Knowl. Manag. Aquat. Ecosyst.
Number 418, 2017
Topical issue on Crayfish
|Number of page(s)||5|
|Published online||13 January 2017|
First record of the spiny-cheek crayfish (Orconectes limosus) in Slovenia – 300 km upstream from its known distribution in the Drava River
Premier enregistrement de l'écrevisse américaine (Orconectes limosus) en Slovénie – 300 km en amont de sa distribution connue dans la rivière Drava
Centre for Cartography of Fauna and Flora,
⁎ Corresponding author: email@example.com
The spiny-cheek crayfish Orconectes limosus (Rafinesque, 1817) is one of the most problematic invasive crayfish species in Europe. Here we report the first occurrence of spiny-cheek crayfish in Slovenia, 300 km upstream from the previously known records in the mouth of Drava River in Croatia. The species was not expected to colonize this area for at least two decades. This new isolated population will significantly alter our predictions of the ongoing colonization of the Drava River basin in Austria, Slovenia and Croatia.
L'écrevisse américaine Orconectes limosus (Rafinesque, 1817) est l'une des espèces d'écrevisses invasives les plus problématiques en Europe. Nous rapportons ici la première occurrence de l'écrevisse américaine en Slovénie, 300 km en amont des sites précédemment connus dans l'embouchure de la Drava en Croatie. L'espèce n'était pas censée coloniser cette zone pendant au moins deux décennies. Cette nouvelle population isolée modifiera considérablement les prédictions de la colonisation en cours du bassin de la Drava en Autriche, en Slovénie et en Croatie.
Key words: non-indigenous crayfish / Slovenia / freshwater invasion
Mots clés : écrevisse non indigène / Slovénie / invasion
© M. Govedič, Published by EDP Sciences 2017
This is an Open Access article distributed under the terms of the Creative Commons Attribution License CC-BY-ND (http://creativecommons.org/licenses/by-nd/4.0/), which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited. If you remix, transform, or build upon the material, you may not distribute the modified material.
Various crayfish species have been introduced outside their indigenous ranges mainly in the last century. Until very recently, Slovenia was one of the few European countries that had avoided non-indigenous crayfish species' introductions. Before 2000 only indigenous freshwater crayfish species existed in Slovenia: the noble crayfish (Astacus astacus), the stone crayfish (Austropotamobius torrentium) and the white-clawed crayfish (Austropotamobius pallipes). Two non-indigenous species were first discovered during this century: the signal crayfish (Pacifastacus leniusculus) and the redclaw crayfish (Cherax quadricarinatus). The presence of signal crayfish is considered to be the consequence of its spread from Austria (Pöckl, 1999). It has also been confirmed as a crayfish plague carrier (Kušar et al., 2013; Maguire et al., 2016). A local redclaw aquaculture is most likely the origin of the redclaw population (Jaklič and Vrezec, 2011). Due to the distribution of other non-indigenous crayfish species in neighbouring countries (Maguire et al., 2011; Kouba et al., 2014) and their colonization speed, we also predict the arrival of the red swamp crayfish (Procambarus clarkii) in the near future in western parts of Slovenia, near to the Italian border.
The spread of non-indigenous spiny-cheek crayfish in Europe has been very fast. This species has been reported from 22 European territories so far (Kouba et al., 2014). After quickly spreading downstream along the Danube River spiny-cheek crayfish started to spread much slower into its tributary, the Drava River (Hudina et al., 2009). Puky and Schád (2006) expected that upstream sections of the Drava River in Hungary will be colonised by spiny-cheek crayfish within 5–10 years. The rate of upstream dispersal in the Drava River is less than 2.5 km yr−1 (Hudina et al., 2009). Lipták and Vitázková (2014) in their analysis of dispersal trends did not include Slovenia in maps of expected distribution in forthcoming years. As upstream spread of the crayfish can be halted by different barriers (Rosewarne et al., 2013), further expansion of its distribution area towards Slovenia is also expected to be limited due to presence of three large dams in this part of the Drava River. The arrival of spiny-cheek crayfish, that was recently confirmed as a crayfish plague carrier also in Croatia (Maguire et al., 2016), was not expected in Slovenia for at least another two decades.
The Drava River is the fourth largest and longest tributary of the Danube River. Run-off hydroelectric stations were built in Austria and upper Slovenia. In lowland parts of Slovenia and Croatia relatively large and not-very-deep reservoirs were built, whereas hydroelectric power stations have been constructed on side channels (Bonacci et al., 1992). That completely altered the hydrological and ecological regime of the Drava River.
Spiny-cheek crayfish were first found in Slovenia on 25.8.2015 (Fig. 1). They were found by chance during an electrofishing survey in an area of small abandoned gravel pits and oxbow lakes in the floodplain of the Drava River south east of Ptuj (Lat: 46° 22′ 31.50″, Lon: 15° 56′ 43.81″). In a 15 ha area, there are 3 gravel pits (0.1–0.2 ha) and 4 oxbow lakes (0.1–0.5 ha). All of them are situated within 200 m of the main river edge; the nearest waterbody is less than 20 m from the main river (Fig. 2). Additional investigations were undertaken using baited traps which were set at all seven waterbodies. Due to inaccessibility manual trapping using a pond net was only possible at one-gravel pit (Tab. 1). All crayfishes were measured (CL – carapace length) and sexed.
A total of 122 crayfish were caught at 4 waterbodies (Tab. 1, Fig. 2). Most of them were caught in one-gravel pit. Specimens ranging from 28 to 49 mm CL were caught during electrofishing, 20–52 mm CL were caught in the traps, while manual search yielded specimens of 20–45 mm CL (Tab. 1, Fig. 3). Catch per unit effort (CPUE – number of crayfish caught per trap per night) varied between water bodies (0.75–3.58). Trap catches were dominated by adult males, which correspond to the findings of Holdich and Black (2007).
The occurrence of the spiny-cheek crayfish in Slovenia is most probably the result of deliberate introductions. All currently known sites of spiny-cheek crayfish are significantly outside of Slovenia (Kouba et al., 2014) and 300 km downstream in the Drava River (Maguire et al., 2011), so the question about its arrival to the country stays open. After Slovenia joined the EU in 2004, it has also opened the possibility of a cross-border online trading of crayfish, which has virtually no control. The area is not generally known as a destination for angling, although it is possible to run into some locals fishing here. There is no guidance information about the use of crayfish as live baits. In Slovenia only earthworms and waxworms can be legally used as live baits for fishing in lakes and rivers. Traditionally live fish, lampreys and mussels were used, but not crayfish. The place where spiny-cheek crayfish were found is easily accessible. I speculate that spiny-cheek crayfish may be present in some other private fishponds, from where it was translocated and introduced into the gravel pit complex next to the Drava River.
In the stretch of the Drava River where spiny-cheek crayfish were found, the hydrological regime is controlled by man-made structures. The discharge is set at 20 m3 s−1 during the summer and 10 m3 s−1 during the winter. There is no water level oscillation after regular rainy days and there are quite stable conditions in the riparian zone of the Drava River. The distance between all examined water bodies and the main Drava River channel is short (Fig. 2) so crayfish can move actively between them. Overland dispersal is a common phenomenon in crayfish and has also been observed in spiny-cheek crayfish (Puky, 2014). During significant flood events all the gravel pits and oxbow lakes in the riparian zone are flooded. Water level oscillation is fast and high. The flood period takes only a few days, but this is the time when spiny-cheek crayfish can more actively disperse between the Drava River channel, oxbow lakes and gravel pits in the flood zone, especially if floods occur during the mating season (Buřič et al., 2009). Floods also increase the probability of crayfish drift downstream in the main river. The newly discovered spiny-cheek crayfish population will have an immediate significant impact downstream and it has altered the predicted spread of this species in the Drava River basin to be much faster than it would have been if colonization occurred by natural upstream dispersal. As this species prefers slow-flowing, larger and warmer rivers (Pöckl, 1999; Petrusek et al., 2006) and shallow parts of lakes (Hirsch et al., 2016) it is expected to spread downstream into the accumulation lakes of the Drava River hydroelectric power plants, where it has the potential to reach high population densities.
The spread of the spiny-cheek crayfish will also affect indigenous crayfish. As spiny-cheek crayfish is a potential vector of crayfish plague, a disease that has devastating effects on indigenous crayfish, thus its presence in the Drava River could lead to the complete elimination of native crayfish populations in the basin. The Noble crayfish and the narrow-clawed crayfish (Astacus leptodactylus) are present downstream in the Drava River in Croatia (Maguire et al., 2011). Interestingly in past two years Croatian researchers did not confirm any noble crayfish 40 km downstream in the Drava River close to Varaždin (Mišel Jelić, pers. comm.). The Stone crayfish populations that are present downstream are also threatened by the spiny-cheek crayfish populations in the tributaries of Drava River in Slovenia and Croatia.
The discovery of this problematic invasive species came as a big surprise. The status and distribution of Slovenia's crayfish populations could soon be impacted detrimentally, due to high dispersal ability of spiny-cheek crayfish in lotic (Buřič et al., 2009) and lentic systems (Hirsch et al., 2016). Eradication options for the introduced spiny-cheek population are being considered. Proposed methods, in particular the use of biocides, are certainly controversial, but have been used effectively elsewhere in the EU to tackle non-indigenous crayfish introductions (Peay et al., 2006). Due to expected spreading there is a need for species monitoring and for careful monitoring of potential contact zones between indigenous and non-indigenous crayfish populations and eliminating the possibility of their contact. There is international border only twelve kilometres downstream so cooperation between Slovenia and Croatia is necessary in this case. As new population presents a new colonization front, the rate of spread might decrease also by its reduction (Moorhouse and Macdonald, 2011).
Electrofishing survey, carried out by Fisheries Research Institute of Slovenia (Danilo Puklavec and Matej Ivenčnik), was a part of a Life project LIVEDRAVA Riparian ecosystem restoration of the lower Drava River in Slovenia (LIFE11 NAT/SI/882). Nino Kirbiš and Eva Žunec helped sampling crayfish and Teja Bizjak helped writing. I also greatly appreciate help from Nick Mott for English language improvements and comments on manuscript. Two anonymous referees made great input.
- Bonacci O, Tadić Z, Trninić D. 1992. Effects of dams and reservoirs on the hydrological characteristics of the Drava River. Regul Rivers 7: 349–357. [CrossRef] [Google Scholar]
- Buřič M, Kouba A, Kozák P. 2009. Spring mating period in Orconectes limosus: the reason for movement. Aquat Sci 71: 473–477. [CrossRef] [Google Scholar]
- Hirsch PE, Burkhardt-Holm P, Töpfer I, Fischer P. 2016. Movement patterns and shelter choice of spiny-cheek crayfish (Orconectes limosus) in a large lake's littoral zone. Aquat Invasions 11: 55–65. [CrossRef] [Google Scholar]
- Holdich D, Black J. 2007. The spiny-cheek crayfish, Orconectes limosus (Rafinesque, 1817) [Crustacea: Decapoda: Cambaridae], digs into the UK. Aquat Invasions 2: 1–15. [CrossRef] [Google Scholar]
- Hudina S, Faller M, Lucić A, Klobučar G, Maguire I. 2009. Distribution and dispersal of two invasive crayfish species in the Drava River basin, Croatia. Knowl Manag Aquat Ecosyst 394 –395: 09. [Google Scholar]
- Jaklič M, Vrezec A. 2011. The first tropical alien crayfish species in European waters: the redclaw Cherax quadricarinatus (Von Martens, 1868) (Decapoda, Parastacidae). Crustaceana 84: 651–665. [CrossRef] [Google Scholar]
- Kouba A, Petrusek A, Kozák P. 2014. Continental-wide distribution of crayfish species in Europe: update and maps. Knowl Manag Aquat Ecosyst 413: 05. [CrossRef] [EDP Sciences] [Google Scholar]
- Kušar D, Vrezec A, Ocepek M, Jenčič V. 2013. Aphanomyces astaci in wild crayfish populations in Slovenia: first report of persistent infection in a stone crayfish Austropotamobius torrentium population. Dis Aquat Organ 103: 157–169. [CrossRef] [PubMed] [Google Scholar]
- Lipták B, Vitázková B. 2014. Review of the current distribution and dispersal trends of two invasive crayfish species in the Danube basin. Water Res Manag 4: 15–22. [Google Scholar]
- Maguire I, Jelić M, Klobučar G. 2011. Update on the distribution of freshwater crayfish in Croatia. Knowl Manag Aquat Ecosyst 401: 31. [CrossRef] [EDP Sciences] [Google Scholar]
- Maguire I, Jelić M, Klobučar G, Delpy M, Delaunay C, Grandjean F. 2016. Prevalence of the pathogen Aphanomyces astaci in freshwater crayfish populations in Croatia. Dis Aquat Organ 118: 45–53. [CrossRef] [PubMed] [Google Scholar]
- Moorhouse TP, Macdonald DW. 2011. The effect of manual removal on movement distances in populations of signal crayfish (Pacifastacus leniusculus). Freshw Biol 56: 2370–2377. [CrossRef] [Google Scholar]
- Peay S, Hiley PD, Collen P, Martin I. 2006. Biocide treatment of ponds in Scotland to eradicate signal crayfish. Bull Fr Pêche Piscic 380–381: 1363–1379. [CrossRef] [EDP Sciences] [Google Scholar]
- Petrusek A, Filipová L, Ďuriš Z, et al. 2006. Distribution of the invasive spiny-cheek crayfish (Orconectes limosus) in the Czech Republic. Past and present. Bull Fr Pêche Piscic 380–381: 903–918. [CrossRef] [EDP Sciences] [Google Scholar]
- Pöckl M. 1999. Distribution of crayfish species in Austria with special reference to introduced species. Freshw Crayfish 12: 733–750. [Google Scholar]
- Puky M. 2014. Invasive crayfish on land: Orconectes limosus (Rafinesque, 1817) (Decapoda: Cambaridae) crossed a terrestrial barrier to move from a side arm into the Danube River at Szeremle, Hungary. Acta Zool Bulg Suppl. 7: 143–146. [Google Scholar]
- Puky M, Schád P. 2006. Orconectes limosus colonises new areas fast along the Danube in Hungary. Bull Fr Pêche Piscic 380–381: 919–926. [CrossRef] [EDP Sciences] [Google Scholar]
- Rosewarne PJ, Piper AT, Wright RM, Dunn AM. 2013. Do low-head riverine structures hinder the spread of invasive crayfish? Case study of signal crayfish (Pacifastacus leniusculus) movements at a flow gauging weir. Manag Biol Inv 4: 273–282. [Google Scholar]
Cite this article as: Govedič M. 2017. First record of the spiny-cheek crayfish (Orconectes limosus) in Slovenia – 300 km upstream from its known distribution in the Drava River. Knowl. Manag. Aquat. Ecosyst., 418, 7.
Location of the newly discovered spiny-cheek crayfish (Orconectes limosus) population (red dot) in Slovenia and the previously known localities (green dots).
|In the text|
Detailed map of the area with newly discovered spiny-cheek crayfish (Orconectes limosus) population in Slovenia.
|In the text|
Current usage metrics show cumulative count of Article Views (full-text article views including HTML views, PDF and ePub downloads, according to the available data) and Abstracts Views on Vision4Press platform.
Data correspond to usage on the plateform after 2015. The current usage metrics is available 48-96 hours after online publication and is updated daily on week days.
Initial download of the metrics may take a while.