Next Article in Journal
Transition from Fire-Dependent Open Forests: Alternative Ecosystem States in the Southeastern United States
Next Article in Special Issue
Self-Compatibility and Reproductive Success of Oenothera drummondii subsp. drummondii: Is It Similar between Native and Non-Native Populations?
Previous Article in Journal
Experimental Warming Effects on Prokaryotic Growth and Viral Production in Coastal Waters of the Northwest Pacific during the Cold Season
Previous Article in Special Issue
Dittrichia viscosa: Native-Non Native Invader
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Brief Report

Hitchhiking Exotic Clam: Dreissena polymorpha (Pallas, 1771) Transported via the Ornamental Plant Trade

1
Department of Zoology and Fisheries, Faculty of Agrobiology, Food and Natural Resources, Czech University of Life Sciences Prague, 165 00 Prague, Czech Republic
2
St. Ursula School, 110 00 Prague, Czech Republic
*
Author to whom correspondence should be addressed.
Diversity 2021, 13(9), 410; https://doi.org/10.3390/d13090410
Submission received: 20 July 2021 / Revised: 16 August 2021 / Accepted: 25 August 2021 / Published: 27 August 2021
(This article belongs to the Special Issue 2021 Feature Papers by Diversity’s Editorial Board Members)

Abstract

:
Ornamental aquaculture is one of the main sources of non-native species worldwide. Unintentionally transported “hitchhiking” organisms have been previously recorded; although most of these species are transported from tropical regions, here we report on the first accidental transport of the zebra mussel (Dreissena polymorpha) in a shipment of ornamental Aegagropila linnaei (Chlorophyta) from Russia to the Czech Republic. This invasive mussel is listed on the national blacklist of alien species in the Czech Republic and can be easily released in outdoor garden ponds together with A. linnaei. Since the Czech Republic is known to be a gateway for aquatic ornamental species from a European perspective, re-export to other European countries is also possible. Thus, the spread of D. polymorpha via this pathway cannot be excluded. This finding should be of importance to conservationists, traders, decision-makers and other stakeholders.

In the era of globalization, biological invasions cause huge environmental and socio-economic losses worldwide, costing billions of dollars each year [1]. Ornamental aquaculture was identified as one of the main sources of non-native organisms [2,3,4,5] with thousands of individuals of thousands of animal and plant species transported per day both intra- and intercontinentally via the pet trade [6,7,8,9,10]. The occurrence of non-native biota is generally perceived as unwanted and harmful, even if there also exists certain examples of introduced endangered species such as Arapaima gigas, the fish of ornamental origin which is native and endangered in South America and recorded in the wild in Indonesia as a potential invader [11]. Therefore, decision-makers try to regulate this pathway via legislative restrictions, but the effectiveness is controversial and contentious in certain cases due to poor education of the general public in this regard [12].
When intentionally released or accidentally escaped, ornamental species can establish, multiply, and subsequently spread to the vicinity and behave as invasive, such as the marbled crayfish Procambarus virginalis in many European countries [13] and the apple snail Pomacea sp. in South Europe [14]. Certain ornamental species have been recorded in small quantities in the wild, such as the redclaw Cherax quadricarinatus [15] and the Mexican dwarf crayfish Cambarellus patzcuarensis [16] in Hungary, but their further spread cannot be excluded, at least in the case of the latter. Moreover, non-native pathogens, such as oomycete Aphanomyces astaci causing crayfish plague, are transmitted by their ornamental hosts [17,18] and can persist in the new environment by infecting native species even if their hosts do not survive.
Not only ornamental species are highlighted in this regard, but also associated biota have been recorded as being transported via this pathway [19,20]. These faunal assemblages are also known as “hitchhikers” and their ornamental hosts can be both animals and plants [21,22]. The predicted and discussed invasion potential of so-called hitchhikers is usually higher in comparison with ornamental species [23]. Some species are transported without close association with any of the ornamental species and can live without hosts freely when introduced to a new locality, and thus their invasion potential is high [22,24]. Improving knowledge about the spread of non-native species including hitchhikers via the international pet industry is crucial to establish effective management strategies to reduce introduction rates. The Czech Republic is known as one of the leading importers and exporters of aquatic ornamental species [2,8]. Most of these organisms are imported from tropical regions in South and South-east Asia, Africa and South America, while imports from other countries in temperate zones are mostly overlooked [2,7].
Therefore, we decided to inspect the shipment of dark green ornamental Marimo (also known as Cladophora balls or moss balls), which is a rare form of Aegagropila linnaei (Chlorophyta), to check on the possible presence of hitchhiking organisms. The shipment included 100 pcs of Marimo balls and was delivered by van from Moscow river in Russia, with a stop in Ukraine, to the Czech Republic in January 2021. Within the personal inspection we found one living and vital individual of freshwater zebra mussel Dreissena polymorpha [25]. This voucher individual had a shell length of 18 mm (Figure 1), which indicated it to be in the adult stage [26]. The voucher specimen was preserved in pure alcohol and deposited at the Department of Zoology and Fisheries, Czech University of Life Sciences Prague, the Patoka’s Lab Collection, No. JP2021/01-001. The record is in line with anecdotal notes on Dreissena polymorpha associated with Marimo balls by hobbyists and aquarium owners [27]: https://eu.indystar.com/story/news/environment/2021/03/12/here-5-things-know-invasive-zebra-mussels-mossballs/4652002001/ (accessed on 19 July 2021).
Dreissena polymorpha (Bivalvia: Dreissenidae) is native to the Ponto-Caspian region [28], and thus Moscow river is out of its native range. Dreissena polymorpha appeared here from the middle of the 19th century [29,30]. The main method of dispersal of D. polymorpha is its ‘natural’ spread through channels and other artificial constructions, while drifting macrophytes and human transport can also be viewed as vectors of this mollusc dispersal [31]. For example, it was recently demonstrated that the overland transport of boats can facilitate dispersal of this species [32,33]. This clam is one of the most successful biofouling and prolific aquatic invasive species, jeopardizing native biota and entire ecosystems [34]. It is currently spread in 33 European countries (including the Czech Republic), 33 U.S. states and territories, and two provinces of Canada [35]. With the use of byssal threads, this mussel attaches to hard submerged surfaces and substrates, forming large colonies which may cause increased water turbidity, displacement of native mussel species, and alteration of nutrient cycling and trophic relationships [35,36,37]. Moreover, mutualistic interactions between D. polymorpha and certain invasive aquatic macrophytes from the genera Elodea, Myriophyllum, and Potamogeton have been recorded to enhance the biomass of the mentioned species [37]. Certain species from the first two mentioned genera are included on the list of invasive species of European Union concern (Regulation No. 1143/2014 on the prevention and management of the introduction and spread of invasive alien species).
Dreissena polymorpha was first recorded in the current territory of the Czech Republic in the early 1900s [38]. Subsequently, based on classification as invasive species with massive environmental impacts, it was added in the national blacklist of alien species [39]. Marimo balls are recommended as suitable species for ornamental outdoor pond planting/stocking (see: https://rybicky.net/atlasrostlin/cladophora_aegagropila [in Czech] (accessed on 19 July 2021)), a hobby which has increasing popularity in the Czech Republic [40]. Therefore, it is obvious that overlooked hitchhiking D. polymorpha can be released together with the Marimo balls and penetrate new waterbodies, for instance, when the ornamental pond is flooded.
Since the Czech Republic has been identified as a gateway for aquatic ornamental species from a European perspective, many imported animals and plants are subsequently re-exported abroad [2]. Thus, hitchhikers can be easily transported via this pathway to other European countries together with ornamental species.
From the aforementioned, it follows that D. polymorpha is a species of global concern and monitoring its introduction pathways is very important for improving the effectiveness of focused management and regulations. The first record of its introduction via international trade with ornamental aquatic plants should be of the attention of conservationists, traders, decision-makers and other stakeholders. Moreover, our finding highlighted the importance of monitoring the route of certain ornamental species transportation from non-tropical regions to the global market.

Author Contributions

Conceptualization, J.P.; methodology, J.P.; validation, J.P.; formal analysis, J.P.; investigation, J.P. and B.P.; resources, B.P.; data curation, J.P.; writing—original draft preparation, J.P.; writing—review and editing, B.P.; visualization, J.P.; supervision, J.P.; project administration, J.P.; funding acquisition, B.P. Both authors have read and agreed to the published version of the manuscript.

Funding

J.P. was funded by the Technology Agency of the Czech Republic within the project “DivLand”, grant number SS02030018”.

Institutional Review Board Statement

Not applicable.

Data Availability Statement

Not applicable.

Acknowledgments

We thank anonymous reviewers for their effort and time when evaluating our manuscript.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Vilà, M.; Hulme, P.E. Impact of Biological Invasions on Ecosystem Services; Springer International Publishing: Cham, Switzerland, 2017; 354p, ISBN 978-3-319-45121-3. [Google Scholar]
  2. Kalous, L.; Patoka, J.; Kopecký, O. European hub for invaders: Risk assessment of freshwater aquarium fishes exported from the Czech Republic. Acta Ichthyol. Piscat. 2015, 15, 239–245. [Google Scholar] [CrossRef] [Green Version]
  3. Nunes, A.L.; Tricarico, E.; Panov, V.E.; Cardoso, A.C.; Katsanevakis, S. Pathways and gateways of freshwater invasions in Europe. Aquat. Invasions 2015, 10, 359–370. [Google Scholar] [CrossRef] [Green Version]
  4. Patoka, J.; Takdir, M.; Yonvitner; Aryadi, H.; Jerikho, R.; Nilawati, J.; Tantu, F.Y.; Bohatá, L.; Aulia, A.; Kamal, M.M.; et al. Two species of illegal South American sailfin catfish of the genus Pterygoplichthys well-established in Indonesia. Knowl. Manag. Aquat. Ecosyst. 2020, 421, 28. [Google Scholar] [CrossRef]
  5. Haubrock, P.; Oficialdegui, F.J.; Yiwen, Z.; Patoka, J.; Yeo, D.C.J.; Kouba, A. The redclaw crayfish: A prominent aquaculture species with invasive potential in tropical and subtropical biodiversity hotspots. Rev. Aquac. 2021, 13, 1488–1530. [Google Scholar] [CrossRef]
  6. Padilla, D.K.; Williams, S.L. Beyond ballast water: Aquarium and ornamental trades as sources of invasive species in aquatic ecosystems. Front. Ecol. Environ. 2004, 2, 131–138. [Google Scholar] [CrossRef]
  7. Patoka, J.; Kalous, L.; Kopecký, O. Imports of ornamental crayfish: The first decade from the Czech Republic’s perspective. Knowl. Manag. Aquat. Ecosyst. 2015, 416, 4. [Google Scholar] [CrossRef]
  8. Evers, H.G.; Pinnegar, J.K.; Taylor, M.I. Where are they all from?—Sources and sustainability in the ornamental freshwater fish trade. J. Fish Biol. 2019, 9, 909–916. [Google Scholar] [CrossRef] [Green Version]
  9. Akmal, S.G.; Zámečníková-Wanma, B.P.; Prabowo, R.E.; Khatami, A.M.; Novák, J.; Petrtýl, M.; Kalous, L.; Patoka, J. Marine ornamental trade in Indonesia. Aquat. Living Resour. 2020, 33, 25. [Google Scholar] [CrossRef]
  10. Novák, J.; Kalous, L.; Patoka, J. Modern ornamental aquaculture in Europe: Early history of freshwater fish imports. Rev. Aquac. 2020, 12, 2042–2060. [Google Scholar] [CrossRef]
  11. Marková, J.; Jerikho, R.; Wardiatno, Y.; Kamal, M.M.; Magalhães, A.L.B.; Bohatá, L.; Kalous, L.; Patoka, J. Conservation paradox of giant arapaima Arapaima gigas (Schinz, 1822) (Pisces: Arapaimidae): Endangered in its native range in Brazil and invasive in Indonesia. Knowl. Manag. Aquat. Ecosyst. 2020, 421, 47. [Google Scholar] [CrossRef]
  12. Patoka, J.; Magalhães, A.L.B.; Kouba, A.; Faulkes, Z.; Jerikho, R.; Vitule, J.R.S. Invasive aquatic pets: Failed policies increase risks of harmful invasions. Biodivers. Conserv. 2018, 27, 3037–3046. [Google Scholar] [CrossRef] [Green Version]
  13. Hossain, M.S.; Patoka, J.; Kouba, A.; Buřič, M. Clonal crayfish as biological model: A review on marbled crayfish. Biologia 2018, 73, 841–855. [Google Scholar] [CrossRef]
  14. Lei, J.; Chen, L.; Li, H. Using ensemble forecasting to examine how climate change promotes worldwide invasion of the golden apple snail (Pomacea canaliculata). Environ. Monit. Assess. 2017, 189, 1–11. [Google Scholar] [CrossRef]
  15. Weiperth, A.; Gál, B.; Kuříková, P.; Langrová, I.; Kouba, A. Risk assessment of pet-traded decapod crustaceans in Hungary with evidence of Cherax quadricarinatus (von Martens, 1868) in the wild. North West J. Zool. 2019, 15, 42–47. [Google Scholar]
  16. Gál, B.; Kuříková, P.; Bláha, M.; Kouba, A.; Patoka, J. Cambarellus patzcuarensis in Hungary: The first dwarf crayfish established outside of North America. Biologia 2017, 72, 1529–1532. [Google Scholar]
  17. Mrugała, A.; Kozubíková-Balcarová, E.; Chucholl, C.; Resino, S.C.; Viljamaa-Dirks, S.; Vukić, J.; Petrusek, A. Trade of ornamental crayfish in Europe as a possible introduction pathway for important crustacean diseases: Crayfish plague and white spot syndrome. Biol. Invasions 2015, 17, 1313–1326. [Google Scholar] [CrossRef]
  18. Putra, M.D.; Bláha, M.; Wardiatno, Y.; Krisanti, M.; Jerikho, R.; Kamal, M.M.; Mojžišová, M.; Bystřický, P.K.; Kouba, A.; Kalous, L.; et al. Procambarus clarkii (Girard, 1852) and crayfish plague as new threats for biodiversity in Indonesia. Aquat. Conserv. 2018, 28, 1434–1440. [Google Scholar] [CrossRef]
  19. Duggan, I.C.; Pullan, S.G. Do freshwater aquaculture facilities provide an invasion risk for zooplankton hitchhikers? Biol. Invasions 2017, 19, 307–314. [Google Scholar] [CrossRef]
  20. Duggan, I.C.; Champion, P.D.; MacIsaac, H.J. Invertebrates associated with aquatic plants bought from aquarium stores in Canada and New Zealand. Biol. Invasions 2018, 20, 3167–3178. [Google Scholar] [CrossRef]
  21. Patoka, J.; Bláha, M.; Devetter, M.; Rylková, K.; Čadková, Z.; Kalous, L. Aquarium hitchhikers: Attached commensals imported with freshwater shrimps via the pet trade. Biol. Invasions 2016, 18, 457–461. [Google Scholar] [CrossRef]
  22. Patoka, J.; Bláha, M.; Kalous, L.; Vrabec, V.; Buřič, M.; Kouba, A. Potential pest transfer mediated by international ornamental plant trade. Sci. Rep. 2016, 6, 25896. [Google Scholar] [CrossRef]
  23. Patoka, J.; Kopecký, O.; Vrabec, V.; Kalous, L. Aquarium molluscs as a case study in risk assessment of incidental freshwater fauna. Biol. Invasions 2017, 19, 2039–2046. [Google Scholar] [CrossRef]
  24. Patoka, J.; Prabowo, R.E.; Petrtýl, M.; Reynolds, J.D.; Kuříková, P.; Zámečníková-Wanma, B.P.; Kalous, L. Marine hitchhikers: A preliminary study on invertebrates unintentionally transported via the international pet trade. NeoBiota 2020, 61, 33–36. [Google Scholar] [CrossRef]
  25. Pallas, P.S. Reise Durch Verschiedene Provinzen des Russischen Reichs. Theil 1. Physicalische Reise Durch Verschiedene Provinzen des Russischen Reichs im 1768- und 1769 sten Jahren; Kaiserliche Akademie der Wissenschaften: St. Petersburg, Russia, 1771. [Google Scholar]
  26. Mackie, G.L. Biology of the exotic zebra mussel, Dreissena polymorpha, in relation to native bivalves and its potential impact in Lake St. Clair. Hydrobiologia 1991, 219, 251–268. [Google Scholar] [CrossRef]
  27. Bowman, S. Have an Aquarium? Here Are the 5 Things to Know about Invasive Zebra Mussels in Moss Balls. 2021. Available online: https://eu.indystar.com/story/news/environment/2021/03/12/here-5-things-know-invasive-zebra-mussels-moss-balls/4652002001/ (accessed on 19 July 2021).
  28. Son, M.O. Native range of the zebra mussel and quagga mussel and new data on their invasions within the Ponto-Caspian Region. Aquat. Invasions 2007, 2, 174–184. [Google Scholar] [CrossRef]
  29. Ludyanskiy, M.L.; McDonald, D.; MacNeill, D. Impact of the zebra mussel, a bivalve invader: Dreissena polymorpha is rapidly colonizing hard surfaces throughout waterways of the United States and Canada. Bioscience 1993, 43, 533–544. [Google Scholar] [CrossRef]
  30. L’vova, A.A. On invasion of Dreissena bugensis (Bivalvia, Dreissenidae) in the Ucha Reservoir (Moscow oblast) and the Moscow River. Zoologicheskiy Zhurnal 2004, 83, 3–20. [Google Scholar]
  31. Horvath, T.G.; Lamberti, G.A. Drifting macrophytes as a mechanism for zebra mussel (Dreissena polymorpha) invasion of lake-outlet streams. Am. Midl. Nat. 1997, 138, 29–36. [Google Scholar] [CrossRef]
  32. Johnson, L.E.; Ricciardi, A.; Cartlon, J.T. Overland dispersal of aquatic invasive species: A risk assessment of transient recreational boating. Ecol. Appl. 2001, 11, 1789–1799. [Google Scholar] [CrossRef]
  33. De Ventura, L.; Weissert, N.; Tobias, R.; Kopp, K.; Jokela, J. Overland transport of recreational boats as a spreading vector of zebra mussel Dreissena polymorpha. Biol. Invasions 2016, 18, 1451–1466. [Google Scholar] [CrossRef]
  34. Ward, J.M.; Ricciardi, A. Impacts of Dreissena invasions on benthic macroinvertebrate communities: A meta-analysis. Divers. Distrib. 2007, 13, 155–165. [Google Scholar] [CrossRef]
  35. Dölle, K.; Kurzmann, D.E. The freshwater mollusk Dreissena polymorpha (zebra mussel)—A review: Living, prospects and jeopardies. Asian J. Environ. Ecol. 2020, 13, 1–17. [Google Scholar] [CrossRef]
  36. Ricciardi, A. Predicting the impacts of an introduced species from its invasion history: An empirical approach applied to zebra mussel invasions. Freshw. Biol. 2003, 48, 972–981. [Google Scholar] [CrossRef]
  37. Crane, K.; Coughlan, N.E.; Cuthbert, R.N.; Dick, J.T.; Kregting, L.; Ricciardi, A.; MacIsaac, H.J.; Reid, N. Friends of mine: An invasive freshwater mussel facilitates growth of invasive macrophytes and mediates their competitive interactions. Freshw. Biol. 2020, 65, 1063–1072. [Google Scholar] [CrossRef]
  38. Šefrová, H.; Laštůvka, Z. Catalogue of alien animal species in the Czech Republic. Acta Univ. Agric. Silvic. Mendel. Brun. 2014, 53, 151–170. [Google Scholar] [CrossRef] [Green Version]
  39. Pergl, J.; Sádlo, J.; Petrusek, A.; Laštůvka, Z.; Musil, J.; Perglová, I.; Šanda, R.; Šefrová, H.; Šíma, J.; Vohralík, V.; et al. Black, Grey and Watch Lists of alien species in the Czech Republic based on environmental impacts and management strategy. NeoBiota 2016, 28, 1–37. [Google Scholar] [CrossRef]
  40. Patoka, J.; Bláha, M.; Kalous, L.; Kouba, A. Irresponsible vendors: Non-native, invasive and threatened animals offered for garden pond stocking. Aquat. Conserv. 2017, 27, 692–697. [Google Scholar] [CrossRef]
Figure 1. The voucher specimen of zebra mussel Dreissena polymorpha transported via the ornamental plant trade from Russia to the Czech Republic; scale bar is equal to 10 mm.
Figure 1. The voucher specimen of zebra mussel Dreissena polymorpha transported via the ornamental plant trade from Russia to the Czech Republic; scale bar is equal to 10 mm.
Diversity 13 00410 g001
Publisher’s Note: MDPI stays neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Share and Cite

MDPI and ACS Style

Patoka, J.; Patoková, B. Hitchhiking Exotic Clam: Dreissena polymorpha (Pallas, 1771) Transported via the Ornamental Plant Trade. Diversity 2021, 13, 410. https://doi.org/10.3390/d13090410

AMA Style

Patoka J, Patoková B. Hitchhiking Exotic Clam: Dreissena polymorpha (Pallas, 1771) Transported via the Ornamental Plant Trade. Diversity. 2021; 13(9):410. https://doi.org/10.3390/d13090410

Chicago/Turabian Style

Patoka, Jiří, and Barbora Patoková. 2021. "Hitchhiking Exotic Clam: Dreissena polymorpha (Pallas, 1771) Transported via the Ornamental Plant Trade" Diversity 13, no. 9: 410. https://doi.org/10.3390/d13090410

APA Style

Patoka, J., & Patoková, B. (2021). Hitchhiking Exotic Clam: Dreissena polymorpha (Pallas, 1771) Transported via the Ornamental Plant Trade. Diversity, 13(9), 410. https://doi.org/10.3390/d13090410

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop