The current distribution of pond slider Trachemys scripta (Reptilia: Emydidae) in Croatia Toni KOREN*, Ana ŠTIH, Ivona BURIĆ, Katarina KOLLER, Boris LAUŠ, Mladen ZADRAVEC Asssociation Hyla, Lipovac I. no 7, HR-10000 Zagreb, Croatia; E-mails: toni.koren@hhdhyla.hr, ana.stih@hhdhyla.hr, ivona.buric@hhdhyla.hr, katarina.koller@hhdhyla.hr, boris.laus@hhdhyla.hr, mladen.zadravec@hhdhyla.hr *Corresponding author Abstract. The pond slider Trachemy scripta was one of the most commonly exported turtles until the last decade and often released into the wild outside its native range. It was introduced to Europe, Africa, South America and Asia and included on the EU list of 100 World's Worst Invasive Alien Species and the List of invasive alien species of Union concern. The import of the subspecies Trachemys scripta elegans into Europe and Croatia has been banned for some time, but the number of specimens recorded in nature is still increasing. In this paper we present 45 new localities were the species was observed in Croatia, which makes a total of 84 known localities. Most of the records, 58%, are in the Continental biogeographical region and the rest in the Mediterranean. It has not yet been recorded for the Alpine biogeographical region. Most records (42%) come from ponds. Three new sightings of females digging nests, laying eggs and sightings of hatchlings were recorded, suggesting successful reproduction of the species. Further surveys of this alien species in Croatia are needed. Key words: invasive species, terrapin, Emydidae, Reptilia Izvleček. Razširjenost gizdave želve Trachemys scripta (Reptilia: Emydidae) na Hrvaškem – Gizdava želva Trachemy scripta je bila v zadnjem desetletju ena izmed najpogosteje izvoženih želv iz Amerike in s strani lastnikov pogosto izpuščena v naravno okolje zunaj njene naravne razširjenosti. Vnesena je bila v Evropo, Afriko, Južno Ameriko in Azijo. Vključena je na Seznam 100 najinvazivnejših tujerodnih vrst sveta in Seznam invazivnih tujerodnih vrst Evropske unije. Uvoz podvrste rdečevratke Trachemys scripta elegans je bil v Evropo in Hrvaško prepovedan, vendar se kljub temu število zabeleženih primerkov v naravi povečuje. V prispevku predstavljamo 45 novih lokalitet, kjer je bila vrsta opažena. Skupno je tako za Hrvaško znanih 84 lokalitet o pojavljanju te vrste. Največ najdb (58 %) je iz kontinentalne geografske regije, preostanek pa iz mediteranske. V alpski geografski regiji vrsta še ni bila potrjena. Večina najdb oz. opazovanj (42 %) je z ribnikov. Poročamo tudi o treh novih opažanjih izvaljenih mladičev ter samic, ki kopljejo gnezdo in odlagajo jajca. Potrebne so nadaljnje raziskave o tej tujerodni invazivni vrsti na Hrvaškem. Ključne besede: invazivne vrste, želve, Emydidae, Reptilia Introduction Invasive species threaten biodiversity and related ecosystem services (Kikillus et al. 2010) and can negatively affect native species through predation, competition and transmission of pathogens (Ficetola et al. 2009). One of the most common invasive species also included on the list of 100 of the World's Worst Invasive Alien Species (Lowe et al. 2000) is the pond slider turtle Trachemys scripta (Thunberg & Schoepff, 1792). It is native to Eastern, Northern and Central America (Ficetola et al. 2009). The three subspecies of pond sliders T. scripta scripta (Schoepff, 1792), T. scripta elegans (Wied, 1838) and T. scripta troostii (Holbrook, 1836) were probably the most commonly traded reptiles in the world up until the last decade (Ficetola et al. 2012). This species has been farmed in large quantities in the southern USA for the last several decades, partially for the global pet trade and partially as food for Asian markets (van Dijk et al. 2017). Pond sliders were very popular owing to their small size, low price and simple requirements (Teillac-Deschamps et al. 2008). Small turtles bought in the pet shops outgrow their enclosures after several years and are usually released into the wild by their owners (Cadi & Joly 2003). In 1975, turtle trade was banned in the USA due to salmonellosis (Williams 2016), after which the baby turtles were sent to markets in Europe and Asia (Cadi & Joly 2003). An estimated 52 million specimens of T. s. elegans were exported from the USA to international markets between 1989 and 1997 (Telecky 2001, Cadi et al. 2004, Scalera 2006). Today, the pond slider is introduced in Europe, Africa, South America and Asia (Cadi et al. 2004). The import of the subspecies T. s. elegans has been banned in the European Union from 1997 via the Protection of Species of Wild Fauna and Flora by Regulating Trade (Anonymous 1997) due to their invasive character and impact on native species (Anonymous 2014). In 2016, T. scripta was included on the list of invasive alien species that are of concern in the European Union (Anonymous 2016), which means that concrete action at the Union level is required to prevent their introduction, establishment or spread. Trachemys scripta has been introduced into the Balkan Peninsula probably around the 1970’s (Džukić & Kalezić 2004). It is known from several countries in the Balkans, e.g. Slovenia (Krofel et al. 2009, Vamberger et al. 2012), Bosnia and Herzegovina (Jelić & Jelić 2015), Serbia (Scalera 2006, Urošević et al. 2016), Montenegro (Žagar et al. 2013), Bulgaria (Tzankov et al. 2015), and Greece (Scalera 2006, van Dijk et al. 2011). Most records are from urban and peri-urban areas of larger cities (Scalera 2006, Tzankov et al. 2015), while illegal import is still a problem in some areas (Tzankov et al. 2015). Successful reproduction in the wild is known from Slovenia (Vamberger et al. 2012). Today, two subspecies are widely distributed in Croatia: T. s. elegans and T. s. scripta. According to Jelić & Jelić (2015), 39 recorded sites of T. scripta are reported for Croatia. The goal of this paper is to summarize all available knowledge about the current range and reproduction of T. scripta subspecies in Croatia. Materials and methods To assess the current range of the slider turtle in Croatia, all available knowledge about its occurrence, referring to the period between 1999 and 2017 was gathered, including data from published literature, field surveys, as well as the verified records from the public sent to us by social media. Recent field survey data includes both random findings and targeted surveys for the slider and general amphibians and reptiles inventories carried out through approximately 350 days in the field. Water bodies both in/nearby cities and those further away from urban areas were checked. All data refer to the period between 1999 and 2017. The distribution map based on the dataset was made in ArcMap (v. 10.2.2, ESRI), in the WGS84 coordinate system. Based on unique localities, the tentative habitat preference and the affiliation to a particular biogeographical region were calculated. Results and discussion During this survey, T. scripta was observed on 44 new localities (Appendix 1), which in addition to the previous knowledge about its distribution (Jelić & Jelić 2015, Schweiger 2015) amounts to a total of 84 localities within Croatia (Figs. 1, 2). In respect to the biogeographical regions, most localities belong to the Continental biogeographical region, i.e. 49 localities (58%), followed by the Mediterranean region, i.e. 35 (42%). No records of this species are known from the Alpine biogeographical region in Croatia. This is probably due to the much lower number of inhabitants per square kilometre (Nejašmić 2000), corresponding to a very limited number of pet shops both now and in the past few decades. In the Continental biogeographical region, T. scripta is present in the lowlands, including lakes, streams and ponds. The highest altitude where it was observed is in a lake 350 meters above sea level. In the Mediterranean biogeographical region, it is present both on the mainland and the Adriatic islands. The highest record concerns the mainland in a pond 475 meters above sea level. While during the first overview of the species distribution in the country (Jelić & Jelić 2015) the species was recorded only on the islands of Krk, Pag and Vir, our records show that it is present also on Veli Brijun, Dugi Otok, Šolta and Korčula. It is hard to say whether these records represent new releases in the last few years or were overlooked during the previous surveys in the country. However, it is probable that the species is present also on other Adriatic islands containing suitable wetland habitats. Figure 1. Map with all visited localities and those at which the presence of Trachemys scripta was confirmed. Slika 1. Zemljevid z vsemi obiskanimi lokalitetami in tistimi, na katerih je vrsta Trachemys scripta potrjena. Figure 2. Map with new and previously published localities of Trachemys scripta in different biogeographical regions of Croatia. Slika 2. Zemljevid z novimi in žeobjavljenimi lokalitetami vrste Trachemys scripta v različnih biogeografskih regijah Hrvaške. NATURA SLOVENIAE 20(1): 33-44 Most specimens were observed in ponds, 35 (42%), followed by lakes, 23 (27%), streams, 12 (14%), rivers, 7 (8%), fountains, 5 (6%), and channels 2 (2%). Specimens are often visible in the ponds, floating and basking in the sun, or sometimes even actively swimming towards the observer, expecting to be fed. This corresponds to the data elsewhere from Europe, where T. scripta are generally released in freshwater areas, which are frequented by humans, such as public ponds and other natural habitats close to urban areas (Bringsoe 2006). 72% of the localities with pond sliders in Croatia and Bosnia and Herzegovina are 15 km or less away from the cities that have more than 10,000 inhabitants (Jelić & Jelić 2015). Trachemys scripta has a total range of about 2–3 km, therefore their presence in the isolated ponds, e.g. more than several kilometres apart, especially in the Mediterranean part of the country, somewhat limits their propagation potential, and the potential for spreading to different habitats (Ryan et al. 2008). On the other hand, specimens released in streams and rivers are most likely to be unnoticed during surveys and are expected to spread and colonize new habitats since their reproduction is predicted to be successful due to similar climate like in Slovenia (Zaninović 2008). The aquatic habitats in which T. scripta was recorded during this study do not necessarily indicate the species’ real habitat preference, but they may indicate the habitats on which the individuals can successfully overwinter, due to its adaptability (Cadi & Joly 2004), and as such, they are crucial for further surveys of this species in the country. Not all T. srcipta populations are reproductively active. So far, successful reproduction in Europe has been reported from Spain (De Roa & Roig 1997, Martínez-Silvestre 1997, Pleguezuelos 2002, Perez-Santigosa 2008), France (Cadi et al. 2004), Italy (Sindaco et al. 2005), Slovenia (Vamberger et al. 2012, Standfuss et al. 2016) and Austria (Kleewein 2014). Egg-laying females and hatchlings were also observed from the Mediterranean region of Turkey (Çiçek & Ayaz 2015). For Croatia, egg laying was for the first time reported in 2013 from the Continental biogeographical region, specifically from Maksimir Forest Park, Zagreb, while few years later, successful reproduction was confirmed on the same location by monitoring of few nests in nature and recording successful hatching (Jelić et. al 2016). Aside from Maksimir Forest Park, egg laying female was also observed on another location in Zagreb, on the shore of Bundek Lake in June 2017 (Dubravko Dender, personal communication). The first indication of breeding in the Mediterranean biogeographical region was stated in Schweiger (2015) for the island of Krk. The author observed a single one year old hatchling. A couple of years earlier, one female was observed digging a hole (Boris Lauš, pers. obs. in 2012), but the location was never again checked to see if eggs were actually laid. In Medulin, Istria, small hatchlings of T. s. elegans were observed in 2015 by the first and second authors in the pond inhabited by more than ten adult specimens. It is most likely that the specimen was hatched in the area. Also, on Dugi Otok Island, near the pond where 6 adult specimens were found, the second author observed one female digging a hole, but no eggs were later found there. While the only evidence of the complete breeding success remains that from the lakes at Maksimir Forest Park (Jelić et al. 2016), it is highly probable that successful breeding can also occur in other parts of Croatia, and in different biogeographical regions. Recently, from a population genetics approach based on 14 highly polymorphic microsatellite loci, the breeding of this species was confirmed at three localities in two different regions of Slovenia (Standfuss et al. 2016), which are similar to the climate conditions of Croatia. Bringsoe (2001) suggested that in northern Europe the climate is too cold, while in the Mediterranean region summers are too dry for successful egg development. But the increasing number of the countries, where reproduction was confirmed, indicates that this is not the case (Jelić et al. 2016, Schweiger 2015, Vamberger et al. 2012, Standfuss et al. 2016). The concerning fact in Croatia is that the number of new localities for this species increased by almost 100% in the last several years. Additionally, in some areas like the pond Sali on Dugi Otok Island or the pond in Medulin (Istria), many adult specimens were observed, and it is possible that they will indeed start to reproduce in the future, if they have not done so already, since this is already known from other Mediterranean regions (Standfuss et al. 2016). Due to the longevity of this species, which may be up to 30 years in the wild (van Dijk et al. 2017), even if for some reason reproduction does not occur, they have still been, and will be, present in the wild for many years. Adults are resistant and can survive long periods in suboptimal areas with low temperature or limited precipitation (Bringsoe 2001). Specimens kept in captivity quickly outgrow their small starter aquariums and become unruly for handling, especially in small apartments in the cities. Consequently, they are still being released into the wild even today. In Croatia, specimens of both T. s. elegans and T. s. scripta cannot be bought from pet stores any more, but they are available on the internet for sale, especially specimens older than ten years, or people just give them away for free on different internet portals. In Croatia, two species of native freshwater turtles occur, Emys orbicularis (Linnaeus, 1758) and Mauremys rivulata (Valenciennes, 1833). Both species are listed in the Red Book of Amphibians and Reptiles of Croatia, E. orbicularis as NT (Near threatened) and M. rivulata as EN (Endangered) (Jelić et al. 2012). Pond sliders may compete with the native pond turtle E. orbicularis for food, egg-laying sites, or basking places (Bury & Wolfheim 1973, Rovero et al. 1999, Lindeman 1999, Cadi & Joly 2003), and can be infested with various pathogens, which have been shown to cause mass mortalities in native species (Iglesias et al. 2015). Some authors consider positive competition with the pond turtle in Europe (Luiselli et al. 1997, Cadi & Joly 2003). The competition with M. rivulata has still not been confirmed, but is probably similar as with E. orbicularis, given that in southernmost Croatia, for example, all three species are found in the same habitats. In conclusion, the known distribution of the pond slider in Croatia has been greatly expanded. Additional breeding activities have also been observed. In light of that, it is necessary to continue the survey of this invasive species in Croatia and create a plan for the future removal of this species from the wild. Acknowledgements We wish to thank all those that have sent their observations of T. scripta in Croatia: Hrvoje Škrlin Vučina, Željko Vasilik, Željko Krpan, Stjepan Mekinić, Frano Barišić, Pavao Dragičević, Jure Skejić, Tena Boroš, Paula Dvorski and Berislav Horvatić. 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Seznam novih najdb vrste Trachemys scripta na Hrvaškem. T.s.e. – Trachemys scripta elegans, T.s.s. – Trachemys scripta scripta. Locality name N (WGS84) Co E (WGS84) ntinental bio Dates Eleva­tion (m) No. of indivi­duals Observer Sub­species geographical region Muhamed 1 2 Rakitje, Rakitje Lake Ivanja Reka, Sava River 45.793196 45.787931 15.829403 16.116482 28.3.2010 2017 115 95 1 1 Kovačević, Ivan Špelić Hrvoje Škrlin Vučina T.s.e. T.s.e. 3 Zagreb, Bundek park, Bundek Lake* 45.785267 15.984014 1.8.2009, 28.7.2012 111 / Željko Vasilik, Boris Lauš T.s.e. 4 Zagreb, Staglišće, 45.785002 15.932071 29.6.2008 116 2 Boris Lauš T.s.e. stream 5 Zagreb, Savica Lakes* 45.776765 16.026599 13.4.2013, 2017 109 2 Boris Lauš, Damir Plačko T.s.e. 6 Zagreb, Jarun Lake* 45.776496 15.927268 1.8.2009, 2017 112 / Boris Lauš, Bojan Šmid T.s.e. 7 Zagreb, Turopolje, stream 45.685480 16.147839 8.4.2017 106 1 Jure Skejić T.s.e. Zagreb, Poljana 8 Čička, Odra, Kosnica 45.669200 16.177200 12.4.2017 100 1 Ivona Burić T.s.e. Stream 9 Zagreb, Turopolje, Sava-Odra Canal 45.668340 16.196176 9.4.2017 100 1 Mladen Zadravec T.s.e. 10 Nature Park Kopački rit, channel »Čonakut« 45.605519 18.801251 6.3.2017 83 1 Katarina Koller Šarić, Hrvoje Domazetović T.s.s. 11 Sisak, north pond 45.496579 16.381176 17.6.2015 96 / Željko Vasilik T.s.e. 12 Sisak, middle pond 45.495000 16.382000 12.4.2015 96 / Željko Vasilik T.s.e. 13 Sisak, former brickworks 45.494013 16.379434 29.5.2014 96 1 Željko Vasilik T.s.e. 14 Sisak, south pond in Ciglarska Graba 45.492534 16.384019 11.4.2017 96 1 Željko Vasilik T.s.e. 15 Karlovac, Novi centar, pond 45.486971 15.541010 2017 110 100 Željko Krpan T.s.e. Duga Resa, bridge 16 across the Mrežnica 45.445734 15.505172 17.6.2008 124 2 Boris Lauš T.s.e. River 17 Požega, fishpond Eminovci 45.347513 17.722460 28.6.2014 152 1 Frano Barišić unknown 18 Vinkovci, Banja Lake 45.288317 18.785394 20.4.2012 77 1 Pavao Dragičević T.s.e. 19 Slavonski Brod, Svilaj, pond 45.119985 18.286853 20.8.2015 80 1 Frano Barišić unknown Muhamed 20 Rakitje, Rakitje Lake 45.793196 15.829403 28.3.2010 115 1 Kovačević, T.s.e. Ivan Špelić Eleva-No. of N E Sub- Locality name Dates tion indivi-Observer (WGS84) (WGS84) species (m) duals Ivanja Reka, Sava Hrvoje Škrlin 21 45.787931 16.116482 2017 95 1 T.s.e. River Vučina Zagreb, Bundek 1.8.2009, Željko Vasilik, 22 45.785267 15.984014 111 / T.s.e. park, Bundek Lake* 28.7.2012 Boris Lauš Zagreb, Staglišće, 23 45.785002 15.932071 29.6.2008 116 2 Boris Lauš T.s.e. stream Zagreb, Savica 13.4.2013, Boris Lauš, 24 45.776765 16.026599 109 2 T.s.e. Lakes* 2017 Damir Plačko 1.8.2009, Boris Lauš, 25 Zagreb, Jarun Lake* 45.776496 15.927268 112 / T.s.e. 2017 Bojan Šmid Zagreb, Turopolje, 26 45.685480 16.147839 8.4.2017 106 1 Jure Skejić T.s.e. stream Zagreb, Poljana 27 Čička, Odra, Kosnica 45.669200 16.177200 12.4.2017 100 1 Ivona Burić T.s.e. Stream Zagreb, Turopolje, Mladen 28 45.668340 16.196176 9.4.2017 100 1 T.s.e. Sava-Odra Canal Zadravec Katarina Nature Park Kopački Koller Šarić, 29 rit, channel 45.605519 18.801251 6.3.2017 83 1 T.s.s. Hrvoje »Čonakut« Domazetović Mediterranean biogeographical region 30 Sisak, north pond 45.496579 16.381176 17.6.2015 96 / Željko Vasilik T.s.e. Istra, Kmeti, south 31 of village St. Lucija, 45.443020 13.588106 19.5.2014 50 1 Toni Koren unknown pond Istra, Anžići village, 32 45.255762 13.762086 10.7.2014 273 1 Ana Štih unknown Korneda Pond Istra, Pazin, Pazinčica Stream, 33 45.245253 13.937681 10.4.2009 257 1 Toni Koren unknown near the water pump Istra, Loborika, 34 44.923264 13.924587 9.7.2014 136 1 Ana Štih unknown Gornji Radeki, pond Istra, Mandalana Toni Koren 35 pond, 1 km west of 44.952108 13.977462 21.6.2014 84 1 unknown Ana Štih Cveki Istra, Veli Brijun 36 44.914626 13.769662 3.5.2014 11 1 Željko Vasilik T.s.e. Island, Brijun Pond Istra, Pula, Medulin, Toni Koren, 37 44.818990 13.942461 23.6.2014 9 10 T.s.e. pond Ana Štih Krk Island, Omišalj, 38 Njivice, lake near 45.170710 14.556338 2.6.2012 15 1 Boris Lauš T.s.e. Njivice Krk Island, two Berislav ponds near Horvatić, 39 Mediterranean 45.161753 14.604901 2009 18 1 T.s.e. Mario mussels farm in Schweiger Čižići Eleva-No. of N E Sub- Locality name Dates tion indivi-Observer (WGS84) (WGS84) species (m) duals Dugi Otok Island, Toni Koren, T.s.e., 40 43.929614 15.165853 4.5.2015 43 6 Sali, Sali Pond Ana Štih T.s.s. Ivona Burić, Šibenik, fountain Marko Blažić, 41 near the »Gospe van 43.734048 15.894212 13.6.2015 15 8 T.s.e. Katarina Grada« church* Koller Dicmo, Dicmo 42 Osoje, near St. 43.628917 16.592802 17.4.2009 346 1 unknown T.s.e. Jakov church, pond Split, Jadro, Jadro Stjepan 43 43.541800 16.519100 20.4.2016 17 1 unknown River Mekinić Cista Provo, Stjepan 44 43.515190 16.927096 22.6.2014 476 1 unknown Crljivica, pond Mekinić Stobreč, Žrnovnica, Stjepan 45 43.513400 16.538600 5.6.2014 5 1 unknown stream Mekinić Stjepan 46 Gornji Sevid, pond 43.509144 16.057949 1.5.2015 140 1 unknown Mekinić Ivona Burić, Šolta Island, Srednje 19.8.2014, Mak 47 43.388104 16.281494 97 1 unknown Selo, pond 28.04.2017 Vujanović, Ana Štih Ana Štih, Korčula Island, 48 42.932672 16.712419 9.6.2017 140 1 Mak T.s.s. Gornja Potirna, pond Vujanović Ana Štih, T.s.e., 49 Donji Majkovi, pond 42.773538 17.912024 19.8.2016 222 4 Toni Koren T.s.s. Dubrovnik, city park, 50 42.656262 18.074957 10.10.2017 18 1 Toni Koren unknown fountain 42.672073 51 Rožat, Ombla river 18.131111 13.08.2015. 0 1 Ana Štih unknown Konavle, Pridvorje, 52 42.552551 18.327373 27.5.2014 63 1 Toni Koren T.s.s. pond * already published localities (Jelić & Jelić 2015, Schweiger 2015, Štih & Koren 2014)