Daphnia lumholtzi

Last updated

Daphnia lumholtzi
Scientific classification OOjs UI icon edit-ltr.svg
Domain: Eukaryota
Kingdom: Animalia
Phylum: Arthropoda
Class: Branchiopoda
Order: Anomopoda
Family: Daphniidae
Genus: Daphnia
Subgenus: Daphnia
Species:
D. lumholtzi
Binomial name
Daphnia lumholtzi
G. O. Sars, 1885

Daphnia lumholtzi is a species of small, invasive water fleas that originates in the tropical and subtropical lakes of Africa, Asia, and Australia. [1] [2] [3] As an invasive species, Daphnia lumholtzi disrupts aquatic habitats by spreading throughout the warmer waters of lakes and reservoirs.

Contents

Description

Daphnia lumholtzi is a small crustacean that is 2–3 mm in length. [4] It has a large helmet and a long tailspine, usually longer than the length of its body, [3] that fluctuates in size. [2] [5] Its body structure is arched, extending to a sharp point. [3] There are roughly 10 prominent spines on the margin of the abdominal shield covering. [3]

Ecology

Temperature

Daphnia lumholtzi is typically found in the warm, shallow regions [6] of bodies of water with larger surface areas. [7] While most species of Daphnia see high mortality at temperatures greater than 25 °C, [8] D. lumholtzi individuals can survive and reproduce at temperatures up to 30 °C, [8] [9] [10] with a thermal optimum occurring at 29 °C. [9] Studies have shown that population density and water surface temperature are positively correlated. [11] Once favorable temperatures are reached, such as those in the late summer, the previously deposited eggs hatch. The lower temperature range of D. lumholtzi extends to 5 °C, where some individuals are able to survive, [8] [9] [10] with survival increasing significantly at 10 °C [8] [10] and reproduction beginning to occur at 15 °C. [8] [10] This significantly broad temperature range in which D. lumholtzi can survive has led to it being labeled a eurythermal species. [12]

Behavior

Both adult and juvenile D. lumholtzi exhibit a vertical migration pattern, moving upward as the sun sets and downward as the sun rises. This behavior leads to large population densities close to the water surface at night and also occurs in the absence of a suggested predator threat. [10]

Diet

Daphnia lumhotzi mostly feeds on phytoplankton ranging from 1 to 25 micrometers in size, [13] but will also eat foods that contain organic detritus, bacteria, and protists which provide an excellent source of nutrients. [4] [13]

Dispersal

Daphnia lumholtzi was originally restricted to the tropical lake and pond regions of southwest Asia, Australia, and most of Africa. [14] The exact location of geographic origin in the United States has not been identified, but scientists believe the introduction of exotic African fish to lakes most likely caused the distribution. [14] It was first detected in Missouri and Texas reservoirs in 1991 and has since been found in more than 16 states and over 125 lakes and reservoirs. [15] Studies have shown that the ability of D. lumholtzi to disperse widely is most likely due to human activity. [5] Heavy boat traffic on lakes and reservoirs during warmer seasons when D. lumholtzi thrive enable them to expand into other nearby bodies of water. [16] The long spines and hairs on eggs act as hooks and enable attachment to boats, facilitating dispersal. The presence of D. lumholtzi in smaller ponds is atypical; however it is unlikely that non-human dispersal mechanisms, such as smaller invertebrates moving between bodies of water, have contributed to its widespread distribution. [5]

Reproduction

Daphnia lumholtzi deposits eggs in lake sediment that can remain dormant for long periods of time. The eggs are characterized by long spines and hairs that act as hooks. [1] Ephippia are protective shells that cover the egg until favorable conditions occur, such as warmer temperatures or a larger amount of resources. These ephippia are able to survive in environmental conditions, including oxygen, salinity, and temperature ranges, that are inhospitable to adult daphnids, although exact ranges for D. lumholtzi ephippia have not been found. [5] This ephippia stage is an example of diapause, a state of suspended animation an organism can enter in order to survive a harsh environment. [17] D. lumholtzi is capable of producing 10 times more ephippia than other daphnid species. [18] In temperatures above the optimal temperature for reproduction, 25 °C, the rate of egg development decreases. [19] In temperatures below 25 °C, egg development slows. [20]

Predators

The main predators of D. lumholtzi are fish and small invertebrate species. Larger fish are almost always successful in their encounters with D. lumholtzi. [14] Small invertebrate predators are less efficient than large fish in catching D. lumholtzi.

Physiology

Being an invasive species, the physiology of D. lumholtzi is relatively well studied for a daphnid.

Respiration

Daphnia lumholtzi individuals prefer areas with high levels of dissolved oxygen and avoid areas where oxygen levels are low. Population surveys have found robust D. lumholtzi populations in water with oxygen saturation levels ranging from 65-163%, while no populations were found in water with saturation levels ranging from 7-50%. [21] The mechanism D. lumholtzi uses for respiration is very similar to that used by other species of Daphnia, with gas exchange occurring through gills that are fed oxygenated water by appendages on the thorax. [22]

Response to salinity

As with most other members of the order Cladocera, D. lumholtzi lives in freshwater and is hyperosmotic to its environment. [23] D. lumholtzi is generally found in habitats with a salinity near 0 grams per liter, but can withstand slightly saline water, up to 1.5 grams per liter, for short amounts of time. [23] This ability to survive short bouts of salinity has likely contributed to D. lumholtzi’s ability to invade North America. [23]

As an invasive species

Daphnia lumholtzi exhibits higher survivorship and reproduction in the late summer, under high heat conditions, when compared to other crustaceans living in these conditions. It has been suggested that D. lumholtzi’s more tropical origins may have enabled it to live in these higher temperatures [15] due to evolutionary changes that resulted in enzymes that are better adapted to the heat. [12] This advantage allows them to be a better competitor and ultimately out-compete other species, specifically native zooplankton species, within the same habitat and come out as a successful invader. In accordance with the competitive exclusion principle, no other species can inhabit the same late summer niche as D. lumholtzi; another factor that allows it to have higher survivorship than other Daphnia species and is ultimately a better invader. It is important to note, however, that high survivorship and reproduction are not the only factors that make D. lumholtzi an invasive species.

Competition between D. lumholtzi is increased in habitats that favor the high light intensity of shallow waters. D. lumholtzi showed greater survivorship than other Daphnia species (specifically D. pulex ), which made them a stronger competitor for light reception and resources in bodies of water receiving high light intensity. It was found to out-compete other species in areas with high light intensity which in turn contributes to its invasive success. [24]

Daphnia lumholtzi is capable of producing 10 times more ephippia than other daphnid species, [18] which can remain dormant until favorable conditions occur. This egg bank gives them an advantage over other species whose eggs cannot withstand desiccation or lower temperatures, [5] enabling them to produce more offspring that survive longer. The reproductive rate also increases with a higher concentration of food. [19] Areas exhibiting high food abundance will therefore attract more D. lumholtzi, and in turn result in a higher rate of reproduction. [24] The greater number of offspring puts pressure on the habitat’s resources and other competitors.

Daphnia lumholtzi is highly plastic, [15] meaning it has the ability to morphologically adapt to factors within the environment by developing structures that enable it to successfully avoid predation. A long tail spine, large helmet, and additional spines on the abdomen are produced in response to predator kairomones, which are predator hormones, within the water. D. lumholtzi does not produce these protective structures when there are no predators present, and looks morphologically similar to other Daphnia species. When predators are detected, D. lumholtzi responds by producing a tail spine, helmet, abdomen spines for protection; other Daphnia species do not adapt this way to predator threats. With the development of these morphological features, predators have a more difficult time preying on D. lumholtzi. This excess energy the predators put into eating D. lumholtzi lessens predator efficiency, making the predators more likely to choose another prey. [14] This prey-switching puts an extra strain on other native zooplankton species, reducing predation on D. lumholtzi and allowing it to outperform other competitors. [11]

Control

Eradication of D. lumholtzi is almost impossible once it has invaded a lake or reservoir. D. lumholtzi is sensitive to various pesticides and manmade chemicals, [4] but the introduction of chemicals to natural lakes is often harmful to other species. The focus of most control measures is the prevention of initial invasion. For now, scientists recommend simple practices, such as thorough cleaning of boats and avoiding aquarium water dumps, to slow the spread of the species. [25]

Related Research Articles

<span class="mw-page-title-main">Centrarchidae</span> Family of fishes

Centrarchidae, better known as sunfishes, is a family of freshwater ray-finned fish belonging to the order Perciformes, native only to North America. There are eight universally included genera within the centrarchid family: Lepomis, Micropterus, Pomoxis (crappies), Enneacanthus, Centrarchus, Archoplites, Ambloplites, and Acantharchus. A genetic study in 2012 suggests that the highly distinct pygmy sunfishes of the genus Elassoma are also centrarchids.

<i>Daphnia</i> Genus of crustaceans

Daphnia is a genus of small planktonic crustaceans, 0.2–6.0 mm (0.01–0.24 in) in length. Daphnia are members of the order Anomopoda, and are one of the several small aquatic crustaceans commonly called water fleas because their saltatory swimming style resembles the movements of fleas. Daphnia spp. live in various aquatic environments ranging from acidic swamps to freshwater lakes and ponds.

<span class="mw-page-title-main">Bigmouth buffalo</span> Species of fish

The bigmouth buffalo is a fish native to North America. It is the largest North American species in the Catostomidae or "sucker" family, and is one of the longest-lived and latest-maturing freshwater fishes, capable of living 127 years and reproducing infrequently. Even at a century old they show no age-related declines, but instead improvements relative to younger individuals, making this species a biological marvel. It is commonly called the gourdhead, marblehead, redmouth buffalo, buffalofish, bernard buffalo, roundhead, or brown buffalo. The bigmouth buffalo is not a carp, nor is any other fish in the sucker family. Although they share the same order, each belong to different suborders and are native to separate continents.

<span class="mw-page-title-main">Freshwater fish</span> Fish that mostly live in freshwater

Freshwater fish are those that spend some or all of their lives in fresh water, such as rivers and lakes, with a salinity of less than 1.05%. These environments differ from marine conditions in many ways, especially the difference in levels of salinity. To survive fresh water, the fish need a range of physiological adaptations.

<i>Cercopagis pengoi</i> Species of small freshwater animal

Cercopagis pengoi, or the fishhook waterflea, is a species of planktonic cladoceran crustaceans that is native in the brackish fringes of the Black Sea and the Caspian Sea. In recent decades it has spread as an invasive species to some freshwater waterways and reservoirs of Eastern Europe and to the brackish Baltic Sea. Further it was introduced in ballast water to the Great Lakes of North America and a number of adjacent lakes, and has become a pest classified among the 100 worst invasive species of the world.

<span class="mw-page-title-main">Gammarus roeseli</span> Species of crustacean

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

<i>Bythotrephes longimanus</i> Spiny water flea

Bythotrephes longimanus, or the spiny water flea, is a planktonic crustacean less than 15 millimetres (0.6 in) long. It is native to fresh waters of Northern Europe and Asia, but has been accidentally introduced and widely distributed in the Great Lakes area of North America since the 1980s. Bythotrephes is typified by a long abdominal spine with several barbs which protect it from predators.

<span class="mw-page-title-main">White-faced darter</span> Species of dragonfly

The white-faced darter or small whiteface is a dragonfly belonging to the genus Leucorrhinia in the family Libellulidae, characterised by red and black markings and a distinctive white patch on the head. It is found in wetlands and peat bogs from northern Europe eastwards to Siberia, and the adults are active from around April till September, which is known as the "flight period". It breeds in acidic bodies of water, laying its eggs in clumps of sphagnum moss that provide a safe habitat for larval development. The larvae are particularly vulnerable to predation by fish, and so are usually found in lakes where fish are not present. L. dubia is listed as a species of least concern (LC) by the IUCN Red List, however, it is potentially threatened by habitat destruction, pollution, and climate change.

<span class="mw-page-title-main">Diplostraca</span> Order of small freshwater animals

The Diplostraca or Cladocera, commonly known as water fleas, is a superorder of small, mostly freshwater crustaceans, most of which feed on microscopic chunks of organic matter, though some forms are predatory.

<i>Daphnia pulex</i> Species of small freshwater animal

Daphnia pulex is the most common species of water flea. It has a cosmopolitan distribution: the species is found throughout the Americas, Europe, and Australia. It is a model species, and was the first crustacean to have its genome sequenced.

<i>Daphnia magna</i> Species of small freshwater animal

Daphnia magna is a small planktonic crustacean that belongs to the subclass Phyllopoda.

Ceriodaphnia dubia is a species of water flea in the class Branchiopoda, living in freshwater lakes, ponds, and marshes in most of the world. They are small, generally less than 1 millimetre (0.039 in) in length. Males are smaller than females. C. dubia moves using a powerful set of second antennae, and is used in toxicity testing of wastewater treatment plant effluent water in the United States. Climate change and particularly ultraviolet radiation B may seriously damage C. dubia populations, as they seems to be more sensitive than other cladocerans such as Daphnia pulex or D. pulicaria.

<i>Leptodora</i> Genus of small freshwater animals

Leptodora is a genus containing two species of large, nearly transparent predatory water fleas. They grow up to 21 mm (0.83 in) long, with two large antennae used for swimming and a single compound eye. The legs are used to catch copepods that it comes into contact with by chance. Leptodora kindtii is found in temperate lakes across the Northern Hemisphere and is probably the only water flea species ever described in a newspaper; L. richardi is only known from eastern Russia. For most of the year, Leptodora reproduces parthenogenetically, with males only appearing late in the season, to produce winter eggs which hatch the following spring. Leptodora is the only genus in its family, the Leptodoridae, and suborder, Haplopoda.

<i>Dikerogammarus villosus</i> Species of crustacean

Dikerogammarus villosus, also known as the killer shrimp, is a species of amphipod crustacean native to the Ponto-Caspian region of eastern Europe, but which has become invasive across the western part of the continent. In the areas it has invaded, it lives in a wide range of habitats and will prey on many other animals. It is fast-growing, reaching sexual maturity in 4–8 weeks. As it has moved through Europe, it threatens other species and has already displaced both native amphipods and previous invaders.

<i>Notonecta maculata</i> Species of true bug

Notonecta maculata is a backswimmer of the family Notonectidae, found in Europe, including the United Kingdom.

<span class="mw-page-title-main">Ephippia</span> Eggs of small crustacea

Ephippia are winter or dry-season eggs of the various species of small crustacean in the order Cladocera ; they are provided with an extra shell layer, which preserves and protects the resting stages inside from harsh environmental conditions until the more favorable times, such as spring, when the reproductive cycle is able to take place once again. Ephippia are part of the back of a mother carrying them until they are fully developed. After molting, the ephippium stays in the water, or in the soil of dried puddles, small ponds, and vernal pools. The resting stages are often called eggs, but are in fact embryos with arrested development. Ephippia can rest for many years before the embryo resumes development upon an appropriate hatching stimulus.

Carla Cáceres is a professor at the University of Illinois Urbana-Champaign known for her research in population, community and evolutionary ecology, focusing on the origins, maintenance, and functional significance of biodiversity within ecosystems. She is a Fellow of the American Association for the Advancement of Science, the Ecological Society of America, and the Association for the Sciences of Limnology and Oceanography

<i>Ambassis macleayi</i> Species of fish

Ambassis macleayi, commonly known as Macleay's glassfish, Macleay's glass perchlet, Macleay's perchlet, reticulated glassfish, reticulated perchlet, or network perchlet, is a species of freshwater fish in the family Ambassidae. It is native to northern Australia and the trans-Fly River region of New Guinea. It is a fish with a vertically flat, narrow body and a standard length generally between 35 and 45 mm, with large specimens reaching 77 mm (3.0 in) long. It generally eats water fleas and other small invertebrates. This fish is considered to be a least-concern species according to the International Union for Conservation of Nature (IUCN), although it could suffer from habitat degradation due to feral pigs and invasive water plants such as the water hyacinth. The fish is suitable for aquarium use in tanks containing other non-aggressive species.

<i>Daphnia longispina</i> Species of small freshwater animal

Daphnia longispina is a planktonic crustacean of the family Daphniidae, a cladoceran freshwater water flea. It is native to Eurasia. D. longispina is similar in size and sometimes confused with the often sympatric D. pulex, but much smaller than D. magna. D. longispina is found in a wide range of standing freshwater bodies from small, ephemeral rock-pools to large lakes.

<i>Daphnia pulicaria</i> Species of small freshwater animal

Daphnia pulicaria is a species of freshwater crustaceans found within the genus of Daphnia, which are often called "water fleas," and they are commonly used as model organisms for scientific research Like other species of Daphnia, they reproduce via cyclic parthenogenesis. D. pulicaria are filter-feeders with a diet primarily consisting of algae, including Ankistrodesmus falcatus, and they can be found in deep lakes located in temperate climates. Furthermore, D. pulicaria are ecologically important herbivorous zooplankton, which help control algal populations and are a source of food for some fish. D. pulicaria are closely related to Daphnia pulex, and numerous studies have investigated the nature and strength of this relationship because these species can produce Daphnia pulex-pulicaria hybrids. In recent years, D. pulicaria along with other Daphnia species have been negatively affected by invasive predators, such as Bythotrephes longimanus.

References

  1. 1 2 Kumud Acharya; Jeffrey D. Jack; Allison S. Smith (2006). "Stoichiometry of Daphnia lumholtzi and their invasion success: are they linked?" (PDF). Archiv für Hydrobiologie . 165 (4): 433–453. doi:10.1127/0003-9136/2006/0165-0433.
  2. 1 2 Andrew R. Dzialowski; Jay T. Lennon; W. J. O'Brien; Val H. Smith (2003). "Predator-induced phenotypic plasticity in the exotic cladoceran Daphnia lumholtzi". Freshwater Biology . 48 (9): 1593–1602. doi:10.1046/j.1365-2427.2003.01111.x. S2CID   15803644.
  3. 1 2 3 4 John E. Havel; Paul D. N. Hebert (1993). "Daphnia lumholtzi in North America: another exotic zooplankter" (PDF). Limnology and Oceanography . 38 (8): 1823–1827. doi:10.4319/lo.1993.38.8.1823. JSTOR   2838457. Archived from the original (PDF) on 2011-07-20. Retrieved 2011-04-19.
  4. 1 2 3 Douglas Grant Smith (2001). Pennak's Freshwater Invertebrates of the United States: Porifera to Crustacea (4th ed.). John Wiley & Sons. ISBN   978-0-471-35837-4.
  5. 1 2 3 4 5 Andrew R. Dzialowski; W. John O'Brien; Steve M. Swaffar (2000). "Range expansion and potential dispersal mechanisms of the exotic cladoceran Daphnia lumholtzi". Journal of Plankton Research . 22 (12): 2205–2223. doi: 10.1093/plankt/22.12.2205 . S2CID   55968164.
  6. Therese L. East; Karl E. Havens; Andrew J. Rodusky; Mark A. Brady (1999). "Daphnia lumholtzi and Daphnia ambigua: population comparisons of an exotica and a native cladoceran in Lake Okeechobee, Florida". Journal of Plankton Research . 21 (8): 1537–1551. doi: 10.1093/plankt/21.8.1537 .
  7. John E. Havel; Jonathan B. Shurin; John R. Jones (2005). "Environmental limits to a rapidly spreading exotic cladoceran". Écoscience . 12 (3): 376–385. doi:10.2980/i1195-6860-12-3-376.1.
  8. 1 2 3 4 5 Lennon, Jay T.; Smith, Val H.; Williams, Kim (2001-04-01). "Influence of Temperature on Exotic Daphnia lumholtzi and Implications for Invasion Success". Journal of Plankton Research. 23 (4): 425–433. doi: 10.1093/plankt/23.4.425 . ISSN   0142-7873.
  9. 1 2 3 Engel, Katharina; Tollrian, Ralph (2012-01-01). "Competitive ability, thermal tolerance and invasion success in exotic Daphnia lumholtzi". Journal of Plankton Research. 34 (1): 92–97. doi: 10.1093/plankt/fbr083 . ISSN   0142-7873.
  10. 1 2 3 4 5 John E. Havel; Winfried Lambert (2006). "Habitat partitioning of native and exotic Daphnia in gradients of temperature and food: mesocosm experiments". Freshwater Biology . 51 (3): 487–498. doi: 10.1111/j.1365-2427.2006.01511.x .
  11. 1 2 Cynthia S. Kolar; James C. Boase; David F. Clapp; David H. Wahl (1997). "Potential effect of invasion by an exotic zooplankter, Daphnia lumholtzi". Journal of Freshwater Ecology . 12 (4): 521–530. doi: 10.1080/02705060.1997.9663566 .
  12. 1 2 Yurista, Peder M. (2004-12-01). "Bioenergetics of a Semi-Tropical Cladoceran, Daphnia Iumholtzi". Journal of Freshwater Ecology. 19 (4): 681–694. doi:10.1080/02705060.2004.9664750. ISSN   0270-5060.
  13. 1 2 James H. Thorp; Alan P. Covich (2001). Ecology and Classification of North American Freshwater Invertebrates. Academic Press. ISBN   978-0-12-690647-9.
  14. 1 2 3 4 Katharina Engel; Ralph Tollrian (2009). "Inducible defences as key adaptations for the successful invasion of Daphnia lumholtzi in North America?". Proceedings of the Royal Society B . 276 (1663): 1865–1873. doi:10.1098/rspb.2008.1861. PMC   2674494 . PMID   19324783.
  15. 1 2 3 Jay T. Lennon; Val H. Smith; Kim Williams (2001). "Influence of temperature on exotic Daphnia lumholtzi and implications for invasion success". Journal of Plankton Research . 23 (4): 425–434. doi: 10.1093/plankt/23.4.425 .
  16. Havel, John E.; Shurin, Jonathan B.; Jones, John R. (December 2002). "Estimating dispersal from patterns of spread: Spatial and local control of lake invasions". Ecology. 83 (12): 3306–3318. doi:10.1890/0012-9658(2002)083[3306:EDFPOS]2.0.CO;2. S2CID   31301830.
  17. Wilmer, Pat; Stone, Graham; Johnston, Ian (2009). Environmental Physiology of Animals . Wiley. pp.  213. ISBN   9781405107242.
  18. 1 2 Allison S. Smith; Kumud Acharya; Jeffrey Jack (2009). "Overcrowding, food and phosphorus limitation effects on ephippia production and population dynamics in the invasive species Daphnia lumholtzi". Hydrobiologia . 618 (1): 47–56. doi:10.1007/s10750-008-9546-2.
  19. 1 2 Kirsten A. Work; Moshe Gophen (1999). "Factors which affect the abundance of an invasive cladoceran, Daphnia lumholtzi, in US reservoirs". Freshwater Biology . 42 (1): 1–10. doi:10.1046/j.1365-2427.1999.00449.x.
  20. Kirsten Kessler; Winfried Lampert (2004). "Depth distribution of Daphnia in response to a deep-water algal maximum: the effect of body size and temperature gradient". Freshwater Biology . 49 (4): 392–401. doi:10.1111/j.1365-2427.2004.01190.x.
  21. Davidson, Norman L. Jr; Kelso, William E. (1997-09-01). "The exotic daphnid, Daphnia lumholtzi, in a Louisiana river-swamp". Journal of Freshwater Ecology. 12 (3): 431–435. doi:10.1080/02705060.1997.9663553. ISSN   0270-5060.
  22. Pennak, Robert (1978). Freshwater Invertebrates of the United States. p. 454. ISBN   9780471358374.
  23. 1 2 3 DeVries, Dennis R.; Wright, Russell A.; DeVries, Tammy S. (2006-09-01). "Daphnia lumholtzi in the Mobile River Drainage, USA: Invasion of a Habitat That Experiences Salinity". Journal of Freshwater Ecology. 21 (3): 527–530. doi: 10.1080/02705060.2006.9665031 . ISSN   0270-5060.
  24. 1 2 Hao Wang; Katherine Dunning; James J. Elser; Yang Kuang (2009). "Daphnia species invasion, competitive exclusion, and chaotic coexistence" (PDF). Discrete and Continuous Dynamical Systems. Series B. 12 (2): 481–493. doi: 10.3934/dcdsb.2009.12.481 .
  25. James A. Stoeckel; Patrice M. Charlebois (1999). "Daphnia lumholtzi: the next Great Lakes exotic?" (PDF). Illinois-Indiana Sea Grant College Program, Illinois Natural History Survey & University of Illinois at Urbana-Champaign. Archived from the original (PDF) on 2010-05-29.