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Prussian carp

The Prussian carp (Carassius gibelio) is a medium-sized, deep-bodied freshwater fish native to and , recognized for its silvery-brown coloration and robust build that closely resembles the (Carassius carassius), though distinguished by a dorsal fin profile, strongly serrated anal and dorsal rays, 29-33 scales, and a black . It typically attains a common length of 20 cm, with a maximum total length of 46.6 cm and weight up to 3 kg, reaching at around 10.3 cm. This species thrives in a wide range of freshwater and brackish environments, including still waters, lowland rivers, canals, reservoirs, and areas with submerged , demonstrating remarkable tolerance to low oxygen levels, pollution, and temperatures from 10°C to 20°C, with a pH range of 7.1-7.5. As a benthopelagic , it consumes , benthic , material, filamentous , and , exhibiting generalist feeding habits that enable it to exploit diverse habitats. A key biological trait is its primarily via , where dominant triploid females (up to 75% of populations) produce unfertilized eggs that develop into clones using sperm from conspecific males or other species, often spawning multiple times per year on submerged vegetation and achieving lifespans of 5-10 years. Potamodromous in , it migrates within freshwater systems, and while it supports minor commercial fisheries in its native range, it is widely regarded as a potential due to its invasive spread. Originally distributed from across to and parts of (35°N-62°N, 10°W-155°E), the Prussian carp has been introduced extensively in and beyond, establishing invasive populations in —first confirmed in , , in 2006 and in 2006—where it outcompetes for resources, reduces abundances by up to fourfold, and diminishes benthic diversity, posing significant ecological and economic threats. As of 2025, it has colonized the and tributaries in , continuing to expand.

Taxonomy and nomenclature

Classification

The Prussian carp, Carassius gibelio, is classified within the domain Eukarya, Animalia, phylum Chordata, class Actinopterygii, order Cypriniformes, family , genus , and species C. gibelio. Phylogenetically, C. gibelio belongs to the genus and is closely related to the (Carassius auratus) and (Carassius carassius), with historical taxonomic confusion arising from hybridization potential among these species; it also shares a broader affinity with the common carp (Cyprinus carpio) within the family. The species was first described by Marcus Elieser Bloch in 1782 as Cyprinus gibelio, with the modern binomial Carassius gibelio established based on that type specimen from European waters. Genetic studies confirm the native origins of C. gibelio span from central Europe (including the Danube River basin) to Siberia and the Amur River basin in the Far East, revealing a hybrid ancestry involving ancestral Carassius lineages that contributed to its polyploidy and invasiveness. Populations of C. gibelio exhibit diverse levels, including diploid (2n=~100 chromosomes) and triploid (3n=~150 chromosomes) forms, with recognition of all-female parthenogenetic lineages that dominate in many regions through gynogenetic reproduction.

and synonyms

The "Prussian carp" is associated with the species' historical presence in the regions of during the 18th century, where it became established in local waters prior to its wider spread across . The name "gibel carp" originates from Eurasian regional terms, such as the "Giebel" or "Gibel," reflecting its early recognition in central European ichthyological literature. The scientific name Carassius gibelio was first described by Marcus Elieser Bloch in 1782 as Cyprinus gibelio, based on specimens likely collected from Prussian freshwater systems. The genus Carassius is a Latinization of "karass" or "karausche," traditional European names for similar cyprinid fishes like the crucian carp. The specific epithet "gibelio" stems from the aforementioned German vernacular "Giebel," used for this silvery carp species in historical accounts. Synonyms for Carassius gibelio include Cyprinus gibelio Bloch, 1782 (the original combination), Carassius auratus gibelio (Bloch, 1782) (reflecting its former subspecies status under ), and Carassius bucephalus Heckel, 1837 (a junior synonym based on morphological variation). Older literature often confused C. gibelio with the crucian carp , leading to misidentifications such as applying "Prussian carp" interchangeably to both species in 19th-century reports. Nomenclatural controversies centered on whether C. gibelio represented a distinct species, a subspecies of the goldfish Carassius auratus, or a hybrid form within the Carassius complex, due to morphological similarities and overlapping ranges. These debates were largely resolved in the 2000s through genetic analyses, including mitochondrial DNA sequencing, which confirmed C. gibelio as a separate species with hidden genetic diversity, including multiple lineages. Key studies, such as Rylková et al. (2010) on goldfish monophyly and Kalous et al. (2012) designating a neotype from the Elbe River basin, provided phylogenetic evidence distinguishing it from C. auratus. Since the 1990s, authoritative databases like FishBase have recognized Carassius gibelio as the valid species name, a status also reflected in its treatment by the IUCN (not evaluated but accepted taxonomically).

Physical description

Morphology

The Prussian carp (Carassius gibelio) exhibits an elongated, robust body form typical of cyprinid fishes, characterized by a deep and laterally compressed profile that provides stability in lentic environments. The body is plump with a rounded abdomen, contributing to its carp-like appearance similar to that of the closely related (Carassius auratus). This structure supports efficient swimming in still or slow-moving waters, with the overall shape aiding in maneuverability. The head is small and short, featuring a terminal mouth positioned upward for surface feeding, surrounded by thick lips but lacking barbels, a key distinction from the (Cyprinus carpio). Pharyngeal teeth are arranged in a single row with a 4-4 formula on each side, adapted for grinding plant material and small . Scales are large and , covering the body evenly, with 29-33 scales along the , which serves as a sensory organ for detecting vibrations. The peritoneum is black. Gill rakers number 37-52 and are structured to filter food particles effectively. The originates midway along the body and includes 3 unbranched rays followed by 16-19 branched rays, with the last unbranched ray strongly serrated and the posterior edge concave or straight. The anal fin has 3 unbranched rays and 5½ branched rays (the ½ denoting the split penultimate ray), also with a serrated last unbranched ray. Paired pectoral and pelvic fins are positioned ventrally for balance and propulsion, while the caudal fin is forked, enhancing agility. A is present, consisting of two chambers that regulate across varying water depths.

Size, coloration, and variations

The Prussian carp (Carassius gibelio) attains a maximum total length of 46.6 cm and a maximum weight of 3 kg, though common adult lengths range from 20 to 40 cm depending on environmental conditions and . Growth rates vary with water temperature, with individuals reaching at lengths of 10.3 to 15 cm, typically within the first few years of life. The species has a reported lifespan of up to 10 years in the wild. In terms of coloration, the Prussian carp exhibits a silvery-brown hue on the surface, transitioning to a lighter silvery-white on the ventral side, which provides in varied environments. Juveniles often display a more pronounced silvery sheen compared to adults. Domesticated strains of closely related species, such as the (Carassius auratus), may exhibit red or orange pigmentation due to . Intraspecific variations are notable, with minimal outside of the breeding season, during which males develop small epithelial tubercles on the head, operculum, and pectoral fins. Triploid females, which predominate in many populations and reproduce gynogenetically, tend to grow larger and exhibit higher growth rates than diploid counterparts. Regional pigmentation differences can occur, influenced by factors such as and , leading to occasional mottling or shifts toward olive-green tones in some environments.

Distribution and habitat

Native range

The Prussian carp (Carassius gibelio) is native to , extending eastward through the basin to and . Its original geographic distribution encompasses major river drainages, including the , , and basins. In , native populations are established in lowland areas of the , while in Asia, the species occurs naturally in river systems of northern and the . Historical records, including ichthyological surveys from the and earlier, confirm the species' pre-human dispersal presence in , particularly in the territories of modern-day , , and . Prior to any recorded introductions, the species was absent from western European waters, with its westernmost native extent limited to central European river systems. Native populations primarily occupy lakes, ponds, and slow-flowing with abundant submerged and periodic flooding. These habitats are characteristic of temperate climates, where water temperatures typically range from 10°C to 20°C, supporting the species' benthopelagic lifestyle in freshwater and occasionally brackish environments. In countries such as and , C. gibelio forms stable populations in Danube tributaries and coastal lagoons, while in , it is widespread in Volga floodplains and River wetlands.

Introduced range and habitat preferences

The Prussian carp (Carassius gibelio) was first introduced outside its native range in and during the , primarily through accidental escapes from facilities in , including regions like and . Subsequent human-mediated spread occurred via intentional stocking for food and ornamental purposes, leading to establishment across much of by the . In , the species was first detected in , , around 2000 and confirmed in open waters in 2006, likely introduced unintentionally through the live baitfish trade originating from . Currently, Prussian carp are widespread in introduced ranges across western and , including countries such as , the , , , , , and . In , introductions have occurred in , , , and , often linked to activities. In , as of 2025, established populations are limited to the Bow, Oldman, , and basins in and , , with potential for expansion southward into the via connections to the basin, currently limited by barriers such as the Qu’Appelle Dam. Prussian carp prefer stagnant or slow-flowing freshwater habitats such as ponds, lakes, reservoirs, canals, and lowland rivers with abundant submerged vegetation, where they often occupy the littoral zones. They exhibit broad environmental tolerances, thriving in conditions unsuitable for many , including high , low dissolved oxygen levels as low as 0.6 mg/L, and water temperatures up to 32°C, with optimal growth around 28°C. As a species, they can survive in brackish waters with salinities up to 14 , though they primarily inhabit freshwater systems. Typically, they are found at depths of 0–5 m, avoiding deeper, oxygen-poor strata.

Biology and ecology

Diet and feeding behavior

The Prussian carp (Carassius gibelio) is an omnivorous with a flexible diet that includes both plant and animal matter, allowing it to exploit diverse food resources in its habitats. Primary components consist of (such as diatoms from Bacillariophyta and from ), , and including chironomid larvae (Diptera) and like Cladocera, Copepoda, and Rotifera. In a study of 155 individuals from Lake Ladik, , animal prey dominated the diet at 77.62% relative importance index (RII), with Cladocera as the most significant group (41.38% RII) across seasons, followed by Rotifera (18.26% RII) and (16.27% RII); fish eggs were also present among the 29 identified prey taxa. Juveniles tend to be planktivorous, focusing on small and periphytic , while adults shift ontogenetically toward benthic such as amphipods, ostracods, and chironomids around 12 cm fork length. In dense populations, Prussian carp increase reliance on plant material and fish eggs, reflecting opportunistic adjustments to resource availability. For instance, in Lake Eğirdir, , cladocerans (primarily Daphnia sp., 25.6% of diet volume) and dipterans like Chironomus sp. (18.6%) were predominant, with gastropods, copepods, ostracods, and mysids also contributing significantly to the benthic and planktonic components. This broad diet supports the species' role as a trophic generalist, bridging primary producers and higher consumers in freshwater ecosystems. Prussian carp exhibit bottom-feeding behavior, using a subterminal oriented downward to suction food from the in a vacuum-like manner typical of cyprinids. This strategy targets and benthic prey in vegetated or muddy areas, with juveniles preferring high-complexity habitats like reed belts for access. Feeding intensity varies seasonally with water temperature, peaking in summer (intensity index 1.25) and lowest in winter (0.27), and shows opportunistic specialization on abundant items like Cladocera. Daily equates to approximately 1.5–2.7% of body weight based on studies in reservoirs, enabling rapid exploitation of resources. Trophic adaptations include tolerance of low-food conditions through substantial storage, with muscle content reaching up to 18–20% in certain seasons, aiding overwintering and resistance. This storage, combined with aggressive resource competition via high foraging rates, positions Prussian carp as effective generalists; their sediment-disturbing suction feeding causes bioturbation that resuspends particles.

Reproduction and life cycle

The Prussian carp (Carassius gibelio) exhibits a unique reproductive strategy dominated by , a form of in which sperm from males of the same or closely related species, such as (Cyprinus carpio) or (Carassius auratus), activates egg development without contributing genetic material to the offspring. This process results in clonal daughters that are genetically identical to the mother, maintaining all-female lineages and enabling rapid population expansion. Populations are overwhelmingly composed of triploid females, which constitute over 95% of individuals in many invaded areas, while rare diploid forms may engage in . Prussian carp also hybridize readily with and , producing viable triploid or aneuploid offspring that can further complicate in shared habitats. Spawning typically occurs during spring and early summer, from to , when water temperatures rise to 14–22°C, with females capable of multiple spawning events over this prolonged period. Eggs are small, , and demersal, attaching to submerged or other substrates in shallow, weedy areas to avoid predation and ensure oxygenation. lasts 2–4 days depending on , with hatching accelerated at higher values (e.g., 52 hours at 22–25°C), after which larvae emerge and begin rapid exogenous feeding. Juveniles grow quickly, reaching at 1–2 years of age in warmer southern ranges, though this may extend to 3–4 years in cooler northern latitudes. Fecundity is high, with females producing 30,000–85,000 eggs per spawning event on average, though values can reach up to 62,000 in larger individuals, supporting the ' invasive potential through sheer reproductive output. The clonal of gynogenetic preserves advantageous genotypes across generations, while occasional sexual events in diploids or hybrids introduce limited variability. Overall, this —marked by early maturity, multiple broods, and unisexual dominance—facilitates the ' persistence and spread in diverse environments.

Invasive status and management

Ecological impacts

The Prussian carp (Carassius gibelio), as an , exerts profound negative effects on native ecosystems by outcompeting local for resources and altering structures, leading to reduced in both and North American waters. In invaded areas, it rapidly establishes dominance, with populations capable of comprising up to 60% of the total in certain lakes, thereby suppressing abundance. This competitive edge stems from its tolerance for low-oxygen and turbid conditions unsuitable for many natives, allowing it to thrive where other decline. Biodiversity impacts are particularly severe, as Prussian carp outcompete and displace native cyprinids, such as the (Carassius carassius) in , where it has become the dominant species in lentic and slow-flowing habitats over the past decades. In , invasions have led to significant declines in native fish populations, including brook stickleback (Culaea inconstans), (Pimephales promelas), lake chub (Couesius plumbeus), and (Catostomus commersonii), with overall native fish abundance dropping to one-fourth of pre-invasion levels in affected riverine systems. Additionally, its feeding behavior preys on benthic invertebrates, shifting community composition toward tolerant taxa like and Simuliidae while reducing diversity of sensitive species, which in turn affects higher trophic levels. These changes threaten specialized natives by altering prey availability and quality in shared river basins. Ecosystem alterations further compound these effects, with Prussian carp acting as bioturbators that rework sediments through , increasing water and reducing light penetration essential for vegetation growth. This feeding on plant material and disrupts submerged macrophytes, leading to habitat loss for vegetation-dependent species and shifts in benthic communities. High accumulations also modify nutrient cycling by resuspending phosphorus and other elements from sediments, exacerbating and altering food webs in invaded waters. Hybridization poses a genetic threat, as Prussian carp's gynogenetic reproduction—where females produce clones using sperm from native males without full fertilization—introduces foreign genes into local populations of related species like and (Cyprinus carpio), potentially eroding and causing reproductive interference. This parasitism wastes reproductive resources of native males, contributing to declines in cyprinid communities across and . In , such interactions have been linked to the widespread displacement of , while in , they amplify potential risks to endemic fish through .

Distribution in North America and control efforts

The Prussian carp (Carassius gibelio) was first confirmed in open waters of in , , with initial records dating to the early 2000s in the drainage. By 2006, established populations were documented in river systems, including the Bow, Oldman, and Rivers, likely introduced via illegal release of aquarium or . An isolated individual was recorded in in 2005, with established populations confirmed by 2018. The species has since expanded, reaching the by 2017 and, as of 2025, occupying the river and its tributaries while moving toward additional connected systems to the northeast. As of 2025, Prussian carp remains confined to these western Canadian provinces, with no verified established populations in the United States, though its proximity to the international border raises concerns for southward spread into watersheds like the basin. In , control efforts emphasize prevention and early detection due to the lack of selective, cost-effective eradication methods for this resilient . 's provincial , implemented since 2016, prohibits possession, transport, and release of Prussian carp, supported by public campaigns and mandatory reporting of sightings to the Alberta Environment and Parks hotline. (eDNA) surveillance has been widely adopted for non-invasive monitoring, with studies in from 2018–2019 sampling 83 sites across river basins and detecting the species at 12 sites to map and inform targeted netting operations. In , a 2020 aquatic includes boat inspection stations and angler reporting apps to curb downstream dispersal, though suppression attempts via and seining have yielded limited success. Cross-border collaboration between Canadian provinces and U.S. states like and focuses on shared monitoring, including joint eDNA protocols and angler education to prevent accidental introductions via angling gear or live bait. Ontario has preemptively classified Prussian carp as a prohibited under its 2016 Invasive Species Act, banning imports and imposing fines up to CAD 100,000 for violations, while funding into biocontrol options like triploid induction to sterilize populations—though field trials remain experimental and unscaled. Overall, these efforts highlight the challenges of managing Prussian carp's parthenogenetic reproduction and tolerance to harsh conditions, with ongoing prioritizing predictive modeling to anticipate range expansion.

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