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Gammarus roeseli

Gammarus roeselii is a species of freshwater amphipod native to Europe.[2]

Gammarus roeseli
Scientific classification Edit this classification
Domain: Eukaryota
Kingdom: Animalia
Phylum: Arthropoda
Class: Malacostraca
Order: Amphipoda
Family: Gammaridae
Genus: Gammarus
Species:
G. roeselii
Binomial name
Gammarus roeselii
Gervais, 1835 [1]
Synonyms

Gammarus roeselii (lapsus)
Rivulogammarus roeseli

Nomenclature

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Gervais described G. roeselii in 1835 under today's correct name G. roeselii GERVAIS , 1835. Since he wrote the description in Latin and used the Latinized name of the baron, i.e. "ROESELIUS", the genitive form is roeselii.[3] Therefore the spelling with double i is taxonomically correct, but often the spelling with only one i is often used.

Description

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Gammarus roeselii adult males reach a length of up to 22 mm; females are smaller than males.[4] The species is distinct from many other common amphipods due to the spines on its fifth through seventh pereiopods.[4] The color of G. roeselii individuals can vary from green to brown, gray, or yellow, and some have reddish markings on parts of their carapaces.[4]

Distribution

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Gammarus roeselii originated in the Balkan area of Europe, and appears to have populated the Pannonian Basin as a glacial refuge before expanding into central and western Europe 10,000 years ago.[5] It is now widespread across continental Europe.[2] Having been in France since at least the mid-1800s it is considered to be a well-established non-native species in central, northern, and western Europe.[6] However, it continues to expand its distribution range, including into new river basins in Italy in the 2010s.[7] Even within the same geographic area – for example in France – some refer to the species as being invasive[8] while others refer to it as being naturalized.[9]

Ecology

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Habitat

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Gammarus roeselii are found in freshwater environments such as ponds, lakes and streams.[4] They are more abundant at warmer temperatures compared to some co-occurring amphipod species.[10] Populations tend to be highest in rivers with moderate water flow and ample plants to be used as shelter.

Trophic interactions

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Gammarus roeselii are omnivores. Although they consume animal prey, their mouthparts are morphologically better adapted for consuming detritus and suspended particles, and for scraping algae and fungi off of detrital material and other surfaces.[11]

Gammarus roeselii are predated on by fish. The distinctive spines of G. roeselii were found in a laboratory experiment to be associated with defense against predation by brown trout.[8]

Like other gammaridean amphipods, G. roeselii serve as hosts for microsporidian parasites.[12] The parasites have a variety of effects on infected G. roeselii. Physiologically, infection can increase salinity tolerance.[13] Infection by some microsporidians can feminize male embryos and lead to female-biased sex ratios.[14] Infection status also alters predator-avoidance behavior in G. roeselii.[15]

Life history

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Males and females form precopulatory mating pairs; after mating, females carry eggs in a brood pouch and then release juveniles. Clutch size is variable, reaching up to 80 or more eggs for some females; clutch sizes are smaller, but eggs are larger, in the winter than during warmer months.[16] Development in the brood pouch can take anywhere from 10 to over 200 days depending on water temperature, and survival of embryos is highest between 10 and 16 °C.[10] Females can produce up to eight broods over their lifetimes.[16] Juveniles moult nine or ten times before reaching sexual maturity.[17]

Traits associated with range expansion

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Gammarus roeselii are a successful invasive species due to their high reproductive rate, tolerance to changing environmental conditions and unique anti-predation characteristics.[citation needed] G. roeselii's mechanism of invasion is still unknown but it is most likely due to human activities such as aquaculture or fish repopulation.[citation needed] G. roeselii were once used as a food source in commercial fisheries, so it is possible that some individuals escaped and were able to populate new areas.[citation needed] G. roeselii have the ability to easily attach their bodies to substrates by using the spines on its metasomes.[citation needed] These organisms are also able to survive out of water for several days at a time, making the transfer of G. roeselii feasible over land.[citation needed]

Sensitivity to environmental impacts

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A number of studies have investigated the effects of toxins and pollutants on G. roeselii. In the 1980s, the insecticides Dyfonate and Ditrifon (which has since been banned in the European Union, India, and other countries) were found to be toxic to G. roeselii.[18] More recently, investigations about imidacloprid, another insecticide, indicated sublethal effects on G. roeseli at environmentally-relevant levels,[19] including effects on reproductive females.[20] Silver nanoparticles have been found to reduce the feeding rate of G. roeseli.[21] The sensitivity of G. roeseli to different stressors may also be affected by infection of microsporidian parasites. For example, infected females were found to be more strongly affected by exposure to cadmium.[22]

References

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  1. ^ "Gammarus roeselii Gervais 1835". Fauna Europaea. 2007-05-04. Archived from the original on October 1, 2007.
  2. ^ a b "Gammarus roeselii Gervais 1835". Fauna Europaea. 2007-05-04. Retrieved 2021-03-01.
  3. ^ Pöckl, Manfred (2014). "Süßwasser-Amphipoden: eine Liebeserklärung? – Selbstreflexionen eines so genannten "Spezialisten"" (PDF). Denisia. 33: 369–392.
  4. ^ a b c d Karaman, Gordon S.; Pinkster, Sjouk (1977-01-01). "Freshwater Gammarus Species from Europe, North Africa and Adjacent Regions of Asia (Crustacea-Amphipoda). Part II. Gammarus Roeseli-Group and Related Species". Bijdragen tot de Dierkunde. 47: 165–196. doi:10.1163/26660644-04702003 – via BRILL.
  5. ^ Csapó, Hedvig; Krzywoźniak, Paula; Grabowski, Michal; Wattier, Remi; Bącela-Spychalska, Karolina; Mamos, Tomasz; Jelić, Mišel; Rewicz, Tomasz (2020-11-29). "Successful post-glacial colonization of Europe by single lineage of freshwater amphipod from its Pannonian Plio-Pleistocene diversification hotspot". Scientific Reports. 10 (1): 18695. doi:10.1038/s41598-020-75568-7. PMC 7596225. PMID 33122728.
  6. ^ Grabowski, Michał (2007). "Alien Crustacea in Polish waters – Amphipoda". Aquatic Invasions. 2 (1): 25–38. doi:10.3391/ai.2007.2.1.3.
  7. ^ Paganelli, Daniele; Gazzola, Andrea; Marchini, Agnese; Sconfietti, Renato (March 2015). "The increasing distribution of Gammarus roeselii Gervais, 1835: first record of the non-indigenous freshwater amphipod in the sub-lacustrine Ticino River basin (Lombardy, Italy)". BioInvasions Records. 4 (1): 37–41. doi:10.3391/bir.2015.4.1.06.
  8. ^ a b Bollache, LoÏc; Kaldonski, Nicolas; Troussard, Jean-Philippe; Lagrue, Clément; Rigaud, Thierry (September 2006). "Spines and behaviour as defences against fish predators in an invasive freshwater amphipod". Animal Behaviour. 72 (3): 627–633. doi:10.1016/j.anbehav.2005.11.020. S2CID 53167471.
  9. ^ Piscart, Christophe; Webb, Dennis; Beisel, Jean Nicolas (2007-09-01). "An acanthocephalan parasite increases the salinity tolerance of the freshwater amphipod Gammarus roeseli (Crustacea: Gammaridae)". Naturwissenschaften. 94 (9): 741–747. doi:10.1007/s00114-007-0252-0. ISSN 1432-1904. PMID 17487466. S2CID 20535998.
  10. ^ a b Pockl, M.; Humpesch, U. H. (June 1990). "Intra- and inter-specific variations in egg survival and brood development time for Austrian populations of Gammarus fossarum and G. roeselii (Crustacea: Amphipoda)". Freshwater Biology. 23 (3): 441–455. doi:10.1111/j.1365-2427.1990.tb00286.x. ISSN 0046-5070.
  11. ^ Maier, Gerhard; Mayer, Gerd; Waloszek, Dieter; Maas, Andreas (2009-01-01). "Mouthpart Morphology of Gammarus Roeselii Compared to a Successful Invader, Dikerogammarus Villosus (Amphipoda)". Journal of Crustacean Biology. 29 (2): 161–174. doi:10.1651/08-3056R.1. ISSN 0278-0372.
  12. ^ Haine, Eleanor R.; Brondani, Emilie; Hume, Kevin D.; Perrot-Minnot, Marie-Jeanne; Gaillard, Maria; Rigaud, Thierry (2004-09-01). "Coexistence of three microsporidia parasites in populations of the freshwater amphipod Gammarus roeselii: evidence for vertical transmission and positive effect on reproduction". International Journal for Parasitology. 34 (10): 1137–1146. doi:10.1016/j.ijpara.2004.06.006. ISSN 0020-7519. PMID 15380685.
  13. ^ Piscart, Christophe; Webb, Dennis; Beisel, Jean Nicolas (2007-08-06). "An acanthocephalan parasite increases the salinity tolerance of the freshwater amphipod Gammarus roeselii (Crustacea: Gammaridae)". Naturwissenschaften. 94 (9): 741–747. doi:10.1007/s00114-007-0252-0. ISSN 0028-1042. PMID 17487466. S2CID 20535998.
  14. ^ Haine, E. R.; Motreuil, S.; Rigaud, T. (September 2007). "Infection by a vertically-transmitted microsporidian parasite is associated with a female-biased sex ratio and survival advantage in the amphipod Gammarus roeseli". Parasitology. 134 (10): 1363–1367. doi:10.1017/S0031182007002715. ISSN 1469-8161. PMID 17445328. S2CID 5688353.
  15. ^ Médoc, Vincent; Rigaud, Thierry; Bollache, Loic; Beisel, Jean-Nicolas (May 2009). "A manipulative parasite increasing an antipredator response decreases its vulnerability to a nonhost predator". Animal Behaviour. 77 (5): 1235–1241. doi:10.1016/j.anbehav.2009.01.029. S2CID 53171571.
  16. ^ a b Pöckl, Manfred (1993). "Reproductive potential and lifetime potential fecundity of the freshwater amphipods Gammarus fossarunt and G. roeselii in Austrian streams and rivers". Freshwater Biology. 30 (1): 73–91. doi:10.1111/j.1365-2427.1993.tb00790.x. ISSN 1365-2427.
  17. ^ Pöckl, Manfred (1992). "Effects of temperature, age and body size on moulting and growth in the freshwater amphipods Gammarus fossarum and G. roeseli". Freshwater Biology. 27 (2): 211–225. doi:10.1111/j.1365-2427.1992.tb00534.x. ISSN 1365-2427.
  18. ^ Ponyi, J. E.; Bankós, L. (1985). "The effect of different pesticides on the amphipod Gammarus roeseli Gervais" (PDF). Miscellanea Zoologica Hungarica. 3: 83–90.
  19. ^ Böttger, R.; Schaller, J.; Mohr, S. (2012-07-01). "Closer to reality — the influence of toxicity test modifications on the sensitivity of Gammarus roeseli to the insecticide imidacloprid". Ecotoxicology and Environmental Safety. 81: 49–54. doi:10.1016/j.ecoenv.2012.04.015. ISSN 0147-6513. PMID 22575057.
  20. ^ Böttger, R.; Feibicke, M.; Schaller, J.; Dudel, G. (2013-07-01). "Effects of low-dosed imidacloprid pulses on the functional role of the caged amphipod Gammarus roeseli in stream mesocosms". Ecotoxicology and Environmental Safety. 93: 93–100. doi:10.1016/j.ecoenv.2013.04.006. ISSN 0147-6513. PMID 23664296.
  21. ^ Andreï, Jennifer; Pain-Devin, Sandrine; Felten, Vincent; Devin, Simon; Giambérini, Laure; Mehennaoui, Kahina; Cambier, Sebastien; Gutleb, Arno C.; Guérold, François (2016-01-01). "Silver nanoparticles impact the functional role of Gammarus roeseli (Crustacea Amphipoda)". Environmental Pollution. 208 (Pt B): 608–618. doi:10.1016/j.envpol.2015.10.036. ISSN 0269-7491. PMID 26552543.
  22. ^ Gismondi, Eric; Beisel, Jean-Nicolas; Cossu-Leguille, Carole (2012-07-20). "Polymorphus Minutus Affects Antitoxic Responses of Gammarus Roeseli Exposed to Cadmium". PLOS ONE. 7 (7): e41475. doi:10.1371/journal.pone.0041475. ISSN 1932-6203. PMC 3401126. PMID 22911795.
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