Pfiesteria shumwayae

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Pfiesteria shumwayae
Scientific classification
Kingdom: Protista Phylum: Dinoflagellata Class: Dinophyceae Order: Phytodiniales Family: Pfiesteriaceae Genus: Pfiesteria Species: P. shumwayae

Description and Significance

Pfiesteria shumwayae is a heterotrophic dinoflagellate belonging to the protist group pyrrophycophyta, or red algae. It was discovered by Dr. Burkholder at North Carolina State University in 1995. These dinoflagellates are found in warm coastal regions and temperate or tropical estuaries, and are known to cause massive fish kills via micropredation. It was once thought that fish kills in these areas were caused by exotoxin secretion by Pfiesteria, however recent research has shown that the parasitic feeding behavior of P. shumwayae is responsible for denuding fish of their epidermis and causing characteristic lesions on dead fish (Vogelbein, Lovko, Shields, Reece, Mason, Haas and Walker, 2002). They also prey on other protists, shellfish tissue, and micro-algal species such as cryptomonads. P. shumwayae cysts and excysted offspring feed on the epidermis of live fish and free floating cells that detach from fish. Pfiesteria is known to exhibit both sexual and asexual reproduction, but asexual reproduction is most common among these dinoflagellates. (Burkholder and Parrow, 2003)

It is also known that P. shumwayae can also have a serious, negative effect on human health. Fisherman who are frequently exposed to Pfiesteria reported having respiratory irritation, rashes, sores and lesions on their skin. Researchers working with P. shumwayae have noted experiencing headaches, dizziness and short-term memory loss. However, there is no evidence supporting illness in individuals who consumed Pfiesteria exposed seafood (North Carolina Public Health, 2006).

Genome structure

Not much research has been done to sequence the Pfiesteria genome probably because researchers are mainly concerned with its harmful environmental effects. Much focus has been put on the actual mechanisms that attribute to fish kills and how to mitigate P. shumwayae damage to fish populations.

Cell structure and Feeding Habits

P. shumwayae is a biflagellate phagotroph that feeds with a peduncle, or feeding tube which extends from its spherical body. The transverse flagellum is wrapped around it and the other is free flowing. The peduncle is used to ingest epidermal cytoplasm and other food matter via myzocytosis (Vogelbein, Lovko, Shields, Reece, Mason, Haas and Walker, 2002). Direct dinospore attachment to the epidermal surface of fish create abrasions and damage to fish tissue such as gills, olfactory organs, oral mucosa and the lateral line canal. After completion of dinospore feeding, the peduncle is stretched thin and retracts as it detaches from the fish to swim away (Burkholder and Parrow, 2003).

Lesions on fish caused by P. shumwayae

Research by Vogelbein, Lovko, Shields, Reece, Mason, Haas and Walker (2002), has shown that cell organelles such as mitochondria and rough endoplasmic reticulum was observed as it passed through the peduncle during feeding. As fish cytoplasm is taken up by the peduncle, the dinospore increases in size because the ingested materials are transported to a food vacuole that occupies most of the cell. Staining of the dinoflagellates after feeding revealed that the food vacuoles within them were filled with nucleic acids and lipids (Skelton, Burkholder and Parrow, 2008).

As P. shumwayae feeds, it uses its peduncle to pierce the cell membrane of its host, allowing host cell cytoplasm to flow through a small circular opening which contracts (Skelton, Burkholder and Parrow, 2008). This sphincter, observed by Calado and Moestrup (1997), contracts in order to control the amount of cytoplasm being ingested into and pushed out of the dinoflagellate’s food vacuole. Calado and Moestrup suggested a theory of two different mechanisms in which suction serves as the driving force behind cytoplasm ingestion.

During feeding, P.shumwayae exhibits cytoplasmic extensions or pseudopodia that are constantly extended and retracted for movement and attachment to host (Lom and Lawler, 1973). Up to six extensions were observed per cell. As the cell moves in response to chemosensory attraction, cytoplasmic extensions are left behind. Other flagellate cells are attracted by these entrails and were observed as they attached themselves to the entrails and ingested them (Skelton, Parrow and Burkholder, 2008). After feeding, on micro-algae and other prey, P. shumwayae leaves behind only the cell membrane; however it is noted that when it feeds on fish cells under anexic laboratory conditions, no visible cell membrane is left behind (Skelton, Burkholder and Parrow, 2008). In addition, research documented by Schnepf and Deichgraber (1984) supports that the cell membrane is not ingested during or after P. shumwayae feeding.

It has been noted that P. shumwayae can feed on prey several times larger than its own size; however feeding occurs on organisms that are usually injured ciliates, rotifers and nematodes. It has also been reported that the dinoflagellates can also ingest heterotrophic bacteria via phagocytosis, but this is an area that is in need of much research (Skelton, Burkholder and Parrow, 2008).

Toxicity

The Pfiesteria species contains P. shumwayae and P. piscicida, both of which have benign and toxic strains. The classification of toxicity in strains of Pfiesteria has to do with whether or not their exotoxins are inducible. In benign strains (NON-IND), toxins are not inducible; dinoflagellates are either not capable of toxic activity or the toxins they produce are negligible. Toxic strains that are actively toxic (TOX-A) or temporarily toxic (TOX-B) depend on whether there is live fish present. (Glasgow, Burkholder, Mallin, Deamer-Melia, and Reed, 2001) In the presence of live fish, P. shumwayae exhibits immediate chemotaxis to fish and gradually becomes toxic. According to research done by Glasgow, Burkholder, Mallin, Deamer-Melia, and Reed (2001), it was demonstrated that shortly after fish death, TOX-A strains of Pfiesteria ceased production of toxins and transformed into an amoeboid form that fed on dead fish remains. In the presence of other micro-algal prey, P. shumwayae reverted to the less toxic TOX-B form. Optimal temperature for toxicity is greater than or equal to 25°C.

Life cycle stages

Experiments were done that indicate toxic strains of P. shumwayae use exotoxins to weaken fish. They can also have effects on mammals as well. Toxins secreted by dinospores are similar to an ATP transmitter that targets the P2X7 receptor (Glasgow, Burkholder, Mallin, Deamer-Melia, and Reed, 2001), causing a severe inflammatory response. Cultured fish exposed to Pfiesteria toxins showed signs of depression, loss of equilibrium, hyper-excitability and decreased respiration. The physical, epidermal damage done to fish by Pfiesteria is speculated to increase the efficiency of toxins into fish tissues. Some strains of Pfiesteria that are less toxic do not kill fish unless it has direct contact with its prey (Glasgow, Burkholder, Mallin, Deamer-Melia, and Reed, 2001).

Reproduction

P. shumwayae shares phylogenic relationships with and shows similar reproductive patterns to the marine diatom ectoparasite Paulsenella and of Amyloodinium. It usually reproduces using asexual fission but is known to exhibit a sexual life cycle as well. Cellular division takes place in non-motile cells, like cysts, that undergo regular mitosis as a diploid zygote. The zygote then undergoes meiosis which results in 2 to 8 bi-flagellated offspring (Parrow and Burkholder, 2003).

In response to unfavorable stimuli, P. shumwayae cells will feed and then become non-motile primary cysts. The size of the cyst depends on how much food material was ingested and the cytoplasm. When isolated culture populations were starved, cells resorted to cannibalism and senescent cysts occurred in small sizes (Parrow and Burkholder, 2003)

Asexual

Diagram of the most commonly observed Pfiesteria shumwayae reproductive cyst development (nucleus represented by black oval)

Reproductive cysts were observed to have several protoplast divisions, internal to the plasma membrane which does not undergo division. (see diagram) The most common form of asexual reproduction of P. shumwayae cysts begins with a primary cyst. This primary cyst undergoes a protoplast division which can either result in two bi-flagellated offspring (A) or become a secondary cyst (B). The number of divisions and of offspring produced depends on the size of the primary cyst. The secondary cyst undergoes another protoplast division internal to the secondary cyst wall, releasing four bi-flagellated offspring (B). If the primary cyst was extremely large, the secondary cyst would undergo another protoplast division forming a tertiary cyst which releases eight bi-flagellated offspring (C). These divisions occur within several hours of each other. The food vacuole (represented by gray oval) present in the primary cyst is not divided amongst the offspring but grows smaller and is inherited by only one offspring (Parrow and Burkholder, 2003). It was observed that the offspring egested the food vacuole after excystment.

Sexual

In sexual reproduction of P. shumwayae, two gametes fuse to form a planozygote. The cell engages in nuclear cyclosis which produces two flagellated offspring. Some of the steps in reproduction are unknown because of the difficulty researchers have in documenting information. The vegetative cells and the gametes look very similar, and fusion can easily be confused with division, making it difficult to differentiate between cycle phases (Parrow and Burkholder, 2003). That is why after nuclear cyclosis, it is unknown whether another division takes place before the excystment of offspring (see diagram). According to Parrow and Burkholder’s research, reproduction in P. shumwayae seems to be unlinked to a survival strategy, and reverts to a sexual cycle because of self- sterility factors that favor outbreeding while taking advantage of food availability and environmental quality. File:Sexshum.jpg

Ecology

Fish kills in warm coastal estuarine waters are usually attributed to harmful algal blooms of Pfiesteria. It is not typical for these blooms to occur after hurricanes and storms or in “high-wave-action, wind mixed” surface waters because Pfiesteria prefers calm, quiet water conditions, like poorly drained brackish water (Glasgow, Burkholder, Mallin, Deamer-Melia, and Reed, 2001). It is implicated that the stress of low oxygen and hypoxia in such waters is the primary cause of these manifestations.

Current Research

It has been established that Pfiesteria shumwayae kills fish by feeding on its epidermis. Research by Skelton, Burkholder and Parrow (2001), supports the idea that Pfiesteria is responsible for fish kills and lesions on wild fish due to myzocytosis and not so much exotoxin release. Many fish kills documented in their on- site field research show that non-inducible and temporarily non-toxic strains of Pfiesteria were present during kills and were not actively toxic. But Vogelbein et al. (2002) stated that there is some ambiguity of the role Pfiesteria plays in the mortality of wild fish due to pathogenicity via micro-predation versus exotoxin release. This conclusion is logical because in vitro assays sometimes cannot discriminate fish kills caused by exotoxins of toxic strains or myzocytosis. It can be suggested that more research be done to propose a definite conclusion to this issue however, retrieving substantial and accurate information on fish kills using traditional research methods is difficult for several reasons: 1). Pfiesteria zoospores change phases or life cycle stages, and may settle out of the water column making it harder to detect and quantify 2). Since these occurrences are in the form of blooms, they tend to be ephemeral and 3). There are Pfiesteria–like species present in the field that are morphologically similar to Pfiesteria, making it difficult for researchers to identify and distinguish one from the other(Glasgow, Burkholder, Mallin, Deamer-Melia, and Reed, 2001).

References

Glasgow H.B., Burkholder, J.M., Mallin, M.A., Deamer- Melia N.J., and Reed, R.E. 2001. Field Ecology of Toxic Pfiesteria complex Species and a Conservative Analysis of Their Role in Estuarine Fish Kills. Environmental Health Perspectives 109(suppl 5):715-730.

North Carolina Public Health. "Pfiesteria." 2006. North Carolina Depaartment of Health and Public Services. 23 Apr. 2008. <http://www.epi.state.nc.us/epi/oee/pfie.html>

Parrow, M.W. and Burkholder, J.M. 2003. Reproduction and sexuality in Pfiesteria shumwayae (Dinophyceae). J. Phycol. 39:697-711.

Skelton, H.M., Burkholder, J.M. and Parrow, M.W. 2008. Axenic Cultivation of the Heterotrophic Dinoflagellate Pfiesteria shumwayae and Observations on Feeding Behavior. J. Phycol. 44:1614-1624.

Vogelbein, W.K., Lovko, V.J., Sheilds, J.D., Reece, K.S., Mason, P.L., Haas, L.W. and Walker C.C. 29 August 2002. Pfiesteria shumwayae kills fish by micropredation not exotoxin secretion. Nature 418:967-970.