Chrysochromulina

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Chrysochromulina
HaptonemaChrysochromulinaFL.jpg
Chrysochromulina
Scientific classification
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Chrysochromulina

Lackey, 1939 [1]
Illustration: Chrysochromulina Prymnesiophyceae009-Chrysochromulina.jpg
Illustration: Chrysochromulina

Chrysochromulina is a genus of haptophytes. This phytoplankton is distributed globally in brackish and marine waters across approximately 60 known species. [2] [3] All Chrysochromulina species are phototrophic, however some have been shown to be mixotrophic, including exhibiting phagotrophy under certain environmental conditions. [3] The cells are small, characterized by having scales, and typically observed using electron microscopy. [2] [3] Some species, under certain environmental conditions have been shown to produce toxic compounds that are harmful to larger marine life including fish. [2] [3] [4]

Morphology

Individuals of the genus are known to grow between 3.0 and 13.0 μm in length, with the largest being those of the Chrysochromulina polylepis species. [2] The cell surface is covered with plate-like scales, with additional layers of different scale types often overlaid. [2]

As is characteristic of all haptophytes, members of the genus Chrysochromulina possess two flagella and a unique flagella-like organelle known as the haptonema. [5] The haptonema can vary widely in length, reaching upwards of 60 μm, [2] and functions in cell attachment and feeding but differs from flagella in terms of microtubule arrangement, [5]

Ecological Significance

Chrysochromulina, as one genus of haptophytes, holds an essential role in global carbon sequestration and toxic bloom formation in world's ocean. Most haptophytes are photosynthetic micro-alga while some of them are mixotrophic. [6] Haptophytes can live in both fresh and marine water systems. This combined lifestyle makes haptophytes efficient organisms in global carbon fixation, and they occupy 30% to 50% photosynthetic biomass in the ocean. [7]

Haptophytes have an evolutionary history around 1.2 billion years long. [6] The evidence from fossils support this statement. In 2014, The draft genome sequence of Chrysochromulina tobinii has been posted by researchers from University of Washington. [6] [8] C. tobinii belongs to the taxon Prymnesiales. As the first complete genome graph in this taxon, it can provide a broad understanding of haptophytes' evolutionary history and the diversity of this clade of algae. Furthermore, it promoted the study about certain genomes and proteins which are responsible for the toxic formation and chemical release. [8]

Toxicity

Some species, such as Chrysochromulina polylepis , have been identified to produce a carbon-heavy membrane damaging toxin. [4] Research has suggested a correlation between marine nitrogen/phosphorus compositions and toxin production levels of these haptophytes; previously recorded high levels of nitrate combined with a low concentration of phosphorus led to rises in toxicity during algal blooms. [9] Further research has since determined that both low nitrogen or low phosphorus levels in the cells capable of leading to an increase in toxin production, with phosphorus proving to be slightly more influential. [4]

Despite this correlation, it unlikely that nitrogen or phosphorus are directly linked to toxin formulation, as the toxins themselves are heavily carbon-based. [4] Additionally, other growth-limiting factors such as light and salinity have also been known to increase toxicity, suggesting that the toxins where selective advantage for cell defense during times of low growth. [4] As such, studies support the idea that the metabolic responses to cellular stresses on an environmental and physiological level due to nutrient limitations are responsible for such toxin productions. [4]

Chrysochromulina blooms

Many Chrysochromulina species have been found to form algal blooms around the world. [10] Some of these blooms in the North Atlantic can produce compounds that are toxic to other marine organisms under the correct environmental conditions. [3] [10] [11] It is common for blooms to be formed between April and August in Scandinavian coastal waters, however the specific Chrysochromulina species present varies from year to year. [3] [10]

Toxic bloom of 1988

In the late spring of 1988 the Chrysochromulina bloom that travelled from the Kattegat to the Skagerrak was made up of only one species, C. polylepis. [10] [11] This particular bloom was toxic to other marine organisms including protozoa, invertebrates, and 900 tonnes of farmed fish due to the production of haemolytic compounds by C. polylepis. [10] [11] C. polylepis is not typically toxic at the concentrations commonly found in the region, however certain environmental conditions such as strong stratification with a warm surface layer and low salinity following a winter featuring high amounts of nitrogen run-off increasing the N:P ratio is believed to have led to the successful C. plylepis bloom. [3] [10] [11] It is also thought that the production of these toxic compounds limited grazing of C. polylepis allowing for the bloom to be dominated by a single species. [10] The toxic effects seemed to reverse quickly and the food web was restored by 1993. [10] [11]

Kattegat bloom in 1992

From April to May in 1992, in the southern Kattegat there was a large bloom made up of many phytoplankton species, with over 90% biomass being Chrysochromulina species. [12] The most abundant species in the bloom were C. hirta, C. spinifera, C. ericina, C. brevifilum and an undescribed species. [12] C. hirta, C. spinifera, and C. ericina are characterized as relatively small cells with long spines protruding to give the overall organisms a 25-76 μm diameter which is too large for the ciliates present to engulf which is likely one reason that the bloom was so successful. [12] Another likely reason for the success of the bloom was the low presence of grazers in the bloom, about 5% of the Chrysochromulina species. [12] There was no evidence directly correlating this bloom or the species present to the production of toxins like the C. polylepis bloom in 1988. [11] [12]

Major viral pathogens

Two major viruses have been found to infect Chrysochromulina: CpV-BQ1 and CeV-01B. [13] [14] Freshwater samples from Lake Ontario were filtered and analyzed using transmission electron microscopy to identify the CpV-BQ1 virus. CpV-BQ1 is an icosahedral nucleocytoplasmic large DNA virus with a genome size 485kb. It is a member of the Megavirales order with characteristics of phycodnaviridae and mimivirus families. Concentrations of Chrysochromulina Lake Ontario were found to be consistent, while the CpV-BQ1 concentrations varied greatly. [13]

CeV-01B was first isolated from coastal Norwegian waters in 1998. It is an icosahedral double stranded DNA virus with a genome size of 474kb. CeV-01B belongs to a subclade of the Megaviridae family. [14]

Related Research Articles

<span class="mw-page-title-main">Algal bloom</span> Spread of planktonic algae in water

An algal bloom or algae bloom is a rapid increase or accumulation in the population of algae in freshwater or marine water systems. It is often recognized by the discoloration in the water from the algae's pigments. The term algae encompasses many types of aquatic photosynthetic organisms, both macroscopic multicellular organisms like seaweed and microscopic unicellular organisms like cyanobacteria. Algal bloom commonly refers to the rapid growth of microscopic unicellular algae, not macroscopic algae. An example of a macroscopic algal bloom is a kelp forest.

<span class="mw-page-title-main">Haptophyte</span> Type of algae

The haptophytes, classified either as the Haptophyta, Haptophytina or Prymnesiophyta, are a clade of algae.

<span class="mw-page-title-main">Eutrophication</span> Excessive plant growth in water

Eutrophication is a general term describing a process in which nutrients accumulate in a body of water, resulting in an increased growth of microorganisms that may deplete the water of oxygen. Although eutrophication is a natural process, manmade or cultural eutrophication is far more common and is a rapid process caused by a variety of polluting inputs including poorly treated sewage, industrial wastewater, and fertilizer runoff. Such nutrient pollution usually causes algal blooms and bacterial growth, resulting in the depletion of dissolved oxygen in water and causing substantial environmental degradation.

<span class="mw-page-title-main">Cyanobacteria</span> Phylum of photosynthesising prokaryotes that can produce toxic blooms in lakes and other waters

Cyanobacteria, also called Cyanobacteriota or Cyanophyta, are a phylum of autotrophic gram-negative bacteria that can obtain biological energy via photosynthesis. The name 'cyanobacteria' refers to their color, which similarly forms the basis of cyanobacteria's common name, blue-green algae, although they are not scientifically classified as algae. They appear to have originated in a freshwater or terrestrial environment.

<span class="mw-page-title-main">Cyanotoxin</span> Toxin produced by cyanobacteria

Cyanotoxins are toxins produced by cyanobacteria. Cyanobacteria are found almost everywhere, but particularly in lakes and in the ocean where, under high concentration of phosphorus conditions, they reproduce exponentially to form blooms. Blooming cyanobacteria can produce cyanotoxins in such concentrations that they can poison and even kill animals and humans. Cyanotoxins can also accumulate in other animals such as fish and shellfish, and cause poisonings such as shellfish poisoning.

Prymnesium parvum is a species of haptophyte. The species is of concern because of its ability to produce the phycotoxin prymnesin. It is a flagellated alga that is normally found suspended in the water column. It was first identified in North America in 1985, but it is not known if it was introduced artificially or missed in previous surveys. Toxin production mainly kills fish and appears to have little effect on cattle or humans. This distinguishes it from a red tide, which is an algal bloom whose toxins lead to harmful effects in people. Although no harmful effects are known, it is recommended not to consume dead or dying fish exposed to a P. parvum bloom.

Phycodnaviridae is a family of large (100–560 kb) double-stranded DNA viruses that infect marine or freshwater eukaryotic algae. Viruses within this family have a similar morphology, with an icosahedral capsid. As of 2014, there were 33 species in this family, divided among 6 genera. This family belongs to a super-group of large viruses known as nucleocytoplasmic large DNA viruses. Evidence was published in 2014 suggesting that specific strains of Phycodnaviridae might infect humans rather than just algal species, as was previously believed. Most genera under this family enter the host cell by cell receptor endocytosis and replicate in the nucleus. Phycodnaviridae play important ecological roles by regulating the growth and productivity of their algal hosts. Algal species such Heterosigma akashiwo and the genus Chrysochromulina can form dense blooms which can be damaging to fisheries, resulting in losses in the aquaculture industry. Heterosigma akashiwo virus (HaV) has been suggested for use as a microbial agent to prevent the recurrence of toxic red tides produced by this algal species. Phycodnaviridae cause death and lysis of freshwater and marine algal species, liberating organic carbon, nitrogen and phosphorus into the water, providing nutrients for the microbial loop.

<i>Heterosigma akashiwo</i> Species of alga

Heterosigma akashiwo is a species of microscopic algae of the class Raphidophyceae. It is a swimming marine alga that episodically forms toxic surface aggregations known as harmful algal bloom. The species name akashiwo is from the Japanese for "red tide".

<span class="mw-page-title-main">Harmful algal bloom</span> Population explosion of organisms that can kill marine life

A harmful algal bloom (HAB), or excessive algae growth, is an algal bloom that causes negative impacts to other organisms by production of natural algae-produced toxins, mechanical damage to other organisms, or by other means. HABs are sometimes defined as only those algal blooms that produce toxins, and sometimes as any algal bloom that can result in severely lower oxygen levels in natural waters, killing organisms in marine or fresh waters. Blooms can last from a few days to many months. After the bloom dies, the microbes that decompose the dead algae use up more of the oxygen, generating a "dead zone" which can cause fish die-offs. When these zones cover a large area for an extended period of time, neither fish nor plants are able to survive. Harmful algal blooms in marine environments are often called "red tides".

<i>Karenia</i> (dinoflagellate) Genus of single-celled organisms

Karenia is a genus that consists of unicellular, photosynthetic, planktonic organisms found in marine environments. The genus currently consists of 12 described species. They are best known for their dense toxic algal blooms and red tides that cause considerable ecological and economical damage; some Karenia species cause severe animal mortality. One species, Karenia brevis, is known to cause respiratory distress and neurotoxic shellfish poisoning (NSP) in humans.

<i>Pseudo-nitzschia</i> Genus of marine planktonic diatoms

Pseudo-nitzschia is a marine planktonic diatom genus that accounts for 4.4% of pennate diatoms found worldwide. Some species are capable of producing the neurotoxin domoic acid (DA), which is responsible for the neurological disorder in humans known as amnesic shellfish poisoning (ASP). Currently, 58 species are known, 28 of which have been shown to produce DA. It was originally hypothesized that only dinoflagellates could produce harmful algal toxins, but a deadly bloom of Pseudo-nitzschia occurred in 1987 in the bays of Prince Edward Island, Canada, and led to an outbreak of ASP. Over 100 people were affected by this outbreak after consuming contaminated mussels; three people died. Since this event, no additional deaths have been attributed to ASP, though the prevalence of toxic diatoms and DA has increased worldwide. This anomaly is likely due to increased awareness of harmful algal blooms (HABs) and their implications for human and ecosystem health.

<i>Prymnesium</i> Genus of single-celled organisms

Prymnesium is a genus of haptophytes, including the species Prymnesium parvum. The genus is a unicellular motile alga. It is ellipsoidal in shape one flagellum is straight and there are two longer ones which enable movement.

Phycotoxins are complex allelopathic chemicals produced by eukaryotic and prokaryotic algal secondary metabolic pathways. More simply, these are toxic chemicals synthesized by photosynthetic organisms. These metabolites are not harmful to the producer but may be toxic to either one or many members of the marine food web. This page focuses on phycotoxins produced by marine microalgae; however, freshwater algae and macroalgae are known phycotoxin producers and may exhibit analogous ecological dynamics. In the pelagic marine food web, phytoplankton are subjected to grazing by macro- and micro-zooplankton as well as competition for nutrients with other phytoplankton species. Marine bacteria try to obtain a share of organic carbon by maintaining symbiotic, parasitic, commensal, or predatory interactions with phytoplankton. Other bacteria will degrade dead phytoplankton or consume organic carbon released by viral lysis. The production of toxins is one strategy that phytoplankton use to deal with this broad range of predators, competitors, and parasites. Smetacek suggested that "planktonic evolution is ruled by protection and not competition. The many shapes of plankton reflect defense responses to specific attack systems". Indeed, phytoplankton retain an abundance of mechanical and chemical defense mechanisms including cell walls, spines, chain/colony formation, and toxic chemical production. These morphological and physiological features have been cited as evidence for strong predatory pressure in the marine environment. However, the importance of competition is also demonstrated by the production of phycotoxins that negatively impact other phytoplankton species. Flagellates are the principle producers of phycotoxins; however, there are known toxigenic diatoms, cyanobacteria, prymnesiophytes, and raphidophytes. Because many of these allelochemicals are large and energetically expensive to produce, they are synthesized in small quantities. However, phycotoxins are known to accumulate in other organisms and can reach high concentrations during algal blooms. Additionally, as biologically active metabolites, phycotoxins may produce ecological effects at low concentrations. These effects may be subtle, but have the potential to impact the biogeographic distributions of phytoplankton and bloom dynamics.

<i>Pyrodinium</i> Species of protist

Pyrodinium is a genus of dinoflagellates. It was first discovered in 1906 in the waters around New Providence Island in the Bahamas. Pyrodinium is a monospecific species with two varieties, Pyrodinium bahamense var. compressum and Pyrodinium bahamanse var. bahamense. Pyrodinium is well known for producing Paralytic Shellfish Toxins (PSTs), e.g. saxitoxin, and the bioluminescence that lights up the bioluminescent bays in the Bahamas, Jamaica and Puerto Rico.

Alexandrium catenella is a species of dinoflagellates. It is among the group of Alexandrium species that produce toxins that cause paralytic shellfish poisoning, and is a cause of red tide. Alexandrium catenella is observed in cold, coastal waters, generally at temperate latitudes. These organisms have been found in the west coast of North America, Japan, Australia, and parts of South Africa.

<span class="mw-page-title-main">Mixotrophic dinoflagellate</span> Plankton

Dinoflagellates are eukaryotic plankton, existing in marine and freshwater environments. Previously, dinoflagellates had been grouped into two categories, phagotrophs and phototrophs. Mixotrophs, however include a combination of phagotrophy and phototrophy. Mixotrophic dinoflagellates are a sub-type of planktonic dinoflagellates and are part of the phylum Dinoflagellata. They are flagellated eukaryotes that combine photoautotrophy when light is available, and heterotrophy via phagocytosis. Dinoflagellates are one of the most diverse and numerous species of phytoplankton, second to diatoms.

Aureoumbra lagunensis is a unicellular planktonic marine microalga that belongs in the genus Aureoumbra under the class Pelagophyceae. It is similar in morphology and pigments to Aureococcus anophagefferens and Pelagococcus subviridis. The cell shape is spherical to subspherical and is 2.5 to 5.0 μm in diameter. It is golden-coloured and is encapsulated with extracellular polysaccharide layers and has a single chloroplast structure with pigments.

<span class="mw-page-title-main">Chrysochromulina ericina virus</span> Giant virus

Chrysochromulina ericina virus 01B, or simply Chrysochromulina ericina virus (CeV) is a giant virus in the family Mimiviridae infecting Haptolina ericina, a marine microalgae member of the Haptophyta. CeV is a dsDNA virus.

<span class="mw-page-title-main">Marine viruses</span> Viruses found in marine environments

Marine viruses are defined by their habitat as viruses that are found in marine environments, that is, in the saltwater of seas or oceans or the brackish water of coastal estuaries. Viruses are small infectious agents that can only replicate inside the living cells of a host organism, because they need the replication machinery of the host to do so. They can infect all types of life forms, from animals and plants to microorganisms, including bacteria and archaea.

Algal viruses are the viruses infecting algae, which are photosynthetic single-celled eukaryotes. As of 2020, there were 61 viruses known to infect algae. Algae are integral components of aquatic food webs and drive nutrient cycling, so the viruses infecting algal populations also impacts the organisms and nutrient cycling systems that depend on them. Thus, these viruses can have significant, worldwide economic and ecological effects. Their genomes varied between 4.4 to 560 kilobase pairs (kbp) long and used double-stranded Deoxyribonucleic Acid (dsDNA), double-stranded Ribonucleic Acid (dsRNA), single-stranded Deoxyribonucleic Acid (ssDNA), and single-stranded Ribonucleic Acid (ssRNA). The viruses ranged between 20 and 210 nm in diameter. Since the discovery of the first algae-infecting virus in 1979, several different techniques have been used to find new viruses infecting algae and it seems that there are many algae-infecting viruses left to be discovered

References

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