Assessment of the current state and trend of World Heritage values
Stable
More than 99% of the Caves of Aggtelek Karst and Slovak Karst is preserved in its original natural condition and is well protected. The other 1% has been substantially modified as “show-caves” to allow human use, which includes 300,000 visitors annually. These caves are also in good condition and monitoring programmes are in place.
Assessment of the current state and trend of other important biodiversity values
Low Concern
Deteriorating
The state of the site’s above-ground biodiversity is regularly assessed through a comprehensive information and monitoring system within the monitoring of habitats and species of European importance in the Slovak Republic. The conservation status is different for individual species and habitats depending on the impacts and threats (Černecký et al., 2020), however, monitoring results show that two-thirds of animal species and one-third of the plant species in the Slovak Karst national park are in unfavourable-inadequate conservation status (State Nature Conservancy of the Slovak Republic, n.d.). The Hungarian cave biota is threatened by many factors, but the general protection serves as a strong base. There is limited data on species distributions and population sizes (Szinetár et al. 2022). The mouflon (Ovis aries, Linnaeus 1758), introduced to Central Europe 120 years ago, behaves as an invasive species and causes significant damages to the fauna and flora of these shallow soil habitats in Hungary (Szinetár et al. 2022).
Additional information
Outdoor recreation and tourism
Tourism generates considerable economic benefits. About 300,000 tourists visit the caves annually (World Heritage Committee, 2013).
Importance for research,
Contribution to education
Unique natural phenomena (e.g. rareness of ice-filled caves) including archaeological findings and historical monuments served as exemplary study objects for science and education.
Outdoor recreation and tourism
The therapeutic effect of the air in the cave Béke near Jósvafő was recognised very early in history and in 1969 it was officially declared the first therapeutic cave in Hungary. Researchers have recognised the special climate of the cave, which - due to the aspects of hygiene and microbiology - has a therapeutic effect. However, the potential use of caves for therapeutical purposes is currently being further researched, the introductory results are very positive (http://www.skhu.eu/funded-projects/medical-wellness-tourism-development-in-the-world-heritage-caves-of-the-aggtelek-and-slovak-karst).
The site contributes to the national economies through tourism and is also important for science and education. Caves are attractive as ecotourism destinations (Béki et al., 2017) and provide unique opportunities to educate the public about biodiversity values and ecosystem services (water availability or human health).
References
| № | References |
|---|---|
| 1 |
ABR Management Plan (2015). Aggtelek Biosphere Reserve Management Plan. Jósvafő 2015. Available at: https://termeszetvedelem.hu/_user/browser/File/UNESCO/kez_t…
|
| 2 |
Bella, P., Bosák, P., Braucher, R., Pruner, P., Hercman, H., Minár, J., Veselský, M., Holec, J., & Léanni, L., (2019). Multi-level Domica–Baradla cave system (Slovakia, Hungary): Middle Pliocene–Pleistocene evolution and implications for the denudation chronology of the Western Carpathians. Geomorphology, 327, pp. 62-79.
|
| 3 |
Bella, P., Gaál, Ľ., Littva, J., Hochmuth, Z., Haviarová, D. and Soták, J. (2018) Moldavská jaskyňa – horizontálny labyrint vytvorený alochtónnymi vodami Bodvy v kontaktnom krase Medzevskej pahorkatiny. Mineralia Slovaca, 50, Bratislava, 159-178.
|
| 4 |
Bella, P., Gaál, Ľ., Papáč, V., Gruber, P. & Soják, M. (2015). Oustanding values of the WHS “Caves of the Slovak and Aggtelek Karst”. Aragonit 20 (1): 15-23. Slovak Caves Administration, Banská Bystrica, ISSN 1335-213X. http://www.ssj.sk/sk/clanok/448-casopis-aragonit-c-20-1
|
| 5 |
Bella, P., Veselský, M., Gaál, Ľ. and Minár, J. (2016). Jósvafő paleo-polje: morphology and relation to the landform evolution of Aggtelek Karst and Jósva River valley, Hungary. Zeitschrift für Geomorphologie. 60, 3, Stuttgart, 219-235.
|
| 6 |
Bolechová, B., Kršák, B., Sidor, C., & Štrba, Ľ. (2022). Development of Cave Tourism in the Domica Area in Slovakia. https://pea. lib. pte. hu/handle/pea/33844.
|
| 7 |
Béki, P., Lasztovicza, D., & Metzger, J. (2017). Caves, as touristic attractions in Hungary: Adventure, Health, Culture, Ecotourism. Applied Studies in Agribusiness and Commerce, 10, pp.58-51.
|
| 8 |
Czerwik-Marcinkowska, J., Wróblewski, W., Gradziński, M., & Uher, B. (2018). Diatom species diversity and their ecological patterns on different substrates in two karstic streams in the Slovak Karst. Journal of Cave and Karst Studies, 80(3), pp.133-144.
|
| 9 |
Czuppon, G., Demény, A., Leél-Össy, S., Óvari, M., Molnár, M., Stieber, J., Kiss, K., Kármán, K., Surányi, G., & Haszpra, L. (2018). Cave monitoring in the Béke and Baradla caves (NE Hungary): implications for the conditions for the formation cave carbonates. International Journal of Speleology, 47(1), pp. 13-28.
|
| 10 |
Derbák, D., Dányi, L., & Hornung, E., (2018). Life history characteristics of a cave isopod (Mesoniscus graniger Friv.). ZooKeys, 801, pp. 359-370.
|
| 11 |
Gaál, Ľ. & Gruber, P. (2015). World Heritage Caves of the Slovak and Aggtelek Karst. ŠOP SR SSJ Liptovský Mikuláš, Aggteleki NP Jósvafő. 124 pp., ISBN 978-80-89802-01-2.
|
| 12 |
Gaál, Ľ., Bella, P., Haviarová, D., Zelinka, J., Papáč, V., Balciar, I. & Labaška, P. (2015). Research, protection and management of the WH caves in Slovakia: an overview of activities since 1995. Aragonit 20 (1): 24-43. Slovak Caves Administration, Banská Bystrica, ISSN 1335-213X. http://www.ssj.sk/sk/clanok/448-casopis-aragonit-c-20-1
|
| 13 |
Gessert, A., Straková, V., Palcsu, L., Koltai, G., Braun, M., Heim, E., & Czébely, A. (2019). Differences in temporal changes of selected water quality parameters on Jasovská Planina Plateau (Slovak Karst, Slovakia). Geographia Cassoviensis XIII(1), pp. 5-20.
|
| 14 |
Gruber, P. & Gaál, L. (2014). Domica-Baradla cave system: a cave that connects us. Aggtelek NP Igazgatóság, Jósvafő. 512 pp. ISBN 978-615-80050-0-5 (in Hungarian and in Slovakian).
|
| 15 |
Gruber, P. (2015). Research, protection and management of inorganic nature in the Aggtelek Karst: 20-years´ retrospective. Aragonit 20 (1): 44-52. Slovak Caves Administration, Banská Bystrica, 76 pp. ISSN 1335-213X. http://www.ssj.sk/sk/clanok/448-casopis-aragonit-c-20-1
|
| 16 |
Gruber, P., Szunyogh, G., & Telbisz, T. (2022). The Caves of Aggtelek Karst, Szalonna Karst and Rudabánya Mountains. In Cave and Karst Systems of Hungary (pp. 275-321). Cham: Springer International Publishing.
|
| 17 |
Hofierka, J., Gallay, M., Bandura, P., & Šašak, J., (2018). Identification of karst sinkholes in a forested karst landscape using airborne laser scanning data and water flow analysis. Geomorphology, 308, pp. 265-277.
|
| 18 |
IUCN (2000). World Heritage nomination – IUCN technical evaluation. Caves of the Aggtelek Karst and Slovak Karst (Hungary / Slovakia). Extension to include Dobšinská Ice cave (Slovakia), pp. 107-113. pp.1-56. Available at: https://whc.unesco.org/document/154115. [Accessed 21 May 2020].
|
| 19 |
IUCN Consultation (2020a). IUCN World Heritage Confidential Consultation form: Respondent 1. Caves of Aggtelek Karst and Slovak Karst (Hungary / Slovakia).
|
| 20 |
IUCN Consultation (2020b). IUCN World Heritage Confidential Consultation form: Respondent 2. Caves of Aggtelek Karst and Slovak Karst (Hungary / Slovakia).
|
| 21 |
IUCN Consultation (2020c). IUCN World Heritage Confidential Consultation form: Respondent 2. Caves of Aggtelek Karst and Slovak Karst (Hungary / Slovakia).
|
| 22 |
Interreg (2023). Interreg programme Hungary-Slovak Republic. Available at: https://www.skhu.eu/cmsadmin/asset/preview?id=619f621cf7c31…
|
| 23 |
Jovicic, V., Volk, B., Vesel, G., Ratej, J., & Schmidt, M. (2023, October). Tunnelling in Slovenian Dinaric Karst: Challenges and Solutions. In ISRM Congress (pp. ISRM-15CONGRESS). ISRM.
|
| 24 |
Kilík, J. and Balážová, A. (2020). Slovak Karst Biosphere Reserve. State Nature Conservancy of the Slovak Republic Administration of the Slovak Karst National Park and Biosphere Reserve. Available at: https://worldprotectedareas.sopsr.sk/wp-content/uploads/202…
|
| 25 |
Kizeková, M., Kanianska, R., Jančová, Ľ., Čunderlík, J., Dugátová, Z., & Makovníková, J. (2019). Above and below ground biomass and carbon stock in permanent grasslands of Slovakia. Agriculture, 65(4), pp.155-163.
|
| 26 |
Knáb, M., Szili-Kovács, T., Márialigeti, K., Móga, J., & Borsodi, A. K. (2018). Bacterial diversity in soils of different Hungarian karst areas. Acta Microbiologica et Immunologica Hungarica, 65(4), pp. 439-458.
|
| 27 |
Kudla, M., Javorská, M., Vašková, J., Čech, V., & Tometzová, D. (2024). Inventory and evaluation of geosites: Case studies of the Slovak Karst as a potential geopark in Slovakia. Sustainability, 16(17), 7783.
|
| 28 |
Ogórek, R., Suchodolski, J., Piecuch, A., Przywara, K., & Višňovská, Z. (2022). Keratinophilic and keratinolytic fungi in cave ecosystems: A culture-based study of Brestovská cave and Demänovská Ľadová and Slobody Caves (Slovakia). Applied Sciences, 12(3), 1455.
|
| 29 |
RIS (2017). Ramsar Information Sheet Hungary Baradla Cave System and related wetlands. RIS for Site no. 1092. Available at: https://rsis.ramsar.org/RISapp/files/RISrep/HU1092RIS_1703_…
|
| 30 |
Slovak Karst National Park (2022). Weekend cleaning of the Slovak Karst National Park. Clean Slovakia – Weekend cleaning of the Slovak Karst National Park. Published online 19 September 2022. Available at: https://www.npslovenskykras.sk/ciste-slovensko-vikendove-ci…
|
| 31 |
Slovak Karst National Park (2025). List of workers. State Nature Conservancy of the Slovak Republic. Available at: https://www.npslovenskykras.sk/kontakt/
|
| 32 |
Slámová, M., Mrázová, M., Hudáková, Ľ., Mikušová, M., Rácz, A., & Slobodník, B. (2024). Parallels of environmentally friendly pastoralism to land cover changes and high nature value farmland. Landscape Research, 49(5), 722-737.
|
| 33 |
State Nature Conservancy of the Slovak Republic (n.d.). Slovak Karst - NP administration Monitoring results. Available at: https://www.biomonitoring.sk/Contacts/SOPOrganizationUnit/D…
|
| 34 |
State Nature Conservancy of the Slovak Republic, Slovak Caves Administration (n.d.). SLOVAK CAVES ADMINISTRATION. Available at: http://www.ssj.sk/en/kontakty
|
| 35 |
State Party of Hungary and Slovakia (2024). Periodic Reporting Cycle 3, Section II: Caves of Aggtelek Karst and Slovak Karst. Available at: https://whc.unesco.org/en/list/725/documents/
|
| 36 |
States Parties of Hungary and Slovakia (2006). Periodic report - First cycle. Section II – Caves of Aggtellek Karst and Slovak Karst, 5 pp. Available at: https://whc.unesco.org/document/162823. [Accessed 21 May 2020].
|
| 37 |
States Parties of Hungary and Slovakia (2014). Periodic report - Second cycle. Section II – Caves of Aggtellek Karst and Slovak Karst, 13 pp. Available at: https://whc.unesco.org/document/164218. [Accessed 21 May 2020].
|
| 38 |
Strukturas (2025). Largest infrastructure construction site in Slovakia for Strukturas MSS. Strukturas. Available at: https://strukturas.no/largest-infrastructure-construction-s…
|
| 39 |
Szinetár, C., Paulovics, P., Csorba, G., & Balázs, G. (2022). The Fauna of Karsts in Hungary. In Cave and Karst Systems of Hungary (pp. 553-577). Cham: Springer International Publishing.
|
| 40 |
Telbisz, T., Gruber, P., Mari, L., Köszegi, M., Bottlik, Z., & Standovár, T., (2020). Geological heritage, geotourism and local development in Aggtelek national park (NE Hungary). Geoheritage, 12(5), pp. 1-18.
|
| 41 |
Telbisz, T., Mari, L., Gessert, A., Dická, J. N., & Gruber, P. (2022). Attitudes and perceptions of local residents and tourists–a comparative study of the twin national parks of Aggtelek (Hungary) and Slovak Karst (Slovakia). Acta Carsologica, 51(1), 93-109.
|
| 42 |
Telbisz, T., Mari, L., Kőszegi, M., Bottlik, Z., Standovár, T., Gruber, P., ... & Stergiou, C. (2023). Park-local people-tourist relationships in karst national parks, the presentation of an international project. Speleologia Iblea–Speleology and Environment Series, 17, 189-194.
|
| 43 |
Tomaškinová, J. & Tomaškin, J. (2013). Integrated management of NP Slovak Karst. Belianum Banská Bystrica, 148 pp. ISBN 978-80-557-0589-7. https://publikacie.umb.sk/prirodne-vedy/environmentalistika…
|
| 44 |
World Heritage Committee (2013). Adoption of retrospective Statements of Outstanding Universal Value. WHC-13/37.COM/8E, pp. 54-55. Available at: https://whc.unesco.org/archive/2013/whc13-37com-8E-en.pdf [Accessed 21 May 2017].
|
| 45 |
Zahorec, P., Papčo, J., Vajda, P., & Szabó, S. (2019). High-precision local gravity survey along planned motorway tunnel in the Slovak Karst. Contributions to Geophysics and Geodesy, 49(2), pp.207-227.
|
| 46 |
Černecký, J., Čuláková, J., Ďuricová, V., Saxa, A., Andráš, P., Ulrych, L., Šuvada, R., Galvánková, J., Lešová, A. & Havranová, I. (2020). Conservation status of hatitats and species of Community interest in the period of 2013 – 2018 in the Slovak Republic. Banská Bystrica: ŠOP SR, 109 pp., ISBN 978- 80-8184-076-0. http://www.sopsr.sk/natura/dokumenty/Monografia_reporting_a…
|
| 47 |
Červená, M., Šťáhlavský, F., Papáč, V., Kováč, Ľ., & Christophoryová, J., (2019). Morphological and cytogenetic characteristics of Neobisium (Blothrus) slovacum Gulička, 1977 (Pseudoscorpiones, Neobisiidae), the northernmost troglobitic species of the subgenus Blothrus in Europe. ZooKeys, 817, pp. 113-130.
|
| 48 |
Šupinský, J., Kaňuk, J., Hochmuth, Z., & Gallay, M., (2019). Detecting dynamics of cave floor ice with selective cloud-to-cloud approach. The Cryosphere, 13, pp. 2835-2851.
|