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Ribogospod. nauka Ukr., 2026; 1(75): 98-114
DOI: https://doi.org/10.61976/fsu2026.01.098
UDC 595.384.1:574.24(4)

Received: 19.01.2026
Received in revised form: 05.03.2026
Published: 31.03.2026

First findings in Ukraine and current distribution trends of Neocaridina davidi (Bouvier, 1904) in freshwaters of Europe

S. Sidorovskyi, This email address is being protected from spambots. You need JavaScript enabled to view it. , ORCID ID 0000-0002-3344-1457,
V. N. Karazin Kharkiv National University, Kharkiv

Purpose. Summary and analysis of scientific sources and new unpublished data on the biology, ecological features and distribution of Neocaridina davidi (Bouvier, 1904) in Europe and Ukraine.

Methodology. The methodology was based on a comprehensive approach that combined the analysis of available scientific sources, the processing of new field materials, and a comparative study of confirmed cases of N. davidi in Europe.

Findings. The generalization of modern data allowed identifying the main factors influencing the success of the introduction and formation of N. davidi populations in freshwater ecosystems. Stable self-reproducing populations of the species have been recorded in Poland, Germany, France, Hungary, and Slovakia in recent decades and are associated with the presence of thermally stable or thermally transformed water bodies that reduce seasonal temperature fluctuations. In Ukraine, N. davidi is known only from isolated finds within Kharkiv city water bodies. The population in the thermally polluted section of the Kharkiv River was short-lived and disappeared after the cessation of warm technological runoff in 2022. In the Novo-Bavarske Reservoir (Kharkiv region), despite the recording of individual individuals in 2024, no signs of the formation of a self-sustaining population were detected, which is probably due to the unstable temperature regime and winter frosts. Experimental studies in EU countries indicate the potential ecological impact of N. davidi on benthic communities, in particular a decrease in the number of small benthic plankton. Microsporidia pathogens have also been identified in European populations of the species, indicating the possibility of interspecific transmission of infections. The results obtained indicate a low invasive potential of N. davidi in Ukraine under current conditions.

Originality. For the first time in Ukraine, the presence of the ornamental freshwater shrimp N. davidi in natural water bodies has been confirmed. It has been established that the penetration of this species into open water systems of Ukraine is associated with the development of the aquarium trade and the release of ornamental aquatic organisms into natural water bodies, which indicates the growing role of the aquarium hobby as one of the important ways of introducing alien invertebrates into freshwater ecosystems.

Practical Value. The results obtained are important for developing and improving strategies for monitoring and controlling invasive shrimps, in particular for developing approaches to their early detection, assessing potential ecological risks, and predicting the possible consequences of accidental or deliberate introductions. The data can be used by conservation organizations, research institutions, and government agencies to make management decisions aimed at conserving native fish and invertebrate species that may be subject to competition, trophic effects, or risk of infection by pathogens associated with N. davidi.

Keywords: cherry shrimp, aquatic bioresources, urbanized water bodies, invasive species, alien invertebrates, biological invasions, freshwater ecosystems, water bodies of Kharkiv region.

REFERENCES

  1. Casatti, L., Langeani, F., & Ferreira, C. P. (2006). Effects of physical habitat degradation on the stream fish assemblage structure in a pasture region. Environ Manage, 38, 974. https://doi.org/10.1007/s00267-005-0212-4.
  2. Ricciardi, A., & MacIsaac, H. J. (2011). Impacts of biological invasions on freshwater ecosystems. Fifty years of invasion ecology: the legacy of Charles Elton. Chichester: Wiley & Sons Ltd, Blackwell, 211–224. https://doi.org/10.1002/9781444329988.ch16 
  3. Britton, J. R., Lynch, A. J., Bardal, H., Bradbeer, S. J., Coetzee, J. A., Coughlan, N. E., Dalu, T., Tricarico, E, Gallardo, B., Lintermans, M., Lucy, F., Liu Olden, C. J. D., Raghavan, R., & Pritchard, E. G. (2023). Preventing and controlling nonnative species invasions to bend the curve of global freshwater biodiversity loss. Environmental Reviews, 31(2), 310–326. https://doi.org/10.1139/er-2022-0103.
  4. Saul, W. C., Roy, H. E., Booy, O., Carnevali, L., Chen, H., Genovesi, P., Harrower, C. A., Hulme, P. E., Pagad, S., & Jeschke, J. M. (2017). Assessing patterns in introduction pathways of alien species by linking major invasion data bases. J Appl Ecol, 54, 657–669. https://doi.org/10.1111/1365-2664.12819.
  5. Turbelin, A. J., Diagne, C., Hudgins, E. J., Moodley, D., Kourantidou, M., Novoa, A., Haubrock, P. J., Bernery, C., Gozlan, R. E., Francis, R. A., & Courchamp, F. (2022). Introduction pathways of economically costly invasive alien species. Biol Invasions, 24, 2061–2079. https://doi.org/10.1007/s10530-022-02796-5.
  6. Cambray, J. A. (2003). Impact on indigenous species biodiversity caused by the globalisation of alien recreational freshwater fisheries. Hydrobiologia, 500, 217–230. https://doi.org/10.1023/A:1024648719995.
  7. Capinha, C., Larson, E. R., Tricarico, E., Olden, J. D., & Gherardi, F. (2013). Effects of Climate Change, Invasive Species, and Disease on the Distribution of Native European Crayfishes. Conservation Biology, 27, 731–740. https://doi.org/10.1111/cobi.12043.
  8. Patoka, J., Magalhães, A. L. B., Kouba, A., Faulkes, Z., Jerikho, R., & Vitule, J. R. S. (2018). Invasive aquatic pets: failed policies increase risks of harmful invasions. Biodivers Conserv, 27, 3037–3046. https://doi.org/10.1007/s10531-018-1581-3.
  9. Bernery, C., Bellard, C., Courchamp, F., Brosse, S., Gozlan, R. E., Jarić, I., Teletchea F., & Leroy, B. (2022). Freshwater fish invasions: a comprehensive review. Annu Rev Ecol Evol Syst, 53, 427–456. https://doi.org/10.1146/annurev-ecolsys-032522-015551.
  10. Padilla, D. K., & Williams, S. L. (2004). Beyond ballast water: aquarium and ornamental trades as sources of invasive species in aquatic ecosystems. Front Ecol Environ, 2, 131–138. https://doi.org/10.1890/1540-9295(2004)002[0131:BBWAAO]2.0.CO;2 
  11. Duggan, I. C. (2010). The freshwater aquarium trade as a vector for incidental invertebrate fauna. Biol Invasions, 12, 3757–3770. https://doi.org/10.1007/s10530-010-9768-x.
  12. Liptak, B., & Vitázkova, B. (2015). Beautiful, but also potentially invasive. Ekol Bratisl, 34, 155–162. https://doi.org/10.1515/eko-2015-0016.
  13. Gippet, J. M. W., & Bertelsmeier, C. (2021). Invasiveness is linked to greater commercial success in the global pet trade. Proceedings of the National Academy of Sciences, 118(14).https://doi.org/10.1073/pnas.2016337118.
  14. Blaha, M., Weiperth, A., Patoka, J., Szajbert, B., Balogh, E. R., Staszny, Á., Ferincz, Á., Lente V., Maciaszek, R., & Kouba, A. (2022). The pet trade as a source of non-native decapods: the case of crayfish and shrimps in a thermal waterbody in Hungary. Environ Monit Assess, 194, 795. https://doi.org/10.1007/s10661-022-10361-9.
  15. Blackburn, T. M., Pyšek, P., Bacher, S., Carlton, J. T., Duncan, R. P., Jarošík, V., Wilson, J. R. U., & Richardson, D. M. (2011). A proposed unified framework for biological invasions. Trends in Ecology & Evolution, 26(7), 333–339. https://doi.org/10.1016/j.tree.2011.03.023 
  16. Mitsugi, M., & Suzuki, H. (2018). Life history of an invasive freshwater shrimp Neocaridina davidi (Bouvier, 1904), (Decapoda: Caridea: Atyidae) in the Tomoe River, the Boso Peninsula, Eastern Japan. Crustacean Research, 47, 9–16. https://doi.org/10.18353/crustacea.47.0_9.
  17. Bouvier, E. L. (1904). Crevettes de la famille des Atyidés; espèces qui font partie des collections du Muséum d’Histoire naturelle. Bull. Mus. Hist. Nat. Paris, 10, 129–138. https://doi.org/10.5962/p.38627 
  18. Milne-Edwards, H. (1840). Histoire naturelle des crustacés: comprenant l’anatomie, la physiologie et la classification de ces animaux Librairie encyclopédique de Roret. Vol. 3.
  19. Kubo, I. (1938). On the Japanese atyid shrimps. Journal of the Imperial Fisheries Institute, Tokyo, 33, 67–100.
  20. Bochini, G. L., Rios, A. D. S., Teles, J. N., Zara, F. J., & Mantelatto, F. L. (2024). Confirmed by integrative taxonomy first and unusual occurrence of the exotic shrimp Neocaridina davidi (Caridea: Atyidae) in Brazil. Boletim do Instituto de Pesca, 50. https://doi.org/10.20950/1678-2305/bip.2024.50.e849.
  21. Tropea, C., Stumpf, L., & López Greco, L. S. (2015). Effect of Temperature on Biochemical Composition, Growth and Reproduction of the Ornamental Red Cherry Shrimp Neocaridina heteropoda heteropoda (Decapoda, Caridea). PLoS ONE, 10(3), e0119468. https://doi.org/10.1371/journal.pone.0119468.
  22. Sidorovskyi, S. A., & Shrestha, М. Y. (2024). Crustacean fauna of Kharkiv region (Ukraine). Biosystems Diversity, 32(3), 314–323. https://doi.org/10.15421/012434.
  23. Klotz, W., Miesen, F. W., Hüllen, S., & Herder, F. (2013). Two Asian fresh water shrimp species found in a thermally polluted stream system in North Rhine-Westphalia, Germany. Aquatic Invasions, 8(3), 333–339. http://dx.doi.org/10.3391/ai.2013.8.3.09.
  24. Schoolmann, G., & Arndt, H. (2018). Population dynamics of the invasive freshwater shrimp Neocaridina davidi in the thermally polluted Gillbach stream (North Rhine-Westphalia, Germany). Limnologica, 71, 1–7. https://doi.org/10.1016/j.limno.2018.05.001.
  25. Jabłońska, A., Mamos, T., Gruszka, P., Szlauer-Łukaszewska, A., & Grabowski, M. (2018). First record and DNA barcodes of the aquarium shrimp, Neocaridina davidi, in Central Europe from thermally polluted River Oder canal, Poland. Knowl. Manag. Aquat. Ecosyst., 419, 14. https://doi.org/10.1051/kmae/2018004.
  26. Pantaleão, J. A. F., Gregati, R. A., da Costa, R. C., López-Greco, L. S., & Negreiros-Fransozo, M. L. (2017). Post-hatching development of the ornamental ‘Red Cherry Shrimp’ Neocaridina davidi (Bouvier, 1904) (Crustacea, Caridea, Atyidae) under laboratorial conditions. Aquac Res, 48, 553–569. https://doi.org/10.1111/are.12903.
  27. Weber, S., & Traunspurger, W. (2016). Influence of the ornamental red cherry shrimp Neocaridina davidi (Bouvier, 1904) on freshwater meiofaunal assemblages. Limnologica, 59, 155–161. https://doi.org/10.1016/j.limno.2016.06.001.
  28. Jamonneau, T., Camargo, A. R., Halima, I. B., Prati, S., & Denys, G. P. J. (2024). Evidence of an established population of Poecilia reticulata and Neocaridina davidi in metropolitan France. Cybium: Revue Internationale d’Ichtyologie, 1-12 https://doi.org/10.26028/cybium/2024-034
  29. Weiperth, A., Gábris, V., Danyik, T., Farkas, A., Kuříková, P., Kouba, A., & Patoka, J. (2019). Occurrence of non-native red cherry shrimp in European temperate waterbodies: a case study from Hungary. Knowl. Manag. Aquat. Ecosyst., 420, 9. https://doi.org/10.1051/kmae/2019002.
  30. Prati, S., Grabner, D. S., Hupało, K., Weiperth, A., Maciaszek, R., Lipták, B., Bojko, J., Bérces, F., & Sures, B. (2024). Invisible invaders: range expansion of feral Neocaridina davidi offers new opportunities for generalist intracellular parasites. Biol Invasions, 26, 2499–2523. https://doi.org/10.1007/s10530-024-03324-3.
  31. Ling, B., Wu, Y., Yu, Q., Wang, C., Hu, M., Meng, X., Long, M., Pan, G., Xiang, Z, Zhou, Z., & Chen, J. (2024). Ecytonucleospora hepatopenaei proliferate in Procambarus clarkii: a warning for crayfish and shrimp aquaculture. Aquaculture, 581, 40457. https://doi.org/10.1016/j.aquaculture.2023.740457.