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18 November 2021 Is gynogenetic reproduction in gibel carp (Carassius gibelio) a major trait responsible for invasiveness?
Md Mehedi Hasan Fuad, Lukáš Vetešník, Andrea Šimková
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The invasion success of gibel carp (Carassius gibelio) depends on demographic and competitive traits. The major biological trait responsible for the invasiveness of C. gibelio is the mode of reproduction. Apart from sexual reproduction, which is typical in fish, C. gibelio is a unique cyprinid species able to reproduce through asexual gynogenesis, which is also known as sperm-dependent parthenogenesis, observed in all-female populations. Though the sexual and asexual forms of C. gibelio co-exist widely in natural habitats, the gynogenetic form has the capacity to modulate the range of effective ecological niches, which may facilitate the process of invasion. In this paper, we reviewed current knowledge of the sexual and gynogenetic forms of gibel carp along with their physiological advantages, immunological traits, and ability to withstand different environmental conditions. As parasitic infection may directly alter the immunology of hosts, and also indirectly alter their investment in reproduction, we provide some insights into the role of parasites as one of the potential drivers facilitating the coexistence of asexual and sexual forms. We highlight evidence that gibel carp have been identified as a serious threat to native species; hence, its impact on the ecosystem is also discussed.


Invasive species are non-native to a given ecosystem; they usually negatively affect biodiversity in natural habitats and may even cause economic losses (Xu et al. 2006, Beck et al. 2008, Xia et al. 2019). They are also identified as one of the main reasons for species extinction in nature (Roberts et al. 2013). The success of invasive species (or invaders) may depend on how ecologically distant they are from native species. The ecological and demographic differences between native and invasive species may enable invasives to exploit free nutritional resources to avoid competition or make them less vulnerable to predators and parasites (Alcaraz et al. 2005). Factors related to species (biotic) or habitat (abiotic) determine whether a given species will be an invader (Ross 1991). The invasion process model proposed by Kolar & Lodge (2001) suggested transitional stages that an alien species has to pass through to become a successful invader. According to this model, these stages are the following: transportation, release, establishment and spread. A similar invasion model was proposed by Heger (2001), demonstrating several stages and steps in chronological order from the immigration of the species to the colonization of new localities (Fig. 1). Gibel carp (Carassius gibelio) is considered an alien fish species in the hydrographic system of the Czech Republic (Lusková et al. 2010). It is also a widely distributed invasive fish among other European countries (Verreycken et al. 2007, Perdikaris et al. 2012, Ribeiro et al. 2015). This omnivorous species, occupying both lentic and lotic habitats, is an unwelcome competitor in the natural habitats of native fish species (Halačka et al. 2003). Gibel carp have been considered responsible for reducing population densities of crucian carp (Carassius carassius) and other native cyprinid species by altering the habitat structure (Savini et al. 2010, Wouters et al. 2012) and exerting reproductive pressure on other cyprinids (utilizing male cyprinids, especially C. carassius and Cyprinus carpio, for the induction of gynogenesis (Papoušek et al. 2008). It has also been reported to effect rapid changes in biodiversity and the food chain complex (Ruppert et al. 2017).

Fig. 1.

Invasion model proposed by Heger (2001).


The gibel carp is considered to be a native species from central Europe to Siberia (Kalous et al. 2012), or alternatively to have been introduced to European waters from eastern Asia (Perdikaris et al. 2012). It invaded the Czech Republic from the River Danube through natural migration via the Slovakian section of the River Morava. The first record of this species comes from the lower reaches of the River Dyje. Consequently, it invaded the adjacent alluvial waters of the two rivers (the River Dyje and the River Morava). Gibel carp rapidly dispersed through these river drainages. Around 1980 it appeared in the drainage of the River Labe (Halačka et al. 2003). In subsequent years, gibel carp populations rapidly increased in the drainage area of the lower and middle reaches of the River Labe and in the lower reaches of the River Vltava and their alluvial waters. At present, C. gibelio occurs in all suitable aquatic habitats in the Czech Republic (Halačka et al. 2003).

Formerly, the gibel carp was recognized as a subspecies of Carassius auratus, i.e. considered as Carassius auratus gibelio (Cherfas 1981, Jiang et al. 1983). Later, Rylková et al. (2013) designated C. gibelio a valid species, one of the members of the C. auratus complex (this complex includes Carassius langsdorfii, Carassius cuvieri, C. auratus and C. gibelio). Recent sampling in the River Dyje (Czech Republic) revealed four mitochondrial lineages of C. auratus complex, namely C. gibelio, C. auratus, C. langsdorfi and the so-called M-line, the three last lines were present at low frequency and mtDNA C. gibelio represented the most common line (96%) (Pakosta et al. 2018). Gibel carp has a specific mode of reproduction exhibiting both asexual and sexual reproduction, which is a rarity in nature and is documented only in a small number of freshwater fishes, including nine genera (Lamatsch & Stöck 2009). Some authors propose an even more complicated system of reproduction in gibel carp, including unisexual gynogenesis, sexual reproduction, and a hybrid-like development mode or androgenesis (nucleo-cytoplasmic hybrid clone) in response to sperm from different species or gibel carp (Wang et al. 2011, Zhang et al. 2015, Gao et al. 2017).

As an invasive species gibel carp tend to aggressively occupy new habitats (Liasko et al. 2011); its rapid reproduction facilitated by gynogenesis (Paschos et al. 2004). For example, in the Czech Republic the early invasive population of gibel carp was composed of triploid females with gynogenetic reproduction, recognized in natural habitats of the River Dyje until 1995, when the first cases of males were detected. Subsequently, mixed populations of triploid gynogenetic females and sexual diploids have been documented (Lusková et al. 2004). Gibel carp spread rapidly by means of its own invasive strategy, assisted by human activity in tributaries of the Danube where it formed stable populations (Lusk et al. 2004). The rapid reproduction achieved by gynogenesis may facilitate the expansion of gibel carp, even when accidentally introduced into the breeding ponds of common carp. In such cases, gibel carp may represent a threat to common carp production (traditionally undertaken in some East and Central European countries) due to competition for food and space (Šimková et al. 2015).

Fig. 2.

Gynogenetic reproduction in gibel carp.


The aim of this study was to review the current knowledge of invasive gibel carp along with their physiological advantages, immunological traits, and ability to withstand different environmental conditions. We specifically focused on the potential advantages of this species related to multiple reproduction strategies potentially facilitating its invasion success.

Genetic background of gynogenesis

In gynogenesis, embryos are formed from female genetic material only. The ovum is activated by sperm from male gibel carp or other cyprinid species. During activation, the sperm penetrates the ovum, but the sperm nucleus does not fuse with the ovum nucleus and there is no syngamy (Barbuti et al. 2012). As a consequence the offspring are clones of the gynogenetic female (Fig. 2).

Li et al. (2014) hypothesized that the ancestor of gynogenetic hexaploid gibel carp is a tetraploid lineage of C. auratus, thus gibel carp may have originated via autotriploidy about 0.5 million years ago. First, C. auratus experienced polyploidization events and gained bisexual reproductive capacity through diploidization. Then, later, recurrent polyploidization events led to hexaploid gibel carp (Li et al. 2014). As a consequence of polyploidization there are different types of clonal reproduction documented in fish complexes, i.e. gynogenesis, parthenogenesis, hybridogenesis, and kleptogenesis (Lampert & Schartl 2010, Stöck et al. 2012, Choleva & Janko 2013, Li et al. 2016b). Due to its capacity to exhibit diverse ploidy within species, the gibel carp is a unique model for studying the transition of reproduction types (sexual vs. asexual) in relation to polyploidy (Lu et al. 2021).

Gynogenetic forms (functionally triploids and evolutionarily hexaploids, 3n = 150) and sexual forms (functionally diploids and evolutionarily tetraploids, 2n = 100) are morphologically indistinguishable in nature (Przybył et al. 2020). However, in studies of C. gibelio, it was shown that the chromosome number for hexaploids ranged between 156 and 162 (for East Asian form of C. gibelio shown Zhou & Gui 2002) and between 150 and 159 (for the European form of C. gibelio shown by Kalous & Knytl 2011), and was suggested that such hexaploids (at least the East Asian form) are able to reproduce by unisexual gynogenesis as well as by bisexual reproduction (Gui & Zhou 2010).

The alteration between ploidy ratios in C. gibelio may also contribute to its invasion process. Przybył et al. (2020) compared ploidy and sex ratios for European and East Asian populations and revealed that incidence of diploid males and females (considered to reproduce sexually) is higher in Europe, whilst triploid females and males prevail in East Asian populations. Interestingly, higher genetic diversity and divergence were confirmed in triploids than in diploids in Asian populations, which facilitates their environmental adaptation (Jiang et al. 2013, Liu et al. 2017). Moreover, it was also shown that genotypic males play an important role in the creation of genetic diversity in gynogenetic gibel carp, this can be considered as a mechanism counteracting the Muller's ratchet process in gynogenetic gibel carp (Zhao et al. 2021). However, for the European form of the gibel carp, a weakened diversity of immune genes was revealed for the triploid gynogenetic form (high proportion of triploid females expressed the same genotype) in the mixed population suggesting that the most common triploid form is a target of parasite adaptation (Šimková et al. 2013, see below). In some countries diploid populations of gibel carp have gradually displaced triploids (Liasko et al. 2011, Przybył et al. 2020). It was suggested that this trajectory could be linked with invasion, as this pattern was not evident in native populations of gibel carp (i.e. in East Asia) (Przybył et al. 2020). However, female triploids are still widely distributed throughout Europe. For example, from 2001 to 2007 in the Czech Republic the ploidy status of male and female gibel carp were investigated and an increasing trend in the proportion of diploid specimens in mixed populations was observed over time. However, a higher percentage of triploid females were also observed in the study areas, which indicates the important role of gynogenesis in maintaining local populations of C. gibelio (Halačka et al. 2003). Until 1990, European C. gibelio populations almost exclusively comprised triploid females, originating through gynogenesis and maintained as discrete clonal lineages. Such mixed diploid-polyploid populations consisting of diploids and triploids are not common in East Asia (the home range of C. gibelio) (Liu et al. 2017), which may indicate the potential link between the evolutionary trajectory of gibel carp populations and its invasiveness in European waters.

The reproductive mode of gynogenetic vs. sexual is indirectly revealed by sex and ploidy ratios (Przybył et al. 2020), even if the presence of triploid males may offer the possibility of bisexual reproduction even in triploid females (Gui & Zhou 2010, Zhang et al. 2015). Gynogenetic specimens of gibel carp are often determined using cytogenetic analyses, i.e. karyotypes (Liasko et al. 2010). Flow cytometry, erythrocyte measurement, nucleolar organizer region analysis, external morphology analysis and tissue measurement are also applied as ploidy determination techniques (Garcia-Abiado et al. 1999). Flow cytometry is an optical technique which determines particle fluorescence after treatment with a DNA-specific dye, such as propidium iodide (Harrell et al. 1998). High-throughput flow cytometry is commonly applied as a cost effective method in terms of reduced labour and consumables compared with more manually intensive methods (Cousin et al. 2009). As the cellular and nuclear dimensions of erythrocytes have been shown experimentally to be proportional to ploidy level in teleost fishes (Beck & Biggers 1983), the size of erythrocytes offers an alternative to flow cytometry (Garcia-Abiado et al. 1999).

Polyploidy also plays a role in the sex determination system of gibel carp (Lu et al. 2021). It was predicted that two rounds of polyploidization and diploidization in gibel carp would lead to different sex determination mechanisms: genotypic sex determination (GSD) and environmental sex determination (ESD) (or temperature sex determination (TSD)) related to facultative reproductive strategies, i.e. unisexual and bisexual reproduction modes (Bachtrog et al. 2014, Mei & Gui 2015, Capel 2017, Zhu et al. 2018). GSD depends on genotypic elements during fertilization (Gamble & Zarkower 2012), whilst ESD is affected by several environmental factors, like temperature (Conover & Kynard 1981), photoperiod (Brown et al. 2014), social (Warner 1982), pH and dissolved oxygen (Baroiller et al. 2009). Genotypic and environmental sex determinations are not mutually exclusive in gibel carp (Li & Gui 2018).

To examine the effect of rearing temperature on sex determination of gibel carp, Li & Gui (2018) conducted an experiment with two artificial strains and one wild strain of gibel carp under a wide range of rearing temperatures. In the case of one artificial strain, all female offspring were generated when the temperature was less than 19 °C, while males were produced when the temperature was above 22 °C. Only male offspring were recorded at a temperature above 31 °C. In the case of the other artificial strain and the wild strain, all female offspring were generated at a temperature lower than 25 °C with males produced at temperatures higher than 28 °C.

Concerning the fertilization of eggs, there are differences between GSD and TSD males. Eggs fertilized by sperm from GSD males go through sexual reproduction events, such as swelling of the sperm nucleus. In contrast, when eggs are fertilized by sperm from TSD males, the sperm remain in a condensed state right through the first mitotic process (Zhu et al. 2018).

The presence of dual reproductive modes (gynogenetic and sexual) in gibel carp has been hypothesized as indicating an evolutionary transition of reproduction from unisexual to sexual reproduction (Gui & Zhou 2010, Li et al. 2016a). Hence, it seems necessary to identify the specific genes related to reproduction and potentially also the genes involved in sex-determination in gynogenetic-sexual fish complexes. The gonadal transcriptomes of asexual Poecilia formosa and its parent sexual species Poecilia mexicana and Poecilia latipinna were analysed in a study by Schedina et al. (2018), in which the overall down-regulation of meiosis-related genes and the misregulation of many genes related to reproduction were revealed in asexual P. formosa, in contrast to sexual P. mexicana and P. latipinna.

Reproductive and physiological advantages facilitating the coexistence of gynogenetic and sexual forms of invasive gibel carp

Gynogenetic gibel carp have the advantages of rapid growth and high fecundity (Perdikaris et al. 2012). From an evolutionary point of view, asexual reproduction has an advantage over sexual reproduction in that sexual reproduction suffers from the two-fold cost of producing males (Gibson et al. 2017); hence, gynogenesis ensures a faster rate of increase in the size of female gibel carp populations. Regarding demography, asexual individuals should exhibit lower fecundity when compared with sexual, according to the demographic advantage hypothesis (Leung & Angers 2017). However, on the basis of mathematical simulation, it was suggested that half of asexual individuals imitate the cost of sex by producing no offspring and that only the presence of non-reproductive individuals in asexual females can result in the long-term coexistence of sexual and asexual species (or forms) (Leung & Angers 2017).

The fitness-related traits of sexual and asexual forms are important for their coexistence in nature and some of them may potentially contribute to the invasiveness of gibel carp. Spatial data on the growth and development of the gynogenetic and sexual forms of gibel carp in the Czech Republic indicate that gynogenetic triploid females have significantly higher growth rates than sexual diploids (Vetešník et al. 2004). Fitness and condition-related traits were examined in gynogenetic and sexual forms of gibel carp in order to reveal whether there are some physiological advantages exhibited by the gynogenetic form, which initially invaded the hydrological systems of the Czech Republic. However, it was shown that gynogenetic and sexual females expressed the same gonado-somatic index, which is considered a measure of reproductive performance or fitness, and that both female forms exhibited a similar level of oestradiol in blood plasma (Šimková et al. 2015). In contrast, a weak fitness advantage measured by fecundity, egg viability, and hatchling growth rate was found for the sperm-dependent asexual species Phoxinus eos-neogaeus when compared to its sexually reproducing parental species, Phoxinus eos and Phoxinus neogaeus (Mee et al. 2013a).

Concerning other physiological traits, the hepatosomatic index (a measure of fish condition) of gynogenetic gibel carp was shown to be higher when compared to the sexual counterpart, which indicates a better physiological condition (energy/ metabolic reserves) for the gynogenetic form (Šimková et al. 2015). However, Šimková et al. (2015) also showed a physiological disadvantage for gynogenetic females, i.e. lower aerobic performance when compared to sexual males. This disadvantage in gynogenetic females seems to be compensated by higher oxygen-carrying capacity per erythrocyte when compared to the sexual form. Finally, the authors proposed that a potential trade-off between the high number of erythrocytes with lower oxygen-carrying capacity per erythrocyte in sexual males and the low number of erythrocytes with high oxygen-carrying capacity per erythrocyte in gynogenetic females may represent a potential mechanism contributing to the coexistence of gynogenetic and sexual gibel carp.

Differences in the effectiveness of the immune systems and contrasting susceptibility to parasite infection may represent another potential mechanism facilitating the coexistence of asexual and sexual forms of gibel carp, thereby contributing to its invasive ability. Hakoyama et al. (2001) reported lower nonspecific immunity and higher parasite loads of generalist trematode parasite species (Metagonimus sp.) in the gynogenetic form of the C. auratus complex. In contrast, Šimková et al. (2015) showed no difference in nonspecific immunity between the gynogenetic and sexual forms of C. gibelio, but revealed higher specific immunity (measured by IgM level) in gynogenetic females. In accordance with the Red Queen hypothesis, which postulates antagonistic co-evolution between hosts and parasites, parasites are under selection to infect the most common host genotypes in the local population (Seger & Hamilton 1988, Hamilton et al. 1990). Thus, in a species (or species complex) with coexisting asexual and sexual forms, due to reduced genetic diversity asexual hosts or the most common asexual phenotypes/genotypes are the targets of parasite adaptation, whilst sexual hosts escape from parasite infection because of high genetic variability generated by recombination (Lively et al. 1990). The high level of parasite infection in common asexual clones could then favour genetically diverse sexual individuals and promote the short-term coexistence of sexual and asexual forms in the same habitat. This response was shown for the sexual top minnow Poeciliopsis monacha coexisting with two gynogenetic triploid clones of Poeciliopsis 2monacha-lucida (Lively et al. 1990). A study of gibel carp focused on the variability of major histocompatibility complex (MHC) genes (representing functional immune genes in vertebrates) and parasite load showed that if gynogenetic and sexual forms coexist in a slightly biased ratio (gynogenetic females comprising 60% of a population and sexuals comprising 40%), the most common MHC clones of the gynogenetic form suffer from high parasite richness or high intensities of infection by metazoan parasites (mostly by host-specific gill monogeneans of Dactylogyrus) (Šimková et al. 2013). However, the temporal dynamics of parasite infection in gynogenetic and sexual forms of gibel carp coexisting in the same habitat (with gynogens comprising an estimated 37% of the population and sexuals comprising 63%) was not consistent with the prediction of the Red Queen hypothesis in a 4-year study (Pakosta et al. 2018), indicating the effects of multiple abiotic and biotic factors on parasite load in both forms. The sexual form was even more strongly infected by monogenean ectoparasites in the first and last years, whilst the gynogenetic form was more strongly parasitized by nematodes in the two final years.

Considering other asexual-sexual complexes in fish, no consistent pattern of parasite load between asexual P. formosa and sexual P. latipinna was observed on the spatial scale, i.e. among different populations (Tobler & Schlupp 2005). Similarly, the mechanisms predicted by the Red Queen hypothesis did not explain the coexistence of sexual and asexual forms in the Cobitis taenia hybrid complex (Kotusz et al. 2014).

Modulation of the ecological niche after invasion

Ecological communities with low species richness are vulnerable to invasions (Milardi et al. 2019). Fish invasion is generally more plausible in areas with native endemic species with a restricted distribution and/or in areas influenced by human activities. Concerning invasive gibel carp, a negative effect on native fish species was documented in the Ömerli Reservoir, Turkey (Gaygusuz et al. 2007). A significant decrease in the abundance of white sucker (Catostomus commersonii) in North America in response to an increase in gibel carp abundance was also reported (Ruppert et al. 2017). Gibel carp has also been reported as a serious threat to commercially important fish species such as European eel (Anguilla anguilla) and tench (Tinca tinca), as well as to other native fish species (Perdikaris et al. 2012). An alternative hypothesis suggests that an invading species may frequently occur in species-rich communities (Stachowicz & Byrnes 2006). A study carried out by Stohlgren et al. (2006) showed a positive relationship between the densities of native and non-indigenous fish species; however, native fish species richness was not significantly correlated with invasive fish richness. In many cases, the competition for resources between native species and invaders actually helps the invasion by altering the food web architecture. Successful invasion by nonnative forms in fish can vary widely between geographic regions, ranging from 38 to 77% (Ross 1991). Successful establishment by an invading fish species is expedited by a broad dietary and habitat niche (Garciá-Berthou 2007, Courant et al. 2017). It has been observed that in some systems niche differentiation can also play a role in the co-existence of sexual and asexual forms of fishes (Weeks et al. 1992, Doeringsfeld et al. 2004). For example, the co-existence of sperm-dependent asexual Chrosomus spp. and its sexual hosts can be maintained by a combination of niche separation and conspecific mate preference (Mee et al. 2013b). However, no information on the potential niche preferences or mating preferences of gynogenetic and sexual forms of invasive gibel carp is currently available.

The trophic niche width of gibel carp is broader than that of native species in all invaded areas (Özdilek & Jones 2014). This ecological characteristic along with gynogenetic reproduction, dietary plasticity, and environmental stress tolerance make gibel carp a successful invasive species (Lusková et al. 2010). Further, the gibel carp is benthopelagic (Erdoğan et al. 2014), readily taking a dominant position in lentic and slow-running waters (Aydin et al. 2011). It may impact the populations of a variety of native freshwater fish species by directly competing for food, i.e. pelagic zooplankton and benthic invertebrates (Lusk et al. 2010), or alter the top-down control of zooplankton (Bondarev et al. 2019). Specifically, due to competition for food and space, gibel carp are responsible for the disappearance of some native cyprinoid species in some areas, i.e. C. carassius, T. tinca, Leucaspius delineatus and Scardinius erythrophthalmus and for the reduction of their population densities in others (Lusk et al. 2010). Gibel carp have wider niches than any other co-existing species and can occupy any vacant niche by slightly altering its dietary pattern (Özdilek et al. 2019).

Environmental tolerance

Declines in native cyprinoid fish populations have been initially attributed to habitat degradation but the invasion of gibel carp has also been identified as an additional negative factor affecting native species (Özdilek & Jones 2014). Gibel carp were shown to alter the flow of nutrients in ecosystems or cause a change in turbidity (Crivelli 1995). A decrease in water quality may even increase the abundance of this species. For example, an increase in the population density of gibel carp and positive changes to reproductive parameters, i.e. spawning period, gonad size, and reproductive effort, were shown in comparison with native fish species over a period of years in a system with low water quality measured by total phosphorus and chlorophyll-a (Tarkan et al. 2012).

There are multiple factors contributing to the increase in gibel carp population size in aquatic ecosystems. The most important is the unique capacity of gibel carp to rapidly reproduce by gynogenesis (see above). Other factors include a capacity to tolerate environmental degradation, tolerance of predation and resistance to food competition from other species (Holčík & Žitňan 1978, Paschos et al. 2004). Gibel carp can also withstand extremely adverse environmental conditions. For example, gibel carp juveniles resulting from gynogenesis (more specifically, from the activation of gibel carp eggs by sperm from Rutilus ylikiensis) exhibited specific growth rates of 3.14% and 0.91% at NH3 concentrations of 0.51 mg/l and 8 mg/l, respectively (Paschos et al. 2004). Gibel carp have the largest somatic glycogen stores among the vertebrates (25-30% of their liver being glycogen) (Hochachka & Somero 1984, Hyvärinen et al. 1985), which allows them to survive anoxia for prolonged periods (De Boeck et al. 2010). The effect on gibel carp of a predefined level of exposure to copper (LC50 330 µg/10 days) was evaluated in a study by De Boeck et al. (2010), in which the level of response of the stress hormone cortisol increased. As a consequence, not only was there a change in ion regulation, but also an alteration in energy metabolism resulting from the promotion of glycogenolysis and increasing glucose levels in the blood. In a similar study, extra glycogen was found to be used by fish exposed to copper in both lethal and sub-lethal doses (Eyckmans et al. 2011). Gibel carp can also tolerate hypoxia and low temperatures (Liasko et al. 2011); with acclimation it can also survive in saline water (Elger & Hentschel 1981). It has the capacity to colonize inland waters with high levels of eutrophication, which otherwise negatively affects the overall diversity of ichthyofauna and the body weights of other fish species (Paulovits et al. 2014).

Impact of gibel carp on ecosystems

Invasive species can have a significant impact on ecosystems by affecting community composition, the distributions of populations, and food webs (Gurevitch & Padilla 2004, David et al. 2017). In some areas of the Baltic ecosystem, high abundance and slow growth suggest that gibel carp may already exert an influence on the coastal food web (Navodaru et al. 2002, Vetemaa et al. 2005). The potential impact of gibel carp on ecosystems is evidenced in several European countries, where the decline of native crucian carp and degradation of its habitat have been reported to be linked to the invasion of gibel carp (Navodaru et al. 2002, Gaygusuz et al. 2007 Paulovits et al. 2014). Gibel carp not only change the composition of native fish populations but also affects native benthic invertebrate communities (Ruppert et al. 2017). Its impact on invertebrate communities is as a “bio-turbator” (a species that reworks soils and sediments) (Richardson et al. 1995). It is able to occupy turbid water, which is often unsuitable for invertebrate communities (Bilotta & Brazier 2008). In addition to causing turbidity, gibel carp can also cause damage by feeding on and uprooting aquatic plants (Richardson et al. 1995), and thus may affect entire aquatic ecosystems (Van der Veer & Nentwig 2015). This species is also capable of preying on amphibians, molluscs, annelids, crustaceans, and insects (Meyer et al. 1998). Vertebrates in higher trophic levels are typically vulnerable to anthropogenic threats. Özdilek & Jones (2014), using estimates to express the trophic positions of fish species, identified a lower trophic position and slightly lower vulnerability to anthropogenic threats for gibel carp when compared to other members of fish communities, this likely contributing to its invasion success.


Alien species are continually introduced into many regions of the world, though not all survive and coexist with the resident native species. Many introduced species, however, have dramatic impacts on native biodiversity and ecosystem functions (Gallien & Carboni 2017). The biggest risks are posed by species with wide ecological tolerance and that exhibit traits linked to invasiveness (Allendorf 1991). The specific biological traits of gibel carp; the coexistence of sexual and asexual forms in the same habitats, the capacity to rapidly reproduce by gynogenesis, the potential for environmental sex determination, as well as its ecological tolerance (including its resistance to anoxia and its capacity to expand its niche width and occupying new areas) have made this species one of the most successful non-native invasive fish species in the waters of the Czech Republic, as well as in Central and eastern Europe.


The study was supported by the Czech Science Foundation, project no. 19-10088S and Masaryk University MUNI/A/1581/2020. We thank Matthew Nicholls for English language revision of the manuscript. Author contributions: all authors contributed to prepare the final draft of review.



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This is an open access article under the terms of the Creative Commons Attribution Licence (CC BY 4.0), which permits use, distribution and reproduction in any medium provided the original work is properly cited.
Md Mehedi Hasan Fuad, Lukáš Vetešník, and Andrea Šimková "Is gynogenetic reproduction in gibel carp (Carassius gibelio) a major trait responsible for invasiveness?," Journal of Vertebrate Biology 70(4), 21049.1-13, (18 November 2021).
Received: 30 June 2021; Accepted: 30 August 2021; Published: 18 November 2021

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