Dikerogammarus haemobaphes

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Dikerogammarus haemobaphes
Scientific classification
Kingdom:
Animalia
Phylum:
Arthropoda
Subphylum:
Crustacea
Class:
Malacostraca
Order:
Amphipoda
Family:
Gammaridae
Genus:
Dikerogammarus
Species:
D. haemobaphes
Binomial name
Dikerogammarus haemobaphes
(Eichwald, 1841)

Dikerogammarus haemobaphes is a species of freshwater gammarid crustacean. These gammarids are commonly known as demon shrimp, likely because they are an extremely successful invasive species.

Native to the Ponto Caspian basin, Dikerogammarus haemobaphes expanded their range in 1955.[1] This expansion began in Lake Balaton, Hungary and then spread into certain rivers and lakes in Austria, Belgium, Germany, Poland, Russia, Ukraine, and the United Kingdom.[1] These crustaceans likely broadened their range due to the interconnection of waterways in Europe and the use of transportation vectors such as boats and ships.[2]  

Identification[]

Dikerogammarus haemobaphes have a semi-transparent, white body consisting of a head, thorax, and abdomen.[3] Their body consists of seven segments, each with a pair of pereopods (walking legs). These shrimp are different from other gammarid species as their peduncle, flagellum of antennae, and gnathopods have short bristles rather than long ones.[3] Males average 16 mm in length, but can grow up to 21 mm. Females range between 7-15 mm long.[4]

Habitat preferences[]

Dikerogammarus haemobaphes have a wide salinity tolerance and are able to live in fresh and brackish water.[5] They are also considered a eurythermal species, because they can tolerate a wide range of thermal temperatures.[5]

Demon shrimp feed on sediments, detritus, unicellular and filamentous algae, and small crustaceans.[6] These shrimp prefer living in coarse grained cobble substrates, but can be found in all types of substrate.[7] Demon shrimp are also commonly found in the same environment as Dreissena polymorpha, or zebra muscles.[6] It has been found that Dikerogammarus haemobaphes prefer living on top of zebra muscle shells rather than other substrate types.[6]

Invasiveness[]

The first known invasion of Dikerogammarus haemobaphes was in Lake Balaton, Hungary in 1955.

The invasion of Dikerogammarus haemobaphes has been shown to negatively impact their new habitat. Demon shrimp are highly successful invaders due to their rapid growth rates and early maturation.[8] They also have a much higher fecundity than native gammarid species, making them able to increase their population quickly.[8] Their wide salinity tolerance, sediment preferences, and thermal tolerance also makes them able to successfully invade foreign ecosystems.

Amphipods play a major role in the energy flow within their environment due to their shredding and decomposition activities.[8] Dikerogammarus haemobaphes has been reported to have lower detrital processing efficiency than native amphipod shrimp, such as Gammarus pulex.[8] Therefore, a shift in the dominant amphipod species would lead to slower decomposition rates within the environment.[8] For these reasons, if the demon shrimp take over a particular environment, the energy flow would be altered, which will cause deleterious effects on that particular niche. Since leaf shredding provides fresh and brackish water ecosystems with carbon and organic matter, a decrease in shredding activities would cause these levels to drop.[9]

In addition to feeding on detritus, Demon shrimp also prey on native shrimp and insect species.[10] This cannibalistic behavior has a significant impact on community dynamics, disrupting local food chains, and altering ecosystem function.[8] The demon shrimp’s omnivorous diet also proves  advantageous over native gammarid species; as they have more available food sources to sustain their growth.[8] The wide habitat breadth, carnivorous activities, high fecundity, and rapid growth of Dikerogammarus haemobaphes makes this species an extremely successful invader.

References[]

  1. ^ a b US Fish and Wildlife Services (July 6, 2018). "Demon Shrimp (Dikerogammarus haemobaphes)" (PDF).
  2. ^ Baker, E (January 28, 2015). "Dikerogammarus haemobaphes (Eichwald, 1841)". Glansis.
  3. ^ a b Baker, E (January 28, 2015). "Dikerogammarus haemobaphes (Eichwald, 1841)". Glansis.
  4. ^ Schram, Frederick R.; Klein, Jan Carel von Vaupel (1999). Crustaceans and the Biodiversity Crisis: Proceedings of the Fourth International Crustacean Congress, Amsterdam, the Netherlands, July 20-24, 1998. BRILL. ISBN 978-90-04-11387-9.
  5. ^ a b Devin, S (April 21, 2006). "Biological and ecological characteristics of invasive species: a gammarid study". Biological Invasions. 9: 13–24. doi:10.1007/s10530-006-9001-0. S2CID 22417055.
  6. ^ a b c US Fish and Wildlife Services (July 6, 2018). "Demon Shrimp (Dikerogammarus haemobaphes)" (PDF).
  7. ^ Clinton, K (February 27, 2018). "Substrate preferences of coexisting invasive amphipods, Dikerogammarus villosus and Dikerogammarus haemobaphes, under field and laboratory conditions". Biological Invasions. 20 (8): 2187–2196. doi:10.1007/s10530-018-1695-2.
  8. ^ a b c d e f g Clinton, K (February 27, 2018). "Substrate preferences of coexisting invasive amphipods, Dikerogammarus villosus and Dikerogammarus haemobaphes, under field and laboratory conditions". Biological Invasions. 20 (8): 2187–2196. doi:10.1007/s10530-018-1695-2.
  9. ^ Louhi, P (June 16, 2016). "Sediment addition reduces the importance of predation on ecosystem functions in experimental stream channels". Canadian Journal of Fisheries and Aquatic Sciences. 74: 32–40. doi:10.1139/cjfas-2015-0530.
  10. ^ The Visitor (December 30, 2014). "Watch out for the Demon Shrimp on loose in river". The Visitor.
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