In Western Europe, many pond owners introduce amphibians for ornamental purposes. Although indigenous amphibians are legally protected in most European countries, retailers are circumventing national and international legislation by selling exotic nonprotected sibling species. We investigated to what extent non-native species of the European water frog complex (genus Pelophylax) have become established in Belgium, using morphological, mitochondrial and nuclear genetic markers. A survey of 87 sampling sites showed the presence of non-native water frogs at 47 locations, mostly Marsh frogs (Pelophylax ridibundus). Surprisingly, at least 19% of all these locations also harboured individuals with mitochondrial haplotypes characteristic of Anatolian water frogs (Pelophylax cf. bedriagae). Nuclear genotyping indicated widespread hybridization and introgression between P. ridibundus and P. cf. bedriagae. In addition, water frogs of Turkish origin obtained through a licensed retailer, also contained P. ridibundus and P. cf. bedriagae, with identical haplotypes to the wild Belgian populations. Although P. ridibundus might have invaded Belgium by natural range expansion from neighbouring countries, our results suggest that its invasion was at least partly enhanced by commercial trade, with origins as far as the Middle East. Also the invasion and rapid spread of Anatolian lineages, masked by their high morphological similarity to P. ridibundus, is likely the result of unregulated commercial trade. We expect that Anatolian frogs will further invade the exotic as well as the native range of P. ridibundus and other Pelophylax species elsewhere in Western and Central Europe, with risks of large-scale hybridization and introgression.

Globalization and increasing human impact on natural aquatic systems have facilitated the movement of species and the establishment of nonindigenous species enhancing hybridisation opportunities between naturally allopatric species. In this review, we focus on a special case of natural hybrid speciation and the consequences of recent anthropogenic hybridisation in the water frog complex (Pelophylax esculentus complex)

The recent genetic screening of water frogs (genus Pelophylax) in Belgium has shown that the invasion of two water frog species from Eastern Europe and the Mediterranean region, P. ridibundus and P. cf. bedriagae is widespread. Possibly other exotic water frogs are invading and establishing themselves through commercial trade. We used a genetic identification approach to rapidly detect and identify morphologically cryptic exotic water frog species in a large number of populations throughout the northern part of Belgium. Among a total of 944 individuals, we found 506 non-indigenous specimens, seven of which belonged to species not recorded before with certainty in Belgium or neighbouring regions in the wild. One of them was identified genetically as the Iberian green frog (P. perezi), but was most likely a P. perezi 9 P. esculentus hybrid. Six individuals of the Levantine frog (P. bedriagae) were found in a pond in the vicinity of a pet shop where the species is sold. All other exotic frogs belonged to four different haplotypes of P. ridibundus, established in Belgium since c. 1970, and two haplotypes of P. cf. bedriagae, a poorlyknown eastern Mediterranean sister species of the latter. Overall, our study underscores the extent of exotic water frog invasions associated with the pet trade. Although two of the exotic species were recorded in small numbers, their early detection is essential with regards to adequate control and eradication of invasive species.

In Belgium, the Pelophylax esculentus complex has recently been subjected to multiple introductions of non-native water frogs, increasing the occurrence of hybridisation events. In the present study, we tested the reliability of morphometric and recently developed microsatellite tools to identify introgression and to determine the origin of exotic Belgian water frogs. By analysing 150 individuals of each taxon of the P. esculentus complex and an additional 60 specimens of the introduced P. cf. bedriagae, we show that neither of the currently available tools appears to have sufficient power to reliably distinguish all Belgian water frog species. We therefore aimed at increasing the discriminatory power of a microsatellite identification tool by developing a new marker panel with additional microsatellite loci. By adding only two new microsatellite loci (RlCA5 and RlCA1b20), all taxa of the P. esculentus complex could be distinguished from each other with high confidence. Three more loci (Res3, Res5 and Res17) provided a powerful discrimination of the exotic species.