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Vipera ursinii rakosiensis at the Last Remaining Site for this Subspecies in Romania ............4 Table 1 : Urgent Priority Actions for the Meadow Viper Vipera ursinii ...................................................5 

Vipera ursinii rakosiensis at the Last Remaining Site for this Subspecies in Romania ............4 Table 1 : Urgent Priority Actions for the Meadow Viper Vipera ursinii ...................................................5 

Context in source publication

Context 1
... Cappelluti/Chiara Braschi , Ministero dell’Ambiente e della Tutela del Territorio e del Mare, Rome, Italy Keith Corbett (former Chair of the Conservation Committee of the Societas Europaea Herpetologica, retired), New Zealand Stela Drucioc/V. Turcanu , Ministry of Ecology and Natural Resources, Chisinau, Moldova Jacques Fretey , Société Nationale de Protection de la Nature (SNPN), Paris, France Patrick Haffner , Muséum national d’Histoire naturelle, Paris, France Valerie Georgiev , Ministry of Environment and Water, Sofia, Bulgaria Ioan Ghira , Romanian Herpetological Society, Cluj, Romania Maja Gluhacovi ć , State Institute for Nature Protection, Zagreb, Croatia Alexandru Iftime , “Grigore Antipa” National Museum of Natural History, Bucharest, Romania Eduard Kletecki , Croatian Natural History Museum, Zagreb, Croatia László Krecsák, Eötvös Loránd University, Budapest, Hungary Claude Miaud , Université de Savoie, Le Bourget du Lac, France Katja Poboljsaj , Centre for Cartography of Fauna and Flora (CKFF), Ljubljana, Slovenia Richard Podloucky (Chair of the Group of Experts of the Conservation of Amphibians and Reptiles), Niedersächsischer Landesbetrieb für Wasserwirtschaft, Küsten- und Naturschutz (NLWKN), Hannover, Germany Demetra Spala , Ministry of the Environment, Athens, Greece Anton Stumpel (Chair of the Conservation Committee of the Societas Europaea Herpetologica), Alterra, Green World Research, Waginingen, the Netherlands Jean-Pierre Vacher , Société Herpétologique de France (SHF), Strasbourg, France The European meadow viper was discovered by Count Orsini on the Apennine massif of Gran Sasso in central Italy, and was first formally described by Bonaparte (1835) as Pelias ursinii . Boulenger (1893) subsequently renamed the species Vipera ursinii . After the collection of further specimens in various parts of southern and central Europe, many years of taxonomic debate about the relationships of this species with the other European vipers then followed. To complicate matters further, Vipera ursinii is itself part of a species complex – the closely related meadow and steppe vipers of the Vipera subgenus Acridophaga – so its taxonomy has taken some time to resolve. For much of the 20 th Century, while various authors continued to dispute the arrangement of species and subspecies boundaries, all populations of this complex were simply assigned to Vipera ursinii . A thorough revision of the systematics of the meadow and steppe viper complex was finally undertaken by Nilson and Andrén (2001). As a result, the following subspecies of Vipera ursinii are currently recognised: The first three taxa listed are montane forms, generally occurring between 900 and 3000 m, while the last two are thought to be found mainly in lowland habitats below 800 m. The distribution in Europe of each is shown in Figure 1. The morphological differences between the subspecies are often subtle, and specimens may be difficult to classify without locality information. Although many aspects of their biology and ecology are also similar, these taxa may face quite different conservation problems and political situations in the various range countries and they are therefore treated separately here where appropriate. Many papers that predate Nilson and Andrén (2001) report the occurrence of Vipera ursinii in countries other than those listed above. However, such accounts refer to taxa that, although they are still part of the meadow and steppe viper species complex, are no longer assigned to Vipera ursinii itself. For example, the steppe viper Vipera renardi , which occurs from Eastern Europe to China, has been variously referred to in the literature as a full species, or as the subspecies Vipera ursinii renardi . The same is the case for Vipera anatolica , V. ebneri , V. eriwanensis and V. lotievi , although all have now all been assigned full species status. Such species are therefore disregarded in this Species Action Plan, even if older references or maps indicate that they should have been included. Useful summaries of the taxonomic history of the meadow viper species complex are provided by Böhme (1993) and Mallow et al (2003). It should be noted that the status of Vipera ursinii is still not entirely clear and that further revisions can be expected. 1. Orsini’s meadow viper Vipera ursinii ursinii – alpine areas of southeast France (12 populations currently known) and central Italy (about 20 populations). 2. Balkan meadow viper Vipera ursinii macrops – recorded on various mountains in the Dinaric Alps, along the north west coast of the Balkan Peninsula, in Croatia, Bosnia-Herzegovina, Serbia, Montenegro, the Former Yugoslav Republic of Macedonia and northern Albania. About 20 known locations but more probably exist. May also have reached the mountains of western Bulgaria, where it is now considered to be extinct. 3. Greek meadow viper Vipera ursinii graeca – endemic to the southern Pindos Mountains of north- central Greece where it is has only been recorded from four sites. 4. Hungarian meadow viper Vipera ursinii rakosiensis – formerly occupied a huge lowland range in the Pannonian steppe region, from eastern Austria (where it is now extinct), across the Great Hungarian Plain to western Romania. Now reduced to 12 sites in Hungary and one in Romania. Possibly once found in adjacent lowland steppe areas of Croatia (Slavonia) and Serbia (Vojvodina). 5. Moldavian meadow viper Vipera ursinii moldavica – a few lowland areas of eastern Romania (one site in Moldavia and three in the Danube Delta) and possibly still survives in the Republic of Moldova. Recorded from lowland areas of northeast Bulgaria, where it is now thought to be extinct. E – Meadow viper populations currently considered to be extinct ? – Continued survival of meadow viper populations unconfirmed 2.2.1. Morphology. Vipera ursinii is the smallest European viper (Arnold 2002). Adults have short, moderately slender bodies and normally attain a total length of approximately 400-450 mm, occasionally reaching 550 mm. The record length is 630 mm for a Hungarian meadow viper, Vipera ursinii rakosiensis (Street 1979), although Gruber (1989) reports that this species can reach 800 mm. Females are generally larger than males (Bruno 1985) and were found to be significantly so in Italy (Filippi and Luiselli 2003) and Hungary (Újvári et al 2000). The tail is very short compared to many other snakes and is proportionally longer in males. The body scales are strongly keeled on the dorsum, although less so on the sides. The somewhat oval, obtusely pointed head of Vipera ursinii , which is slightly narrower in males (Street 1979), is not particularly distinct from the neck and shows no evidence of a nose horn. The very small eyes have the typical vertical pupils of vipers. 2.2.2. Colouration. Vipera ursinii differs from many other vipers in that sexual dimorphism in its colouration is absent (L. Krecsák pers. com. ), or is at least much less evident (Street 1979; Shine and Madsen 1994). The grey or brownish ground colour is usually lighter dorsally and there is also a dark wavy band along the back of most individuals. This is black, brown or reddish and often has a narrow black border down either side. However, this marking does not form such a pronounced dorsal zigzag as in many other Vipera species and, in some specimens, may even be broken up into a series of elliptical or rhomboidal patches along the back. There are dark spots along the sides of the body and dark stripes extend backwards from the eyes to the side of the neck. There is usually a dark Λ , X or even H shaped marking on the back of the head, along with a few symmetrical dark patches. The pale coloured lip scales may be marked with black or brown. The underside of meadow vipers can be either pale or dark, ...

Citations

... Grassland vipers often live in small, isolated populations, which makes them sensitive to habitat fragmentation and degradation (Mizsei et al. 2018). Although certain ESUs of grassland vipers are not considered threatened, as their IUCN Red List status is Least Concern, the majority of these taxa face varying levels of extinction risk, ranging from vulnerable to critically endangered (Edgar and Bird 2005, Göçmen et al. 2017, Mizsei et al. 2018. In light of the current predictions of climate change outcomes, cold-climate-adapted Mediterranean reptiles, including V. ursinii, V. walser, and V. graeca, are the most threatened snakes in Europe (Araújo et al. 2006, Carvalho et al. 2010, Martínez-Freiría 2015, Mizsei et al. 2021). ...
Article
The thermal tolerance of ectotherms is a critical factor that influences their distribution, physiology, behaviour, and, ultimately, survival. Understanding the factors that shape thermal tolerance in these organisms is, therefore, of great importance for predicting their responses to forecasted climate warming. Here, we investigated the voluntary thermal maximum (VTmax) of nine grassland viper taxa and explored the factors that influence this trait. The small size of these vipers and the open landscape they inhabit render them particularly vulnerable to overheating and dehydration. We found that the VTmax of grassland vipers is influenced by environmental temperature, precipitation, short-wave flux, and individual body size, rather than by phylogenetic relatedness. Vipers living in colder environments exhibited a higher VTmax, contradicting the hypothesis that environmental temperature is positively related to VTmax. Our findings emphasize the importance of considering local to regional adaptations and environmental conditions when studying thermal physiology and the evolution of thermal tolerance in ectotherms.
... The populations of V. u. rakosiensis and V. u. moldavica are known to be the smallest and most threatened ones within V. ursinii (Nilson and Andrén, 2001;Edgar and Bird, 2005;Halpern, 2007). The use of highly polymorphic markers like microsatellites allowed us to evaluate the genetic diversity between most V. ursinii subspecies, and even compare it to geographically close populations of V. renardi. ...
Article
Full-text available
The Meadow and Steppe viper, Vipera ursinii-renardi complex is a well-studied group that is divided into several morphological subspecies. In this study, we combine the analyses of two mitochondrial genes with 9 microsatellite markers to compare both phylogenetic signals. Whereas the signal is similar between both genomes within most subspecies, the relative relationships between subspecies are more differentiated. Moreover, the nuclear phylogenetic reconstruction supports genetic homogeneity within V. u. macrops (in contrast to mtDNA). Both genetic portions show an unexpected differentiation between a population from Bistra Mountain and other V. u. macrops populations. Globally, the microsatellite markers suggest high genetic diversity in most subspecies, even in V. u. rakosisensis which is highly threatened; only V. u. macrops showed a limited genetic diversity. Within lowland subspecies, the differentiation between populations is globally limited compared to the distance between them (except in some populations of V. u. moldavica). The limited differentiation might be the consequence of a recent isolation (few decades) of previously large populations. Nevertheless, the only way to maintain this genetic diversity and to avoid an increase in genetic differentiation between populations in the future is to recreate suitable habitats and reconnect the populations.
... Misinformation and negative public perception have led to the wholesale slaughter of venomous pit vipers across North America and Europe. Events such as Rattlesnake and copperhead roundups in the US (Adams et al., 1994;Fitch, 1998;Burghardt et al., 2009), and the killing of individual snakes, such as the meadow viper (Vipera ursinii), the Cyperian Blunt-nosed Viper (Macrovipera lebetina lebetina), and the Northern adder (Vipera berus) when they are encountered in Europe (Edgar and Bird, 2006;Stumpel et al. 2015, Julian andHodges, 2019) are examples of direct persecution against viperid species. This widespread persecution continues to take place in both areas, and is a serious conservation concern for many viperid species, despite these species causing very low numbers of fatalities across these two continents (Chip-paux, 2012). ...
Article
Full-text available
Venomous snake species across the globe have been historically categorized as aggressive and dangerous, leading to widespread persecution and killings. Despite the conservation importance of educating the public about the docile nature of these species, few studies have attempted to quantify the response of viperid species to human interactions. Here we report the responses of free-ranging copperheads to a potential human encounter using a set of hierarchical behavioral trials. Out of a total of 69 snakes, only two individuals feigned striking and only two attempted to bite (3% of all individuals). Our results support the findings of previous studies documenting the docile nature of other viperid species and can hopefully be used to change the public perception of venomous snakes. Convincing the public and policy makers that viperid species are docile is critical to long-term conservation of these species in the U.S. and around the globe.
... In fact, road construction in grasslands leads to the segregation and subsequent isolation of small sub-populations (Filippi and Luiselli 2004) which is followed by loss of genetic variation, potentially causing local extinctions (Újvári et al. 2002). High densities of European wild boar Sus scrofa, an increase of winter sport activities with the accompanying infrastructures, intentional killings, as well as climate change (which could boost upward shift of tree line, favouring forestation of montane meadows), also continue to threaten meadow viper populations (Filippi and Luiselli 2004, Edgar and Bird 2005, Joger et al. 2009, Zamfirescu et al. 2011. ...
... Considering all these threats, high attention is addressed to the conservation of the meadow viper in many National and European protected areas (PAs), such as National Parks and Sites of Community Importance (SCI) of the Natura 2000 ecological network. Despite these noticeable conservation efforts, population declines are observed (Újvári et al. 2000, Baillie et al. 2004, Edgar and Bird 2005, Zamfirescu et al. 2012). In the following, we evaluate coverage of PAs of the observed and the potential distribution of this species by means of a large dataset of occurrences. ...
... occurrence records (excluding duplicate occurrences; n = 515) resulted in 94.6% of records falling within the cells reported in the revised distribution of Mizsei et al. (2018): 452 points fall within 'verified' atlas' cells, 28 in the 'new' cells, 0 in 'unverified' cells, 6 in 'historical' cells and 0 in 'errors'. The remaining 6.4% of our dataset was outside from Mizsei et al. (2018) range; indeed, these occurrences, taken from verified bibliographical sources, correspond to extinct populations (Kovács et al. 2002, Edgar andBird 2005). After correcting for spatial autocorrelation, the remaining number of occurrence records were: macrops n = 50, moldavica n = 62, rakosiensis n = 44 and ursinii n = 109. ...
Article
Full-text available
The meadow viper Vipera ursinii includes four subspecies with five allopatric areas of distribution in Europe. It is currently considered one of the most threatened reptile species on the continent, mainly because of its patchy distribution and concurrent habitat loss. Taking advantage of a database composed of occurrence data from bibliographical sources and field observations, we present the first European-scale assessment of the historical knowledge and chronogeonemy of this species. In addition, we evaluate the habitat use and coverage of protected areas with regard to both actual occurrences and modelled potentially suitable areas. This was done for Vipera ursinii s.l. as well as for each of the four subspecies. Our results show different patterns of historical knowledge as well as different degrees of legal protection, depending on the country and subspecies considered. Furthermore, most of the occurrences are from habitats which are classified as vulnerable. A gap analysis reveals an inadequate protection status for modelled areas of potential suitability and a heterogeneous coverage of protected areas, again depending on the subspecies considered. Our findings assist towards a more focused conservation management of all V. ursinii subspecies in the next future, which could take place by connecting landscape-scale research with field studies to update management strategies of protected areas. For these latter, Europe-wide coordinated actions are required to promote plans targeting the same conservation goals.
... 9 The Bern Convention approved a European conservation action plan for the meadow viper in 2005. 8 In Hungary an appropriate species conservation plan exists for the protection of this species and a complex conservation project was initiated, cofunded by European Commission's LIFE and later LIFE+ funds. ...
... Péchy et al., 2015) and France (http://www.vipere-orsini.com/fr/). The Life project in Hungary has incorporated land protection, habitat restoration, creation of a Hungarian meadow viper conservation and exhibition centre, captive breeding and repatriation, monitoring, research, and education outreach to save the Hungarian meadow viper (e.g., Újvári et al., 2000;Edgar and Bird, 2006). Importantly, we propose that our ranking be used to direct similar potential conservation work and research, and help local conservation practitioners motivate for conservation of particular habitats or protection of individual species. ...
... Subalpine-alpine meadow habitats are less affected by habitat alteration, even though many are used for intensive grazing by sheep, cattle and goats. The remaining European populations survive in small, isolated habitat patches that are often suboptimal for long-term persistence (Nilson and Andrén, 2001;Újvári et al., 2002;Filippi and Luiselli, 2004;Edgar and Bird, 2005). ...
Article
Vipera ursinii graeca is a restricted-range, endemic snake of the Pindos mountain range in the southwestern Balkans. The subspecies was previously reported from eight localities in Greece and one locality in southern Albania. We used species distribution modelling based on climate data from known localities in Greece to estimate the potential distribution of the subspecies. The model predicted suitable areas for eleven mountains in southern Albania, which we visited in ten field expeditions in four years. Based on 78 live individuals and 33 shed skins, we validated the presence of the snake on eight of the eleven mountains. Six populations (Dhëmbel, Llofiz, Griba, Shendelli, Tomorr and Trebeshinë Mountains) are reported here for the first time. Morphological characters undoubtedly supported that all individuals found at these new localities belong to V. u. graeca. Genetic analysis of mitochondrial DNA sequences also confirmed the identity of the snakes as V. u. graeca and a low number of identified haplotypes suggested low genetic variability among populations despite significant spatial isolation. All localities were subalpine-alpine calcareous meadows above 1600 m. These high montane habitats are separated by deep valleys and are threatened by overgrazing, soil erosion, and a potential increase in the elevation of the tree line due to climate change. Our surveys increased the number of known populations by 60% and the known geographical range of the subspecies by approximately 30%. Our study serves as a baseline for further ecological research and for conservation measures for one of the least known European viperid snakes.
... The critical state of this taxa has also been recognized internationally and the Hungarian meadow viper is included on the Bern Convention Appendix II [Council of Europe, 1979Europe, (revised 2002], and is listed in Appendix I of the Convention on International Trade in Endangered Species of Wild Flora and Fauna (CITES, 2014) and on the International Union for Conservation of Nature (IUCN) Red List as Endangered (IUCN, 2014). The Bern Convention approved a European conservation action plan for meadow vipers in 2005 (Edgar & Bird, 2005). The Hungarian meadow viper is listed on Annex II of the Habitats Directive [Council of Europe, 1979(revised 2002), 1991; therefore all occurrences were included in the Natura 2000 Network. ...
Article
In order to stop the decline of Hungarian meadow viper Vipera ursinii rakosiensis, in 2004 MME BirdLife Hungary together with national parks and Budapest Zoo started a complex conservation programme, supported by the European Union LIFE-Nature fund. The Hungarian Meadow Viper Conservation Centre was established with 16 adult individuals, collected from six different populations. By 2013 the number of vipers bred reached c. 1700 individuals. First reintroductions took place in March 2010, with 30 adult snakes released into a reconstructed habitat in Kiskunság National Park. By 2013, a total of 240 snakes had been released into three locations. Snakes were released by relocating the animals in the artificial burrows they used in the semi-natural terrariums at the Hungarian Meadow Viper Conservation Centre. At the release sites vipers were recorded 255 times during post-release monitoring, and 69 individuals were identified. Eighteen of the observed ♀♀ were gravid, and ten juvenile or subadult individuals were documented. In order to develop a remote-tracking method, pre-programmed radio-tags with a detection range of 200–300 m were surgically implanted into the abdomens of 16 vipers. These tags also operated as temperature loggers, recording data every 5 minutes for one year. Zoos play an important role in communicating the results of this captive-breeding and release programme. Exhibits of live Hungarian meadow vipers are located at Budapest Zoo and Schönbrunn Zoo in Vienna, Austria, and there are information points about the species located in all Hungarian zoos.
... The Orsini's meadow viper, a European endemic species, is considered one of the most threatened snakes in Europe (Edgar & Bird, 2007). It is classified as 'vulnerable' by the World Conservation Union (IUCN, 2009) and is the subject of a European conservation action plan (Edgar & Bird, 2007) and several European conservation projects (LIFE06NAT/F/ 000143, LIFE04NAT/HU/000116). ...
... The Orsini's meadow viper, a European endemic species, is considered one of the most threatened snakes in Europe (Edgar & Bird, 2007). It is classified as 'vulnerable' by the World Conservation Union (IUCN, 2009) and is the subject of a European conservation action plan (Edgar & Bird, 2007) and several European conservation projects (LIFE06NAT/F/ 000143, LIFE04NAT/HU/000116). This species, which is the smallest European viper, typically lives in dry meadow habitats and has a very atypical diet, feeding mostly on insects (Agrimi & Luiselli, 1992;Baron, 1992). ...
... Eventually, this work would help defining a robust and shared standardized GIS-based method to address some key objectives and priority actions concerning distribution surveys and population and conservation status monitoring as highlighted in the Action Plan for the Conservation of the Meadow Viper (Edgar & Bird, 2007). ...
Article
Full-text available
Aim Snakes are more vulnerable to extinction than many other taxa. Additionally, their secretive behaviour makes it difficult to acquire the baseline ecological knowledge required to reliably evaluate extinction risks. Consequently, the conservation status of snakes has only been assessed for small populations; reliable methods for large‐scale evaluation remain to be tested. In this study, we explored how habitat‐suitability models ( HSM s) could be used to provide relevant information to help assess extinction risks and formulate appropriate conservation strategies for the Orsini's viper ( Vipera ursinii ), a rare, endangered snake species. Location Provence‐Alpes‐Côte d'Azur region in south‐eastern France ( c . 30,000 km²). Methods We developed a high‐resolution HSM (50 × 50 m) using a large sample of species presence data and nine climatic and land cover predictors. We used this model to predict the potential distribution of the Orsini's viper as well as to investigate the main environmental drivers explaining this distribution. We also assessed the geographical barriers between local populations and tested whether forest cutting would reduce fragmentation. Results The occurrence of the Orsini's viper was strongly correlated with the annual cumulative temperature and with vegetation cover type. The total extent of suitable habitat covered 2.98% of the study area and was highly fragmented into 1417 distinct areas. Among these areas of suitable habitat, 21 were confirmed to have the species. These represented 22,134 ha and a potential carrying capacity of 168,000 individuals. Main conclusions Our HSM was consistent with the past assessment of the distribution of the Orsini's viper. Our HSM represents a sound benchmark for the distribution of the species and can provide a powerful tool to help with the search of new populations, the identification of areas for habitat restoration, the test conservation strategies and effects of climate change. We found that forest cutting may lead to reconnect close isolated areas of suitable habitat.
... Remaining small and fragmented populations became vulnerable and small, local catastrophes could fully destroy them (Nilson & Andrén, 2001;Újváry et al., 2001). A Population and Habitat Viability Assessment organized by IUCN Captive Breeding Specialist Group and Budapest Zoo in 2001, the approved Species Conservation Plan (Dankovics et al., 2004) and the European Action Plan (Edgar & Bird, 2005) all came to the conclusion that complex conservation effort is needed with inclusion of additional elements to ongoing conservation measures, like habitat reconstruction and enlargement and captive breeding and re-introduction. . The set of actions implemented in the conservation program can be categorized into four major groups: monitoring of the species and its habitats; defragmentation and enlargement of recent habitats through grassland reconstruction; captive breeding and re-introduction of the species; information of the public and public awareness campaign (Halpern, 2007). ...