First record of the Danube sturgeon Acipenser gueldenstaedtii Brandt & Ratzeburg, 1833 in Al-Furat Lake, Syria: likely aquaculture escapees
Artikel-Kategorie: Research Article
Online veröffentlicht: 19. Sept. 2025
Seitenbereich: 171 - 177
Eingereicht: 16. Mai 2025
Akzeptiert: 03. Juli 2025
DOI: https://doi.org/10.26881/oahs-2025.1.13
Schlüsselwörter
© 2025 Ahmad E. Aidek et al., published by Sciendo
This work is licensed under the Creative Commons Attribution-NonCommercial-NoDerivatives 4.0 International License.
Sturgeons (family Acipenseridae) are ancient aquatic vertebrates characterized by their elongated bodies, cartilaginous skeletons, and rows of bony scutes (Kuhajda, 2014). Primarily inhabiting freshwater and brackish environments, some species migrate to marine waters for spawning (Lohe, 2021). As benthic predators and prey, sturgeons play a vital ecological role (Chen et al., 2022). However, overfishing, habitat loss, and pollution have severely threatened many sturgeon populations (IUCN, 2021), necessitating urgent conservation efforts for these evolutionarily significant fishes (White et al., 2023).
The Danube sturgeon
The record of the Danube sturgeon (
The key reasons for the cultivation of
Saygı et al. (2018) conducted a comprehensive study on the future of aquaculture in the Middle East, covering the period from 1950 to 2023. Their findings emphasized the need for more detailed analyses of aquaculture practices in the examined countries. Additionally, they recommended that governments adopt stricter regulatory measures in fisheries policies to ensure sustainable growth.
In contrast, Memis et al. (2002) highlighted the remarkable expansion of freshwater aquaculture in Turkey. Between the early 1970s and 1999, licensed fish farms surged from just 2 to 1444. Cage farming also experienced significant growth, with 57 farms established by 1999, producing 4100 tons of fish. Overall, aquaculture production skyrocketed from 3075 tons in 1986 to 63 000 tons in 1999. Inland production, primarily trout (
The study projected that Turkey’s aquaculture sector would continue expanding due to rising domestic demand, population growth, and increasing exports. Efforts are underway to diversify production by introducing new marine fish and shellfish species. However, bureaucratic hurdles in licensing— particularly for marine aquaculture—remain a major obstacle. The process is often cumbersome, plagued by technical knowledge gaps, and hindered by insufficient collaboration and knowledge-sharing on emerging industry developments.
Escapes of aquaculture fish into natural water bodies are common globally (Morris et al., 2008), including in Turkey (Innal & Erkakan, 2006). Such incidents often result from facility damage or predation. Sturgeon escapes have been documented previously, such as in the River Evros estuary (Koutrakis & Economidis, 2006). Here, we report an escape of
Three juvenile

Map showing the sampling locations where three specimens of
Since genetic analysis was not available to be performed, identification of the specimens was solely morphological and followed established taxonomic keys (Artûhin, 1979; Bănărescu, 1964; Peseridi, 1986).
The collected specimens (three juveniles in 2020, one subadult in 2022) measured approximately 300 mm total length (TL) for the specimen from October 2020, 400 mm TL for the specimens from November 2020, 550 mm TL for the specimen recorded in 2022, and 1000 mm TL for the specimen caught in the waters around Elazığ City, Turkey and used for comparison (Fig. 2). Specimens when photographed were not alive.

The data given in this study were compared with those reported by other authors for wild populations (Artûhin, 1979; Bănărescu, 1964; Peseridi, 1986) and were found to fall within the range of these populations.
The presence of
Turkey hosts seven sturgeon species (
Turkey is a primary source of non-native aquatic species in Syria and Iraq, whether through natural dispersal or accidental introduction (Tarkan et al., 2017). Analogous cases include non-native fish spreading from Ukraine to Belarus (Karatayev et al., 2008; Rizevsky et al., 2007). The recent record of
The introduction of non-native
The Syrian freshwater ecosystems (e.g., Euphrates River) are already degraded due to pollution, dams, and invasive species (e.g.,
In this section, several issues need to be addressed, beginning with immediate actions. It is important to confirm the sighting by verifying the species’ identity through genetic analysis using environmental DNA (eDNA) or tissue sampling to rule out misidentification. Additionally, rapid surveys should be conducted to assess the population status, including population size, age structure, and possible origin, such as natural migration versus human introduction.
In collaboration with Turkish authorities, long-term monitoring strategies can be divided into scientific monitoring, citizen science, and local engagement. Scientific monitoring includes telemetry tracking using acoustic or satellite tags to study movement patterns within the lake and potential migration routes. Regular seasonal surveys, such as gillnetting and hydroacoustics, should be conducted to monitor population trends, along with eDNA sampling to detect sturgeon presence. Citizen science and local engagement involve establishing a community reporting system where fishermen and locals are trained to report sturgeon sightings with photo verification, as well as awareness campaigns to educate stakeholders on sturgeon conservation to reduce bycatch and illegal fishing. Collaboration with Turkish authorities includes transboundary data sharing by coordinating with Turkish fisheries agencies to track potential upstream or downstream migration from the Euphrates-Tigris basin, as well as joint research initiatives with Turkish universities or conservation groups for genetic studies and habitat assessments.
Habitat management involves protecting spawning grounds by identifying and safeguarding potential breeding sites in the lake or connected rivers. Mitigating bycatch is also essential by promoting sturgeon-safe fishing gear, such as modified nets, to reduce accidental catches. Water quality control should be implemented by monitoring pollution levels that may affect sturgeon health.
Policy and conservation measures include advocating for legal protection by pushing for national listing under Syrian wildlife protection laws, if the species is not already covered. If the population is viable, restoration programs, such as habitat restoration through flow management and substrate improvements, should be considered.
Research priorities include genetic studies to determine whether the population is native, introduced, or escaped from aquaculture, as well as food web analysis to assess the sturgeon’s role in the lake ecosystem, including potential prey–predator dynamics.
In conclusion, the absence of adults or spawning evidence suggests these juveniles may represent accidental introductions rather than an established population, though further monitoring is critical to assess recruitment. Non-native sturgeon introductions can disrupt local ecosystems by altering benthic dynamics, increasing predation pressure, and risking genetic hybridization. Proactive management is essential to mitigate such impacts. Certain limitations in the present study should be acknowledged, including small sample size, reliance on morphology, and lack of genetic data.