Jump to content

Coccolithophore

From Wikipedia, the free encyclopedia
The printable version is no longer supported and may have rendering errors. Please update your browser bookmarks and please use the default browser print function instead.

Coccolithophore
Paraphyletic grouping of algae
Temporal range: Rhaetian–Recent
Coccolithus pelagicus
Coccolithus pelagicus
Scientific classificationEdit this classification
Domain: Eukaryota
Clade: Diaphoretickes
Phylum: Haptista
Subphylum: Haptophytina
Class: Prymnesiophyceae
Groups included
Coccolithophore cells are covered with protective calcified (chalk) scales called coccoliths

Coccolithophores, or coccolithophorids, are single-celled organisms which are part of the phytoplankton, the autotrophic (self-feeding) component of the plankton community. They form a group of about 200 species, and belong either to the kingdom Protista, according to Robert Whittaker's five-kingdom system, or clade Hacrobia, according to a newer biological classification system. Within the Hacrobia, the coccolithophores are in the phylum or division Haptophyta, class Prymnesiophyceae (or Coccolithophyceae). Coccolithophores are almost exclusively marine, are photosynthetic and mixotrophic, and exist in large numbers throughout the sunlight zone of the ocean.

Coccolithophores are the most productive calcifying organisms on the planet, covering themselves with a calcium carbonate shell called a coccosphere. However, the reasons they calcify remain elusive. One key function may be that the coccosphere offers protection against microzooplankton predation, which is one of the main causes of phytoplankton death in the ocean.[1]

Coccolithophores are ecologically important, and biogeochemically they play significant roles in the marine biological pump and the carbon cycle.[2][1] Depending on habitat, they can produce up to 40 percent of the local marine primary production.[3] They are of particular interest to those studying global climate change because, as ocean acidity increases, their coccoliths may become even more important as a carbon sink.[4] Management strategies are being employed to prevent eutrophication-related coccolithophore blooms, as these blooms lead to a decrease in nutrient flow to lower levels of the ocean.[5]

The most abundant species of coccolithophore, Emiliania huxleyi, belongs to the order Isochrysidales and family Noëlaerhabdaceae.[6] It is found in temperate, subtropical, and tropical oceans.[7] This makes E. huxleyi an important part of the planktonic base of a large proportion of marine food webs. It is also the fastest growing coccolithophore in laboratory cultures.[8] It is studied for the extensive blooms it forms in nutrient depleted waters after the reformation of the summer thermocline.[9][10] and for its production of molecules known as alkenones that are commonly used by earth scientists as a means to estimate past sea surface temperatures.[11]

Overview

Coccolithophores (or coccolithophorids, from the adjective[12]) form a group of about 200 phytoplankton species.[13] They belong either to the kingdom Protista, according to Robert Whittaker's Five kingdom classification, or clade Hacrobia, according to the newer biological classification system. Within the Hacrobia, the coccolithophores are in the phylum or division Haptophyta, class Prymnesiophyceae (or Coccolithophyceae).[6] Coccolithophores are distinguished by special calcium carbonate plates (or scales) of uncertain function called coccoliths, which are also important microfossils. However, there are Prymnesiophyceae species lacking coccoliths (e.g. in genus Prymnesium), so not every member of Prymnesiophyceae is a coccolithophore.[14]

Coccolithophores are single-celled phytoplankton that produce small calcium carbonate (CaCO3) scales (coccoliths) which cover the cell surface in the form of a spherical coating, called a coccosphere. Many species are also mixotrophs, and are able to photosynthesise as well as ingest prey.[15]

Coccolithophores have been an integral part of marine plankton communities since the Jurassic.[16][17] Today, coccolithophores contribute ~1–10% to inorganic carbon fixation (calcification) to total carbon fixation (calcification plus photosynthesis) in the surface ocean[18] and ~50% to pelagic CaCO3 sediments.[19] Their calcareous shell increases the sinking velocity of photosynthetically fixed CO2 into the deep ocean by ballasting organic matter.[20][21] At the same time, the biogenic precipitation of calcium carbonate during coccolith formation reduces the total alkalinity of seawater and releases CO2.[22][23] Thus, coccolithophores play an important role in the marine carbon cycle by influencing the efficiency of the biological carbon pump and the oceanic uptake of atmospheric CO2.[1]

As of 2021, it is not known why coccolithophores calcify and how their ability to produce coccoliths is associated with their ecological success.[24][25][26][27][28] The most plausible benefit of having a coccosphere seems to be a protection against predators or viruses.[29][27] Viral infection is an important cause of phytoplankton death in the oceans,[30] and it has recently been shown that calcification can influence the interaction between a coccolithophore and its virus.[31][32] The major predators of marine phytoplankton are microzooplankton like ciliates and dinoflagellates. These are estimated to consume about two-thirds of the primary production in the ocean[33] and microzooplankton can exert a strong grazing pressure on coccolithophore populations.[34] Although calcification does not prevent predation, it has been argued that the coccosphere reduces the grazing efficiency by making it more difficult for the predator to utilise the organic content of coccolithophores.[35] Heterotrophic protists are able to selectively choose prey on the basis of its size or shape and through chemical signals[36][37] and may thus favor other prey that is available and not protected by coccoliths.[1]

Structure

Coccolithophore cell surrounded by its shield of coccoliths. The coccolith-bearing cell is called the coccosphere.[38][39]

Coccolithophores are spherical cells about 5–100 micrometres across, enclosed by calcareous plates called coccoliths, which are about 2–25 micrometres across. Each cell contains two brown chloroplasts which surround the nucleus.[40]

Enclosed in each coccosphere is a single cell with membrane bound organelles. Two large chloroplasts with brown pigment are located on either side of the cell and surround the nucleus, mitochondria, golgi apparatus, endoplasmic reticulum, and other organelles. Each cell also has two flagellar structures, which are involved not only in motility, but also in mitosis and formation of the cytoskeleton.[41] In some species, a functional or vestigial haptonema is also present.[42] This structure, which is unique to haptophytes, coils and uncoils in response to environmental stimuli. Although poorly understood, it has been proposed to be involved in prey capture.[41]

Ecology

Life history strategy

Life cycle strategies of phytoplankton
(a) dinoflagellates tend to utilize a haplontic (asexual) life cycle, (b) diatoms tend to utilize a diplontic (sexual) life cycle, and (c) coccolithophores tend to utilize a haplo-diplontic life cycle. Note that not all coccolithophores calcify in their haploid phase.[3]

The complex life cycle of coccolithophores is known as a haplodiplontic life cycle, and is characterized by an alternation of both asexual and sexual phases. The asexual phase is known as the haploid phase, while the sexual phase is known as the diploid phase. During the haploid phase, coccolithophores produce haploid cells through mitosis. These haploid cells can then divide further through mitosis or undergo sexual reproduction with other haploid cells. The resulting diploid cell goes through meiosis to produce haploid cells again, starting the cycle over. With coccolithophores, asexual reproduction by mitosis is possible in both phases of the life cycle, which is a contrast with most other organisms that have alternating life cycles.[43] Both abiotic and biotic factors may affect the frequency with which each phase occurs.[44]

Coccolithophores reproduce asexually through binary fission. In this process the coccoliths from the parent cell are divided between the two daughter cells. There have been suggestions stating the possible presence of a sexual reproduction process due to the diploid stages of the coccolithophores, but this process has never been observed.[45]

K or r- selected strategies of coccolithophores depend on their life cycle stage. When coccolithophores are diploid, they are r-selected. In this phase they tolerate a wider range of nutrient compositions. When they are haploid they are K- selected and are often more competitive in stable low nutrient environments.[45] Most coccolithophores are K strategist and are usually found on nutrient-poor surface waters. They are poor competitors when compared to other phytoplankton and thrive in habitats where other phytoplankton would not survive.[46] These two stages in the life cycle of coccolithophores occur seasonally, where more nutrition is available in warmer seasons and less is available in cooler seasons. This type of life cycle is known as a complex heteromorphic life cycle.[45]

Global distribution

Global distribution of coccolithophores in the ocean

Coccolithophores occur throughout the world's oceans. Their distribution varies vertically by stratified layers in the ocean and geographically by different temporal zones.[47] While most modern coccolithophores can be located in their associated stratified oligotrophic conditions, the most abundant areas of coccolithophores where there is the highest species diversity are located in subtropical zones with a temperate climate.[48] While water temperature and the amount of light intensity entering the water's surface are the more influential factors in determining where species are located, the ocean currents also can determine the location where certain species of coccolithophores are found.[49]

Although motility and colony formation vary according to the life cycle of different coccolithophore species, there is often alternation between a motile, haploid phase, and a non-motile diploid phase. In both phases, the organism's dispersal is largely due to ocean currents and circulation patterns.[50]

Within the Pacific Ocean, approximately 90 species have been identified with six separate zones relating to different Pacific currents that contain unique groupings of different species of coccolithophores.[51] The highest diversity of coccolithophores in the Pacific Ocean was in an area of the ocean considered the Central North Zone which is an area between 30 oN and 5 oN, composed of the North Equatorial Current and the Equatorial Countercurrent. These two currents move in opposite directions, east and west, allowing for a strong mixing of waters and allowing a large variety of species to populate the area.[51]

In the Atlantic Ocean, the most abundant species are E. huxleyi and Florisphaera profunda with smaller concentrations of the species Umbellosphaera irregularis, Umbellosphaera tenuis and different species of Gephyrocapsa.[51] Deep-dwelling coccolithophore species abundance is greatly affected by nutricline and thermocline depths. These coccolithophores increase in abundance when the nutricline and thermocline are deep and decrease when they are shallow.[52]

Size comparison between the relatively large coccolithophore Scyphosphaera apsteinii and the relatively small but ubiquitous coccolithophore Emiliania huxleyi[53]

The complete distribution of coccolithophores is currently not known and some regions, such as the Indian Ocean, are not as well studied as other locations in the Pacific and Atlantic Oceans. It is also very hard to explain distributions due to multiple constantly changing factors involving the ocean's properties, such as coastal and equatorial upwelling, frontal systems, benthic environments, unique oceanic topography, and pockets of isolated high or low water temperatures.[54]

The upper photic zone is low in nutrient concentration, high in light intensity and penetration, and usually higher in temperature. The lower photic zone is high in nutrient concentration, low in light intensity and penetration and relatively cool. The middle photic zone is an area that contains the same values in between that of the lower and upper photic zones.[48]

Calcidiscus leptoporus
Coccolithus braarudii
Scyphosphaera apsteinii
Larger coccolithophores such as the species above are less numerous than the smaller but ubiquitous Emiliania huxleyi, but they are heavily calcified and make important contributions to global calcification.[55][56] Unmarked scale bars 5 μm.

Great Calcite Belt

Yearly cycle of the Great Calcite Belt in the Southern Ocean
Main article: Great Calcite Belt

The Great Calcite Belt of the Southern Ocean is a region of elevated summertime upper ocean calcite concentration derived from coccolithophores, despite the region being known for its diatom predominance. The overlap of two major phytoplankton groups, coccolithophores and diatoms, in the dynamic frontal systems characteristic of this region provides an ideal setting to study environmental influences on the distribution of different species within these taxonomic groups.[57]

The Great Calcite Belt, defined as an elevated particulate inorganic carbon (PIC) feature occurring alongside seasonally elevated chlorophyll a in austral spring and summer in the Southern Ocean,[58] plays an important role in climate fluctuations,[59][60] accounting for over 60% of the Southern Ocean area (30–60° S).[61] The region between 30° and 50° S has the highest uptake of anthropogenic carbon dioxide (CO2) alongside the North Atlantic and North Pacific oceans.[62]

Effect of global climate change on distribution

Recent studies show that climate change has direct and indirect impacts on Coccolithophore distribution and productivity. They will inevitably be affected by the increasing temperatures and thermal stratification of the top layer of the ocean, since these are prime controls on their ecology, although it is not clear whether global warming would result in net increase or decrease of coccolithophores. As they are calcifying organisms, it has been suggested that ocean acidification due to increasing carbon dioxide could severely affect coccolithophores.[52] Recent CO2 increases have seen a sharp increase in the population of coccolithophores.[63]

Role in the food web

Satellite photograph: The milky blue colour of this phytoplankton bloom in Barents Sea strongly suggests it contains coccolithophores
A coccolithovirus, Emiliania huxleyi virus 86 (arrowed), infecting an Emiliania huxleyi coccolithophore.[64][65] This giant marine virus has one of the largest known virus genomes.[66]

Coccolithophores are one of the more abundant primary producers in the ocean. As such, they are a large contributor to the primary productivity of the tropical and subtropical oceans, however, exactly how much has yet to have been recorded.[67]

Dependence on nutrients

The ratio between the concentrations of nitrogen, phosphorus and silicate in particular areas of the ocean dictates competitive dominance within phytoplankton communities. Each ratio essentially tips the odds in favor of either diatoms or other groups of phytoplankton, such as coccolithophores. A low silicate to nitrogen and phosphorus ratio allows coccolithophores to outcompete other phytoplankton species; however, when silicate to phosphorus to nitrogen ratios are high coccolithophores are outcompeted by diatoms. The increase in agricultural processes lead to eutrophication of waters and thus, coccolithophore blooms in these high nitrogen and phosphorus, low silicate environments.[5]

Impact on water column productivity

The calcite in calcium carbonate allows coccoliths to scatter more light than they absorb. This has two important consequences: 1) Surface waters become brighter, meaning they have a higher albedo, and 2) there is induced photoinhibition, meaning photosythetic production is diminished due to an excess of light. In case 1), a high concentration of coccoliths leads to a simultaneous increase in surface water temperature and decrease in the temperature of deeper waters. This results in more stratification in the water column and a decrease in the vertical mixing of nutrients. However, a 2012 study estimated that the overall effect of coccolithophores on the increase in radiative forcing of the ocean is less than that from anthropogenic factors.[68] Therefore, the overall result of large blooms of coccolithophores is a decrease in water column productivity, rather than a contribution to global warming.

Predator-prey interactions

Their predators include the common predators of all phytoplankton including small fish, zooplankton, and shellfish larvae.[46][69] Viruses specific to this species have been isolated from several locations worldwide and appear to play a major role in spring bloom dynamics.

Toxicity

No environmental evidence of coccolithophore toxicity has been reported, but they belong to the class Prymnesiophyceae which contain orders with toxic species. Toxic species have been found in the genera Prymnesium Massart and Chrysochromulina Lackey. Members of the genus Prymnesium have been found to produce haemolytic compounds, the agent responsible for toxicity. Some of these toxic species are responsible for large fish kills and can be accumulated in organisms such as shellfish; transferring it through the food chain. In laboratory tests for toxicity members of the oceanic coccolithophore genera Emiliania, Gephyrocapsa, Calcidiscus and Coccolithus were shown to be non-toxic as were species of the coastal genus Hymenomonas, however several species of Pleurochrysis and Jomonlithus, both coastal genera were toxic to Artemia.[69]

Community interactions

Coccolithophorids are predominantly found as single, free-floating haploid or diploid cells.[47]

Competition

Most phytoplankton need sunlight and nutrients from the ocean to survive, so they thrive in areas with large inputs of nutrient rich water upwelling from the lower levels of the ocean. Most coccolithophores require sunlight only for energy production, and have a higher ratio of nitrate uptake over ammonium uptake (nitrogen is required for growth and can be used directly from nitrate but not ammonium). Because of this they thrive in still, nutrient-poor environments where other phytoplankton are starving.[70] Trade-offs associated with these faster growth rates include a smaller cell radius and lower cell volume than other types of phytoplankton.

Viral infection and coevolution

Giant DNA-containing viruses are known to lytically infect coccolithophores, particularly E. huxleyi. These viruses, known as E. huxleyi viruses (EhVs), appear to infect the coccosphere coated diploid phase of the life cycle almost exclusively. It has been proposed that as the haploid organism is not infected and therefore not affected by the virus, the co-evolutionary "arms race" between coccolithophores and these viruses does not follow the classic Red Queen evolutionary framework, but instead a "Cheshire Cat" ecological dynamic.[71] More recent work has suggested that viral synthesis of sphingolipids and induction of programmed cell death provides a more direct link to study a Red Queen-like coevolutionary arms race at least between the coccolithoviruses and diploid organism.[44]

Evolution and diversity

Coccolithophores are members of the clade Haptophyta, which is a sister clade to Centrohelida, which are both in Haptista.[72] The oldest known coccolithophores are known from the Late Triassic, around the Norian-Rhaetian boundary.[73] Diversity steadily increased over the course of the Mesozoic, reaching its apex during the Late Cretaceous. However, there was a sharp drop during the Cretaceous-Paleogene extinction event, when more than 90% of coccolithophore species became extinct. Coccoliths reached another, lower apex of diversity during the Paleocene-Eocene thermal maximum, but have subsequently declined since the Oligocene due to decreasing global temperatures, with species that produced large and heavily calcified coccoliths most heavily affected.[27]

Evolutionary history of coccolithophores:[27] (A) Coccolithophore species richness over time; (B) The fossil record of major coccolithophore biomineralization innovations and morphogroups.
Coccolithophore diversity. Emiliania huxleyi (E), the reference species for coccolithophore studies, is contrasted with a range of other species spanning the biodiversity of modern coccolithophores. All images are scanning electron micrographs of cells collected by seawater filtration from the open ocean. Species illustrated: (A) Coccolithus pelagicus, (B) Calcidiscus leptoporus, (C) Braarudosphaera bigelowii, (D) Gephyrocapsa oceanica, (E) Emiliania huxleyi, (F) Discosphaera tubifera, (G) Rhabdosphaera clavigera, (H) Calciosolenia murrayi, (I) Umbellosphaera irregularis, (J) Gladiolithus flabellatus, (K and L) Florisphaera profunda, (M) Syracosphaera pulchra, and (N) Helicosphaera carteri. Scale bar is 5 μm.

Coccolithophore shells

Part of a series related to
Biomineralization
General
Exoskeletons (shells)
Endoskeletons (bones)
Teeth, scales, tusks etc
Calcification
Silicification
Other forms
Related
See also: Protist shell and coccolith
  • Exoskeleton: coccospheres and coccoliths

Each coccolithophore encloses itself in a protective shell of coccoliths, calcified scales which make up its exoskeleton or coccosphere.[74] The coccoliths are created inside the coccolithophore cell and while some species maintain a single layer throughout life only producing new coccoliths as the cell grows, others continually produce and shed coccoliths.

Composition

The primary constituent of coccoliths is calcium carbonate, or chalk. Calcium carbonate is transparent, so the organisms' photosynthetic activity is not compromised by encapsulation in a coccosphere.[46]

Formation

Coccoliths are produced by a biomineralization process known as coccolithogenesis.[40] Generally, calcification of coccoliths occurs in the presence of light, and these scales are produced much more during the exponential phase of growth than the stationary phase.[75] Although not yet entirely understood, the biomineralization process is tightly regulated by calcium signaling. Calcite formation begins in the golgi complex where protein templates nucleate the formation of CaCO3 crystals and complex acidic polysaccharides control the shape and growth of these crystals.[50] As each scale is produced, it is exported in a Golgi-derived vesicle and added to the inner surface of the coccosphere. This means that the most recently produced coccoliths may lie beneath older coccoliths.[43] Depending upon the phytoplankton's stage in the life cycle, two different types of coccoliths may be formed. Holococcoliths are produced only in the haploid phase, lack radial symmetry, and are composed of anywhere from hundreds to thousands of similar minute (ca 0.1 μm) rhombic calcite crystals. These crystals are thought to form at least partially outside the cell. Heterococcoliths occur only in the diploid phase, have radial symmetry, and are composed of relatively few complex crystal units (fewer than 100). Although they are rare, combination coccospheres, which contain both holococcoliths and heterococcoliths, have been observed in the plankton recording coccolithophore life cycle transitions. Finally, the coccospheres of some species are highly modified with various appendages made of specialized coccoliths.[54]

Function

While the exact function of the coccosphere is unclear, many potential functions have been proposed. Most obviously coccoliths may protect the phytoplankton from predators. It also appears that it helps them to create a more stable pH. During photosynthesis carbon dioxide is removed from the water, making it more basic. Also calcification removes carbon dioxide, but chemistry behind it leads to the opposite pH reaction; it makes the water more acidic. The combination of photosynthesis and calcification therefore even out each other regarding pH changes.[76] In addition, these exoskeletons may confer an advantage in energy production, as coccolithogenesis seems highly coupled with photosynthesis. Organic precipitation of calcium carbonate from bicarbonate solution produces free carbon dioxide directly within the cellular body of the alga, this additional source of gas is then available to the Coccolithophore for photosynthesis. It has been suggested that they may provide a cell-wall like barrier to isolate intracellular chemistry from the marine environment.[77] More specific, defensive properties of coccoliths may include protection from osmotic changes, chemical or mechanical shock, and short-wavelength light.[42] It has also been proposed that the added weight of multiple layers of coccoliths allows the organism to sink to lower, more nutrient rich layers of the water and conversely, that coccoliths add buoyancy, stopping the cell from sinking to dangerous depths.[78] Coccolith appendages have also been proposed to serve several functions, such as inhibiting grazing by zooplankton.[54]

Uses

Coccoliths are the main component of the Chalk, a Late Cretaceous rock formation which outcrops widely in southern England and forms the White Cliffs of Dover, and of other similar rocks in many other parts of the world.[10] At the present day sedimented coccoliths are a major component of the calcareous oozes that cover up to 35% of the ocean floor and is kilometres thick in places.[50] Because of their abundance and wide geographic ranges, the coccoliths which make up the layers of this ooze and the chalky sediment formed as it is compacted serve as valuable microfossils.

Energetic costs of coccolithophore calcification.[27] Energetic costs reported as a percentage of total photosynthetic budget.

Calcification, the biological production of calcium carbonate (CaCO3), is a key process in the marine carbon cycle. Coccolithophores are the major planktonic group responsible for pelagic CaCO3 production.[79][80] The diagram on the right shows the energetic costs of coccolithophore calcification:

(A) Transport processes include the transport into the cell from the surrounding seawater of primary calcification substrates Ca2+ and HCO3− (black arrows) and the removal of the end product H+ from the cell (gray arrow). The transport of Ca2+ through the cytoplasm to the CV is the dominant cost associated with calcification.[27]
(B) Metabolic processes include the synthesis of CAPs (gray rectangles) by the Golgi complex (white rectangles) that regulate the nucleation and geometry of CaCO3 crystals. The completed coccolith (gray plate) is a complex structure of intricately arranged CAPs and CaCO3 crystals.[27]
(C) Mechanical and structural processes account for the secretion of the completed coccoliths that are transported from their original position adjacent to the nucleus to the cell periphery, where they are transferred to the surface of the cell. The costs associated with these processes are likely to be comparable to organic-scale exocytosis in noncalcifying haptophyte algae.[27]
Benefits of coccolithophore calcification[27]

The diagram on the left shows the benefits of coccolithophore calcification. (A) Accelerated photosynthesis includes CCM (1) and enhanced light uptake via scattering of scarce photons for deep-dwelling species (2). (B) Protection from photodamage includes sunshade protection from ultraviolet (UV) light and photosynthetic active radiation (PAR) (1) and energy dissipation under high-light conditions (2). (C) Armor protection includes protection against viral/bacterial infections (1) and grazing by selective (2) and nonselective (3) grazers.[27]

The degree by which calcification can adapt to ocean acidification is presently unknown. Cell physiological examinations found the essential H+ efflux (stemming from the use of HCO3− for intra-cellular calcification) to become more costly with ongoing ocean acidification as the electrochemical H+ inside-out gradient is reduced and passive proton outflow impeded.[81] Adapted cells would have to activate proton channels more frequently, adjust their membrane potential, and/or lower their internal pH.[82] Reduced intra-cellular pH would severely affect the entire cellular machinery and require other processes (e.g. photosynthesis) to co-adapt in order to keep H+ efflux alive.[83][84] The obligatory H+ efflux associated with calcification may therefore pose a fundamental constraint on adaptation which may potentially explain why "calcification crisis" were possible during long-lasting (thousands of years) CO2 perturbation events[85][86] even though evolutionary adaption to changing carbonate chemistry conditions is possible within one year.[85][86] Unraveling these fundamental constraints and the limits of adaptation should be a focus in future coccolithophore studies because knowing them is the key information required to understand to what extent the calcification response to carbonate chemistry perturbations can be compensated by evolution.[87]

Silicate- or cellulose-armored functional groups such as diatoms and dinoflagellates do not need to sustain the calcification-related H+ efflux. Thus, they probably do not need to adapt in order to keep costs for the production of structural elements low. On the contrary, dinoflagellates (except for calcifying species;[88] with generally inefficient CO2-fixing RuBisCO enzymes[89] may even profit from chemical changes since photosynthetic carbon fixation as their source of structural elements in the form of cellulose should be facilitated by the ocean acidification-associated CO2 fertilization.[90][91] Under the assumption that any form of shell/exoskeleton protects phytoplankton against predation[29] non-calcareous armors may be the preferable solution to realize protection in a future ocean.[87]

Representation of comparative energetic effort for armor construction in three major shell-forming phytoplankton taxa as a function of carbonate chemistry conditions[87]

The diagram on the right is a representation of how the comparative energetic effort for armor construction in diatoms, dinoflagellates and coccolithophores appear to operate. The frustule (diatom shell) seems to be the most inexpensive armor under all circumstances because diatoms typically outcompete all other groups when silicate is available. The coccosphere is relatively inexpensive under sufficient [CO2], high [HCO3−], and low [H+] because the substrate is saturating and protons are easily released into seawater.[81] In contrast, the construction of thecal elements, which are organic (cellulose) plates that constitute the dinoflagellate shell, should rather be favored at high H+ concentrations because these usually coincide with high [CO2]. Under these conditions dinoflagellates could down-regulate the energy-consuming operation of carbon concentrating mechanisms to fuel the production of organic source material for their shell. Therefore, a shift in carbonate chemistry conditions toward high [CO2] may promote their competitiveness relative to coccolithophores. However, such a hypothetical gain in competitiveness due to altered carbonate chemistry conditions would not automatically lead to dinoflagellate dominance because a huge number of factors other than carbonate chemistry have an influence on species composition as well.[87][92]

Defence against predation

Currently, the evidence supporting or refuting a protective function of the coccosphere against predation is limited. Some researchers found that overall microzooplankton predation rates were reduced during blooms of the coccolithophore Emiliania huxleyi,[93][94] while others found high microzooplankton grazing rates on natural coccolithophore communities.[95] In 2020, researchers found that in situ ingestion rates of microzooplankton on E. huxleyi did not differ significantly from those on similar sized non-calcifying phytoplankton.[96] In laboratory experiments the heterotrophic dinoflagellate Oxyrrhis marina preferred calcified over non-calcified cells of E. huxleyi, which was hypothesised to be due to size selective feeding behaviour, since calcified cells are larger than non-calcified E. huxleyi.[97] In 2015, Harvey et al. investigated predation by the dinoflagellate O. marina on different genotypes of non-calcifying E. huxleyi as well as calcified strains that differed in the degree of calcification.[98] They found that the ingestion rate of O. marina was dependent on the genotype of E. huxleyi that was offered, rather than on their degree of calcification. In the same study, however, the authors found that predators which preyed on non-calcifying genotypes grew faster than those fed with calcified cells.[98] In 2018, Strom et al. compared predation rates of the dinoflagellate Amphidinium longum on calcified relative to naked E. huxleyi prey and found no evidence that the coccosphere prevents ingestion by the grazer.[99] Instead, ingestion rates were dependent on the offered genotype of E. huxleyi.[99] Altogether, these two studies suggest that the genotype has a strong influence on ingestion by the microzooplankton species, but if and how calcification protects coccolithophores from microzooplankton predation could not be fully clarified.[1]

Importance in global climate change

Part of a series on
Plankton
Phytoplankton
Trophic mode
By size
By taxonomy
By habitat
Other types
Blooms
Related topics

Impact on the carbon cycle

Coccolithophores have both long and short term effects on the carbon cycle. The production of coccoliths requires the uptake of dissolved inorganic carbon and calcium. Calcium carbonate and carbon dioxide are produced from calcium and bicarbonate by the following chemical reaction:[100]

Ca2+ + 2HCO−3 ⇌ CaCO3 + CO2 + H2O

Because coccolithophores are photosynthetic organisms, they are able to use some of the CO2 released in the calcification reaction for photosynthesis.[101]

However, the production of calcium carbonate drives surface alkalinity down, and in conditions of low alkalinity the CO2 is instead released back into the atmosphere.[102] As a result of this, researchers have postulated that large blooms of coccolithophores may contribute to global warming in the short term.[103] A more widely accepted idea, however, is that over the long term coccolithophores contribute to an overall decrease in atmospheric CO2 concentrations. During calcification two carbon atoms are taken up and one of them becomes trapped as calcium carbonate. This calcium carbonate sinks to the bottom of the ocean in the form of coccoliths and becomes part of sediment; thus, coccolithophores provide a sink for emitted carbon, mediating the effects of greenhouse gas emissions.[103]

Evolutionary responses to ocean acidification

Research also suggests that ocean acidification due to increasing concentrations of CO2 in the atmosphere may affect the calcification machinery of coccolithophores. This may not only affect immediate events such as increases in population or coccolith production, but also may induce evolutionary adaptation of coccolithophore species over longer periods of time. For example, coccolithophores use H+ ion channels in to constantly pump H+ ions out of the cell during coccolith production. This allows them to avoid acidosis, as coccolith production would otherwise produce a toxic excess of H+ ions. When the function of these ion channels is disrupted, the coccolithophores stop the calcification process to avoid acidosis, thus forming a feedback loop.[104] Low ocean alkalinity, impairs ion channel function and therefore places evolutionary selective pressure on coccolithophores and makes them (and other ocean calcifiers) vulnerable to ocean acidification.[105] In 2008, field evidence indicating an increase in calcification of newly formed ocean sediments containing coccolithophores bolstered the first ever experimental data showing that an increase in ocean CO2 concentration results in an increase in calcification of these organisms. Decreasing coccolith mass is related to both the increasing concentrations of CO2 and decreasing concentrations of CO2−3 in the world's oceans. This lower calcification is assumed to put coccolithophores at ecological disadvantage. Some species like Calcidiscus leptoporus, however, are not affected in this way, while the most abundant coccolithophore species, E. huxleyi might be (study results are mixed).[104][106] Also, highly calcified coccolithophorids have been found in conditions of low CaCO3 saturation contrary to predictions.[4] Understanding the effects of increasing ocean acidification on coccolithophore species is absolutely essential to predicting the future chemical composition of the ocean, particularly its carbonate chemistry. Viable conservation and management measures will come from future research in this area. Groups like the European-based CALMARO[107] are monitoring the responses of coccolithophore populations to varying pH's and working to determine environmentally sound measures of control.

Impact on microfossil record

See also: Protists in the fossil record

Coccolith fossils are prominent and valuable calcareous microfossils. They are the largest global source of biogenic calcium carbonate, and significantly contribute to the global carbon cycle.[108] They are the main constituent of chalk deposits such as the white cliffs of Dover.

Of particular interest are fossils dating back to the Palaeocene-Eocene Thermal Maximum 55 million years ago. This period is thought to correspond most directly to the current levels of CO2 in the ocean.[109] Finally, field evidence of coccolithophore fossils in rock were used to show that the deep-sea fossil record bears a rock record bias similar to the one that is widely accepted to affect the land-based fossil record.[110]

Impact on the oceans

See also: CLAW hypothesis

The coccolithophorids help in regulating the temperature of the oceans. They thrive in warm seas and release dimethyl sulfide (DMS) into the air whose nuclei help to produce thicker clouds to block the sun.[111] When the oceans cool, the number of coccolithophorids decrease and the amount of clouds also decrease. When there are fewer clouds blocking the sun, the temperature also rises. This, therefore, maintains the balance and equilibrium of nature.[112][113]

See also

References

  1. ^ a b c d e Haunost, Mathias; Riebesell, Ulf; D'Amore, Francesco; Kelting, Ole; Bach, Lennart T. (30 June 2021). "Influence of the Calcium Carbonate Shell of Coccolithophores on Ingestion and Growth of a Dinoflagellate Predator". Frontiers in Marine Science. 8. Frontiers Media SA. doi:10.3389/fmars.2021.664269. ISSN 2296-7745. Material was copied from this source, which is available under a Creative Commons Attribution 4.0 International License.
  2. ^ Rost, Björn; Riebesell, Ulf (2004). "Coccolithophores and the biological pump: Responses to environmental changes". Coccolithophores. Berlin, Heidelberg: Springer Berlin Heidelberg. pp. 99–125. doi:10.1007/978-3-662-06278-4_5. ISBN 978-3-642-06016-8.
  3. ^ a b de Vries, Joost; Monteiro, Fanny; Wheeler, Glen; Poulton, Alex; Godrijan, Jelena; Cerino, Federica; Malinverno, Elisa; Langer, Gerald; Brownlee, Colin (2021-02-16). "Haplo-diplontic life cycle expands coccolithophore niche". Biogeosciences. 18 (3). Copernicus GmbH: 1161–1184. Bibcode:2021BGeo...18.1161D. doi:10.5194/bg-18-1161-2021. ISSN 1726-4189. S2CID 233976784. Material was copied from this source, which is available under a Creative Commons Attribution 4.0 International License.
  4. ^ a b Smith, H.E.K.; et al. (2012), "Predominance of heavily calcified coccolithophores at low CaCO3 saturation during winter in the Bay of Biscay", Proceedings of the National Academy of Sciences, 109 (23): 8845–8849, Bibcode:2012PNAS..109.8845S, doi:10.1073/pnas.1117508109, PMC 3384182, PMID 22615387
  5. ^ a b Yunev, O.A.; et al. (2007), "Nutrient and phytoplankton trends on the western Black Sea shelf in response to cultural eutrophication and climate changes", Estuarine, Coastal and Shelf Science, 74 (1–2): 63–67, Bibcode:2007ECSS...74...63Y, doi:10.1016/j.ecss.2007.03.030
  6. ^ a b Hay, W.W.; Mohler, H.P.; Roth, P.H.; Schmidt, R.R.; Boudreaux, J.E. (1967), "Calcareous nannoplankton zonation of the Cenozoic of the Gulf Coast and Caribbean-Antillean area, and transoceanic correlation", Transactions of the Gulf Coast Association of Geological Societies, 17: 428–480.
  7. ^ "Biogeography and dispersal of micro-organisms: a review emphasizing protists", Acta Protozoologica, 45 (2): 111–136, 2005
  8. ^ Buitenhuis, Erik T.; Pangerc, Tanja; Franklin, Daniel J.; Le Quéré, Corinne; Malin, Gill (2008), "Growth Rates of Six Coccolithoripd Strains as a Function of Temperature", Limnology and Oceanography, 53 (3): 1181–1185, Bibcode:2008LimOc..53.1181B, doi:10.4319/lo.2008.53.3.1181, S2CID 16601834
  9. ^ Egge, JK; Aksnes, DL (1992), "Silicate as regulating nutrient in phytoplankton competition", Marine Ecology Progress Series, 83 (2): 281–289, Bibcode:1992MEPS...83..281E, doi:10.3354/meps083281
  10. ^ a b "Life at the Edge of Sight — Scott Chimileski, Roberto Kolter | Harvard University Press". www.hup.harvard.edu. Retrieved 2018-01-26.
  11. ^ Bentaleb, I.; et al. (1999), "Silicate as regulating nutrient in phytoplankton competition", Marine Chemistry, 64 (4): 301–313, doi:10.1016/S0304-4203(98)00079-6.
  12. ^ "International Nanoplankton Association".
  13. ^ Young, J. R.; Geisen, M.; Probert, I. (2005). "A review of selected aspects of coccolithophore biology with implications for paleobiodiversity estimation" (PDF). Micropaleontology. 51 (4): 267–288. Bibcode:2005MiPal..51..267Y. doi:10.2113/gsmicropal.51.4.267.
  14. ^ Schaechter, Moselio (2012). Eukaryotic Microbes. Academic Press. p. 239. ISBN 978-0-12-383876-6. Retrieved 30 January 2015.
  15. ^ Avrahami, Yoav; Frada, Miguel J. (31 March 2020). Mock, T. (ed.). "Detection of Phagotrophy in the Marine Phytoplankton Group of the Coccolithophores (Calcihaptophycidae, Haptophyta) During Nutrient‐replete and Phosphate‐limited Growth". Journal of Phycology. 56 (4): 1103–1108. doi:10.1111/jpy.12997. ISSN 0022-3646.{{cite journal}}: CS1 maint: date and year (link)
  16. ^ Bown, Paul R.; Lees, Jackie A.; Young, Jeremy R. (2004). "Calcareous nannoplankton evolution and diversity through time". Coccolithophores. pp. 481–508. doi:10.1007/978-3-662-06278-4_18. ISBN 978-3-642-06016-8.
  17. ^ Hay, William W. (2004). "Carbonate fluxes and calcareous nannoplankton". Coccolithophores. pp. 509–528. doi:10.1007/978-3-662-06278-4_19. ISBN 978-3-642-06016-8.
  18. ^ Poulton, Alex J.; Adey, Tim R.; Balch, William M.; Holligan, Patrick M. (2007). "Relating coccolithophore calcification rates to phytoplankton community dynamics: Regional differences and implications for carbon export". Deep Sea Research Part II: Topical Studies in Oceanography. 54 (5–7): 538–557. Bibcode:2007DSRII..54..538P. doi:10.1016/j.dsr2.2006.12.003.
  19. ^ Broecker, Wallace; Clark, Elizabeth (2009). "Ratio of coccolith CaCO3to foraminifera CaCO3in late Holocene deep sea sediments". Paleoceanography. 24 (3). Bibcode:2009PalOc..24.3205B. doi:10.1029/2009PA001731.
  20. ^ Klaas, Christine; Archer, David E. (2002). "Association of sinking organic matter with various types of mineral ballast in the deep sea: Implications for the rain ratio". Global Biogeochemical Cycles. 16 (4): 1116. Bibcode:2002GBioC..16.1116K. doi:10.1029/2001GB001765. S2CID 34159028.
  21. ^ Honjo, Susumu; Manganini, Steven J.; Krishfield, Richard A.; Francois, Roger (2008). "Particulate organic carbon fluxes to the ocean interior and factors controlling the biological pump: A synthesis of global sediment trap programs since 1983". Progress in Oceanography. 76 (3): 217–285. Bibcode:2008PrOce..76..217H. doi:10.1016/j.pocean.2007.11.003.
  22. ^ Frankignoulle, Michel; Canon, Christine; Gattuso, Jean-Pierre (1994). "Marine calcification as a source of carbon dioxide: Positive feedback of increasing atmospheric CO2". Limnology and Oceanography. 39 (2): 458–462. Bibcode:1994LimOc..39..458F. doi:10.4319/lo.1994.39.2.0458. hdl:2268/246251.
  23. ^ Rost, Björn; Riebesell, Ulf (2004). "Coccolithophores and the biological pump: Responses to environmental changes". Coccolithophores. pp. 99–125. doi:10.1007/978-3-662-06278-4_5. ISBN 978-3-642-06016-8.
  24. ^ Young, J. R. (1987). Possible Functional Interpretations of Coccolith Morphology. New York: Springer-Verlag, 305–313.
  25. ^ Young, J. R. (1994). "Functions of coccoliths", in Coccolithophores, eds A. Winter and W. G. Siesser (Cambridge: Cambridge University Press), 63–82.
  26. ^ Raven, JA; Crawfurd, K. (2012). "Environmental controls on coccolithophore calcification". Marine Ecology Progress Series. 470: 137–166. Bibcode:2012MEPS..470..137R. doi:10.3354/meps09993. hdl:10453/114799.
  27. ^ a b c d e f g h i j Monteiro, Fanny M.; Bach, Lennart T.; Brownlee, Colin; Bown, Paul; Rickaby, Rosalind E. M.; Poulton, Alex J.; Tyrrell, Toby; Beaufort, Luc; Dutkiewicz, Stephanie; Gibbs, Samantha; Gutowska, Magdalena A.; Lee, Renee; Riebesell, Ulf; Young, Jeremy; Ridgwell, Andy (2016). "Why marine phytoplankton calcify". Science Advances. 2 (7): e1501822. Bibcode:2016SciA....2E1822M. doi:10.1126/sciadv.1501822. PMC 4956192. PMID 27453937.
  28. ^ Müller, Marius N. (2019). "On the Genesis and Function of Coccolithophore Calcification". Frontiers in Marine Science. 6. doi:10.3389/fmars.2019.00049.
  29. ^ a b Hamm, Christian; Smetacek, Victor (2007). "Armor: Why, when, and How". Evolution of Primary Producers in the Sea. pp. 311–332. doi:10.1016/B978-012370518-1/50015-1. ISBN 9780123705181.
  30. ^ Brussaard, Corina P. D. (2004). "Viral Control of Phytoplankton Populations-a Review1". The Journal of Eukaryotic Microbiology. 51 (2): 125–138. doi:10.1111/j.1550-7408.2004.tb00537.x. PMID 15134247. S2CID 21017882.
  31. ^ Johns, Christopher T.; Grubb, Austin R.; Nissimov, Jozef I.; Natale, Frank; Knapp, Viki; Mui, Alwin; Fredricks, Helen F.; Van Mooy, Benjamin A. S.; Bidle, Kay D. (2019). "The mutual interplay between calcification and coccolithovirus infection". Environmental Microbiology. 21 (6): 1896–1915. Bibcode:2019EnvMi..21.1896J. doi:10.1111/1462-2920.14362. PMC 7379532. PMID 30043404.
  32. ^ Haunost, Mathias; Riebesell, Ulf; Bach, Lennart T. (2020). "The Calcium Carbonate Shell of Emiliania huxleyi Provides Limited Protection Against Viral Infection". Frontiers in Marine Science. 7. doi:10.3389/fmars.2020.530757.
  33. ^ Calbet, Albert; Landry, Michael R. (2004). "Phytoplankton growth, microzooplankton grazing, and carbon cycling in marine systems". Limnology and Oceanography. 49 (1): 51–57. Bibcode:2004LimOc..49...51C. doi:10.4319/lo.2004.49.1.0051. hdl:10261/134985. S2CID 22995996.
  34. ^ Mayers, K.M.J.; Poulton, A.J.; Daniels, C.J.; Wells, S.R.; Woodward, E.M.S.; Tarran, G.A.; Widdicombe, C.E.; Mayor, D.J.; Atkinson, A.; Giering, S.L.C. (2019). "Growth and mortality of coccolithophores during spring in a temperate Shelf Sea (Celtic Sea, April 2015)". Progress in Oceanography. 177: 101928. Bibcode:2019PrOce.17701928M. doi:10.1016/j.pocean.2018.02.024. S2CID 135347218.
  35. ^ Young, J. R. (1994) "Functions of coccoliths". In: Coccolithophores, Eds A. Winter and W. G. Siesser (Cambridge: Cambridge University Press), 63–82.
  36. ^ Tillmann, Urban (2004). "Interactions between Planktonic Microalgae and Protozoan Grazers1". The Journal of Eukaryotic Microbiology. 51 (2): 156–168. doi:10.1111/j.1550-7408.2004.tb00540.x. PMID 15134250. S2CID 36526359.
  37. ^ Breckels, M. N.; Roberts, E. C.; Archer, S. D.; Malin, G.; Steinke, M. (2011). "The role of dissolved infochemicals in mediating predator-prey interactions in the heterotrophic dinoflagellate Oxyrrhis marina". Journal of Plankton Research. 33 (4): 629–639. doi:10.1093/plankt/fbq114.
  38. ^ Aloisi, G. (6 August 2015). "Covariation of metabolic rates and cell size in coccolithophores". Biogeosciences. 12 (15). Copernicus GmbH: 4665–4692. Bibcode:2015BGeo...12.4665A. doi:10.5194/bg-12-4665-2015. ISSN 1726-4189. S2CID 6227548.
  39. ^ Henderiks, Jorijntje (2008). "Coccolithophore size rules — Reconstructing ancient cell geometry and cellular calcite quota from fossil coccoliths". Marine Micropaleontology. 67 (1–2). Elsevier BV: 143–154. Bibcode:2008MarMP..67..143H. doi:10.1016/j.marmicro.2008.01.005. ISSN 0377-8398.
  40. ^ a b Moheimani, N.R.; Webb, J.P.; Borowitzka, M.A. (2012), "Bioremediation and other potential applications of coccolithophorid algae: A review. . Bioremediation and other potential applications of coccolithophorid algae: A review", Algal Research, 1 (2): 120–133, doi:10.1016/j.algal.2012.06.002
  41. ^ a b Billard, Chantal; Inouye, Isoa (August 17, 2004). "What is new in coccolithophore biology?". In Thierstein, Hans R.; Young, Jeremy R. (eds.). Coccolithophores-from molecular processes to global impact. Berlin: Springler. pp. 1–29. ISBN 9783540219286..
  42. ^ a b Jordan, R.W. (2012), "Haptophyta", eLS, doi:10.1002/9780470015902.a0001981.pub2, ISBN 978-0470016176
  43. ^ a b Young, J.R.; Karen, H. (2003). "Biomineralization Within Vesicles: The Calcite of Coccoliths". In Dove, P.M.; Yoreo, J.J.; Weiner, S. (eds.). Reviews in Mineralogy and Geochemistry. Washington, D.C.: Mineralogical Society of America. pp. 189–216.
  44. ^ a b Vardi, A.; et al. (2012), "Host–virus dynamics and subcellular controls of cell fate in a natural coccolithophore population", Proceedings of the National Academy of Sciences, 109 (47): 19327–19332, Bibcode:2012PNAS..10919327V, doi:10.1073/pnas.1208895109, PMC 3511156, PMID 23134731
  45. ^ a b c Houdan; Probert, I; Zatylny, C; Véron, B; Billard, C; et al. (2006), ". Ecology of oceanic coccolithophores. I. Nutritional preferences of the two stages in the life cycle of Coccolithus braarudii and Calcidiscus leptoporus", Aquatic Microbial Ecology, 44: 291–301, doi:10.3354/ame044291
  46. ^ a b c Hogan, M.C. ""Coccolithophores"". In Cleveland, Cutler J. (ed.). Encyclopedia of Earth. Washington, D.C.: Environmental Information Coalition, National Council for Science and the Environment.
  47. ^ a b Geisen, M.; et al. (August 17, 2004). "Species level variation in coccolithophores=". In Thierstein, Hans R.; Young, Jeremy R. (eds.). Coccolithophores-from molecular processes to global impact. Berlin: Springler. pp. 1–29. ISBN 9783540219286..
  48. ^ a b Jordan, R. W.; Chamberlain, A.H.L. (1997), "Biodiversity among haptophyte algae", Biodiversity & Conservation, 6 (1): 131–152, doi:10.1023/A:1018383817777, S2CID 9564456
  49. ^ Boeckel; Baumann, Karl-Heinz; Henrich, Rüdiger; Kinkel, Hanno; et al. (2006), "Coccolith distribution patterns in South Atlantic and Southern Ocean surface sediments in relation to environmental gradients", Deep-Sea Research Part I: Oceanographic Research Papers, 53 (6): 1073–1099, Bibcode:2006DSRI...53.1073B, doi:10.1016/j.dsr.2005.11.006
  50. ^ a b c de Vargas, C.; Aubrey, M.P.; Probert, I.; Young, J. (2007). "From coastal hunters to oceanic farmers.". In Falkowski, P.G.; Knoll, A.H. (eds.). Origin and Evolution of Coccolithophores. Boston: Elsevier. pp. 251–285.
  51. ^ a b c Okada; Honjo, Susumu; et al. (1973), "The distribution of oceanic coccolithophores in the Pacific", Deep-Sea Research and Oceanographic Abstracts, 20 (4): 355–374, Bibcode:1973DSRA...20..355O, doi:10.1016/0011-7471(73)90059-4
  52. ^ a b Kinkel, H.; et al. (2000), "Coccolithophores in the equatorial Atlantic Ocean: response to seasonal and Late Quaternary surface water variability", Marine Micropaleontology, 39 (1–4): 87–112, Bibcode:2000MarMP..39...87K, doi:10.1016/s0377-8398(00)00016-5
  53. ^ Gafar, N. A., Eyre, B. D. and Schulz, K. G. (2019). "A comparison of species specific sensitivities to changing light and carbonate chemistry in calcifying marine phytoplankton". Scientific Reports, 9(1): 1–12. doi:10.1038/s41598-019-38661-0. Material was copied from this source, which is available under a Creative Commons Attribution 4.0 International License.
  54. ^ a b c Young, J.R.; et al. (2009), "Coccolith function and morphogenesis: insights from appendage-bearing coccolithophores of the family syracosphaeraceae (haptophyta)", Journal of Phycology, 45 (1): 213–226, doi:10.1111/j.1529-8817.2008.00643.x, PMID 27033659, S2CID 27901484
  55. ^ Daniels, C.J., Sheward, R.M. and Poulton, A.J. (2014) "Biogeochemical implications of comparative growth rates of Emiliania huxleyi and Coccolithus species". Biogeosciences, 11(23): 6915–6925. doi:10.5194/bg-11-6915-2014.
  56. ^ Durak, G.M., Taylor, A.R., Walker, C.E., Probert, I., De Vargas, C., Audic, S., Schroeder, D., Brownlee, C. and Wheeler, G.L. (2016) "A role for diatom-like silicon transporters in calcifying coccolithophores". Nature communications, 7: 10543. doi:10.1038/ncomms10543. Material was copied from this source, which is available under a Creative Commons Attribution 4.0 International License.
  57. ^ Smith, Helen E. K.; Poulton, Alex J.; Garley, Rebecca; Hopkins, Jason; Lubelczyk, Laura C.; Drapeau, Dave T.; Rauschenberg, Sara; Twining, Ben S.; Bates, Nicholas R.; Balch, William M. (2017). "The influence of environmental variability on the biogeography of coccolithophores and diatoms in the Great Calcite Belt". Biogeosciences. 14 (21): 4905–4925. Bibcode:2017BGeo...14.4905S. doi:10.5194/bg-14-4905-2017. Material was copied from this source, which is available under a Creative Commons Attribution 4.0 International License.
  58. ^ Balch, W. M.; Gordon, Howard R.; Bowler, B. C.; Drapeau, D. T.; Booth, E. S. (2005). "Calcium carbonate measurements in the surface global ocean based on Moderate-Resolution Imaging Spectroradiometer data". Journal of Geophysical Research. 110 (C7): C07001. Bibcode:2005JGRC..110.7001B. doi:10.1029/2004JC002560.
  59. ^ Sarmiento, Jorge L.; Hughes, Tertia M. C.; Stouffer, Ronald J.; Manabe, Syukuro (1998). "Simulated response of the ocean carbon cycle to anthropogenic climate warming". Nature. 393 (6682): 245–249. Bibcode:1998Natur.393..245S. doi:10.1038/30455. S2CID 4317429.
  60. ^ Sarmiento, J. L.; Slater, R.; Barber, R.; Bopp, L.; Doney, S. C.; Hirst, A. C.; Kleypas, J.; Matear, R.; Mikolajewicz, U.; Monfray, P.; Soldatov, V.; Spall, S. A.; Stouffer, R. (2004). "Response of ocean ecosystems to climate warming" (PDF). Global Biogeochemical Cycles. 18 (3): n/a. Bibcode:2004GBioC..18.3003S. doi:10.1029/2003GB002134. hdl:1912/3392. S2CID 15482539.
  61. ^ Balch, W. M.; Drapeau, D. T.; Bowler, B. C.; Lyczskowski, E.; Booth, E. S.; Alley, D. (2011). "The contribution of coccolithophores to the optical and inorganic carbon budgets during the Southern Ocean Gas Exchange Experiment: New evidence in support of the "Great Calcite Belt" hypothesis". Journal of Geophysical Research. 116 (C4): C00F06. Bibcode:2011JGRC..116.0F06B. doi:10.1029/2011JC006941.
  62. ^ Sabine, C. L.; Feely, R. A.; Gruber, N.; Key, R. M.; Lee, K.; Bullister, J. L.; Wanninkhof, R.; Wong, C. S.; Wallace, D. W.; Tilbrook, B.; Millero, F. J.; Peng, T. H.; Kozyr, A.; Ono, T.; Rios, A. F. (2004). "The Oceanic Sink for Anthropogenic CO2" (PDF). Science. 305 (5682): 367–371. Bibcode:2004Sci...305..367S. doi:10.1126/science.1097403. PMID 15256665. S2CID 5607281.
  63. ^ Gitau, Beatrice (28 November 2015). "What's fueling the rise of coccolithophores in the oceans?". www.csmonitor.com. The Christian Science Monitor. Retrieved 30 November 2015.
  64. ^ "Viral Zone". ExPASy. Retrieved 15 June 2015.
  65. ^ ICTV. "Virus Taxonomy: 2014 Release". Retrieved 15 June 2015.
  66. ^ Largest known viral genomes Giantviruses.org. Accessed: 11 June 2020.
  67. ^ Rost, B.; Riebesell, U. (2004), "Coccolithophores and the biological pump: responses to environmental changes" (PDF), Coccolithophores, 2: 99–125, CiteSeerX 10.1.1.455.2864, doi:10.1007/978-3-662-06278-4_5, ISBN 978-3-642-06016-8, archived (PDF) from the original on 2012-11-10
  68. ^ Morrissey, J.F.; Sumich, J.L. (2012). Introduction to the Biology of Marine Life. p. 67.
  69. ^ a b Houdan, A.; et al. (2004), "Toxicity of coastal coccolithophores (Prymnesiophyceae, Haptophyta)", Journal of Plankton Research, 26 (8): 875–883, doi:10.1093/plankt/fbh079
  70. ^ Litchman, E.; et al. (2007), "The role of functional traits and trade-offs in structuring phytoplankton communities: scaling from cellular to ecosystem level", Ecology Letters, 10 (12): 1170–1181, Bibcode:2007EcolL..10.1170L, doi:10.1111/j.1461-0248.2007.01117.x, PMID 17927770
  71. ^ Frada, M.; et al. (2008), "The "Cheshire Cat" escape strategy of the coccolithophore Emiliania huxleyi in response to viral infection", Proceedings of the National Academy of Sciences, 105 (41): 15944–15949, Bibcode:2008PNAS..10515944F, doi:10.1073/pnas.0807707105, PMC 2572935, PMID 18824682
  72. ^ Taylor, Alison R.; Brownlee, Colin; Wheeler, Glen (2017-01-03). "Coccolithophore Cell Biology: Chalking Up Progress" (PDF). Annual Review of Marine Science. 9 (1). Annual Reviews: 283–310. Bibcode:2017ARMS....9..283T. doi:10.1146/annurev-marine-122414-034032. ISSN 1941-1405. PMID 27814031. Archived (PDF) from the original on 2021-07-16.
  73. ^ Gardin, Silvia; Krystyn, Leopold; Richoz, Sylvain; Bartolini, Annachiara; Galbrun, Bruno (October 2012). "Where and when the earliest coccolithophores?: Where and when the earliest coccolithophores?". Lethaia. 45 (4): 507–523. doi:10.1111/j.1502-3931.2012.00311.x.
  74. ^ Falkowski, P.G.; Knoll, A.H. (August 29, 2007). Evolution of Primary Producers in the Sea. Amsterdam, Boston: Elsevier Academic Press. ISBN 9780123705181.
  75. ^ Linschooten, Cornelis; et al. (1991), "Role of the light-dark cycle and medium composition on the production of coccoliths by Emiliania huxleyi (haptophyceae)", Journal of Phycology, 27 (1): 82–86, doi:10.1111/j.0022-3646.1991.00082.x, S2CID 84368830
  76. ^ "Microscopic marine plants bioengineer their environment to enhance their own growth - The Conversation". 2 August 2016.
  77. ^ Westbroek, P.; et al. (1983), "Calcification in Coccolithophoridae: Wasteful or Functional?", Ecological Bulletins: 291–299
  78. ^ Irie, Takahiro; et al. (2010), "Increasing costs due to ocean acidification drives phytoplankton to be more heavily calcified: optimal growth strategy of coccolithophores", PLOS ONE, 5 (10): e13436, Bibcode:2010PLoSO...513436I, doi:10.1371/journal.pone.0013436, PMC 2955539, PMID 20976167
  79. ^ Krumhardt, Kristen M.; Lovenduski, Nicole S.; Iglesias-Rodriguez, M. Debora; Kleypas, Joan A. (2017). "Coccolithophore growth and calcification in a changing ocean". Progress in Oceanography. 159: 276–295. Bibcode:2017PrOce.159..276K. doi:10.1016/j.pocean.2017.10.007.
  80. ^ Daniels, Chris J.; Poulton, Alex J.; Balch, William M.; Marañón, Emilio; Adey, Tim; Bowler, Bruce C.; Cermeño, Pedro; Charalampopoulou, Anastasia; Crawford, David W.; Drapeau, Dave; Feng, Yuanyuan; Fernández, Ana; Fernández, Emilio; Fragoso, Glaucia M.; González, Natalia; Graziano, Lisa M.; Heslop, Rachel; Holligan, Patrick M.; Hopkins, Jason; Huete-Ortega, María; Hutchins, David A.; Lam, Phoebe J.; Lipsen, Michael S.; López-Sandoval, Daffne C.; Loucaides, Socratis; Marchetti, Adrian; Mayers, Kyle M. J.; Rees, Andrew P.; Sobrino, Cristina; et al. (2018). "A global compilation of coccolithophore calcification rates". Earth System Science Data. 10 (4): 1859–1876. Bibcode:2018ESSD...10.1859D. doi:10.5194/essd-10-1859-2018. Material was copied from this source, which is available under a Creative Commons Attribution 4.0 International License.
  81. ^ a b Taylor, Alison R.; Chrachri, Abdul; Wheeler, Glen; Goddard, Helen; Brownlee, Colin (2011). "A Voltage-Gated H+ Channel Underlying pH Homeostasis in Calcifying Coccolithophores". PLOS Biology. 9 (6): e1001085. doi:10.1371/journal.pbio.1001085. PMC 3119654. PMID 21713028.
  82. ^ Taylor, Alison R.; Brownlee, Colin; Wheeler, Glen L. (2012). "Proton channels in algae: Reasons to be excited". Trends in Plant Science. 17 (11): 675–684. doi:10.1016/j.tplants.2012.06.009. PMID 22819465.
  83. ^ Benner, Ina; Diner, Rachel E.; Lefebvre, Stephane C.; Li, Dian; Komada, Tomoko; Carpenter, Edward J.; Stillman, Jonathon H. (2013). "Emiliania huxleyi increases calcification but not expression of calcification-related genes in long-term exposure to elevated temperature and p CO 2". Philosophical Transactions of the Royal Society B: Biological Sciences. 368 (1627). doi:10.1098/rstb.2013.0049. PMC 3758179. PMID 23980248.
  84. ^ Lohbeck, Annette; Tietjens, Maike; Bund, Andreas (2014). "Das physische Selbstkonzept, die individuell präferierte Bezugsnormorientierung und die Zielorientierung bei Grundschulkindern der zweiten und vierten Jahrgangsstufe". Zeitschrift für Sportpsychologie. 21: 1–12. doi:10.1026/1612-5010/a000109.
  85. ^ a b Erba, Elisabetta; Tremolada, Fabrizio (2004). "Nannofossil carbonate fluxes during the Early Cretaceous: Phytoplankton response to nutrification episodes, atmospheric CO2, and anoxia". Paleoceanography. 19 (1): n/a. Bibcode:2004PalOc..19.1008E. doi:10.1029/2003PA000884.
  86. ^ a b Erba, Elisabetta (2006). "The first 150 million years history of calcareous nannoplankton: Biosphere–geosphere interactions". Palaeogeography, Palaeoclimatology, Palaeoecology. 232 (2–4): 237–250. Bibcode:2006PPP...232..237E. doi:10.1016/j.palaeo.2005.09.013.
  87. ^ a b c d Bach, Lennart Thomas; Riebesell, Ulf; Gutowska, Magdalena A.; Federwisch, Luisa; Schulz, Kai Georg (2015). "A unifying concept of coccolithophore sensitivity to changing carbonate chemistry embedded in an ecological framework". Progress in Oceanography. 135: 125–138. Bibcode:2015PrOce.135..125B. doi:10.1016/j.pocean.2015.04.012. Material was copied from this source, which is available under a Creative Commons Attribution 4.0 International License.
  88. ^ Van De Waal, Dedmer B.; John, Uwe; Ziveri, Patrizia; Reichart, Gert-Jan; Hoins, Mirja; Sluijs, Appy; Rost, Björn (2013). "Ocean Acidification Reduces Growth and Calcification in a Marine Dinoflagellate". PLOS ONE. 8 (6): e65987. Bibcode:2013PLoSO...865987V. doi:10.1371/journal.pone.0065987. PMC 3679017. PMID 23776586.
  89. ^ Tortell, Philippe D. (2000). "Evolutionary and ecological perspectives on carbon acquisition in phytoplankton". Limnology and Oceanography. 45 (3): 744–750. Bibcode:2000LimOc..45..744T. doi:10.4319/lo.2000.45.3.0744.
  90. ^ Fu, Fei-Xue; Zhang, Yaohong; Warner, Mark E.; Feng, Yuanyuan; Sun, Jun; Hutchins, David A. (2008). "A comparison of future increased CO2 and temperature effects on sympatric Heterosigma akashiwo and Prorocentrum minimum". Harmful Algae. 7: 76–90. doi:10.1016/j.hal.2007.05.006.
  91. ^ Reinfelder, John R. (2011). "Carbon Concentrating Mechanisms in Eukaryotic Marine Phytoplankton". Annual Review of Marine Science. 3: 291–315. Bibcode:2011ARMS....3..291R. doi:10.1146/annurev-marine-120709-142720. PMID 21329207.
  92. ^ Xu, K.; Hutchins, D.; Gao, K. (9 April 2018). "Coccolith arrangement follows Eulerian mathematics in the coccolithophore Emiliania huxleyi". PeerJ. 6: e4608. doi:10.7717/PEERJ.4608. ISSN 2167-8359. PMC 5896503. PMID 29666762. Wikidata Q52718666.
  93. ^ Fileman, E.S.; Cummings, D.G.; Llewellyn, C.A. (2002). "Microplankton community structure and the impact of microzooplankton grazing during an Emiliania huxleyi bloom, off the Devon coast". Journal of the Marine Biological Association of the United Kingdom. 82 (3): 359–368. Bibcode:2002JMBUK..82..359F. doi:10.1017/S0025315402005593. S2CID 85890446.
  94. ^ Olson, M.Brady; Strom, Suzanne L. (2002). "Phytoplankton growth, microzooplankton herbivory and community structure in the southeast Bering Sea: Insight into the formation and temporal persistence of an Emiliania huxleyi bloom". Deep Sea Research Part II: Topical Studies in Oceanography. 49 (26): 5969–5990. Bibcode:2002DSRII..49.5969O. doi:10.1016/S0967-0645(02)00329-6.
  95. ^ Mayers, K.M.J.; Poulton, A.J.; Daniels, C.J.; Wells, S.R.; Woodward, E.M.S.; Tarran, G.A.; Widdicombe, C.E.; Mayor, D.J.; Atkinson, A.; Giering, S.L.C. (2019). "Growth and mortality of coccolithophores during spring in a temperate Shelf Sea (Celtic Sea, April 2015)". Progress in Oceanography. 177: 101928. Bibcode:2019PrOce.17701928M. doi:10.1016/j.pocean.2018.02.024. S2CID 135347218.
  96. ^ Mayers, Kyle M. J.; Poulton, Alex J.; Bidle, Kay; Thamatrakoln, Kimberlee; Schieler, Brittany; Giering, Sarah L. C.; Wells, Seona R.; Tarran, Glen A.; Mayor, Dan; Johnson, Matthew; Riebesell, Ulf; Larsen, Aud; Vardi, Assaf; Harvey, Elizabeth L. (2020). "The Possession of Coccoliths Fails to Deter Microzooplankton Grazers". Frontiers in Marine Science. 7. doi:10.3389/fmars.2020.569896. hdl:1912/26802.
  97. ^ Hansen, FC; Witte, HJ; Passarge, J. (1996). "Grazing in the heterotrophic dinoflagellate Oxyrrhis marina: Size selectivity and preference for calcified Emiliania huxleyi cells". Aquatic Microbial Ecology. 10: 307–313. doi:10.3354/ame010307.
  98. ^ a b Harvey, Elizabeth L.; Bidle, Kay D.; Johnson, Matthew D. (2015). "Consequences of strain variability and calcification in Emiliania huxleyion microzooplankton grazing". Journal of Plankton Research: fbv081. doi:10.1093/plankt/fbv081. hdl:1912/7739.
  99. ^ a b Strom, Suzanne L.; Bright, Kelley J.; Fredrickson, Kerri A.; Cooney, Elizabeth C. (2018). "Phytoplankton defenses: Do Emiliania huxleyi coccoliths protect against microzooplankton predators?". Limnology and Oceanography. 63 (2): 617–627. Bibcode:2018LimOc..63..617S. doi:10.1002/lno.10655. S2CID 90415703.
  100. ^ Mejia, R. (2011), "Will Ion Channels Help Coccolithophores Adapt to Ocean Acidification?", PLOS Biology, 9 (6): e1001087, doi:10.1371/journal.pbio.1001087, PMC 3119655, PMID 21713029
  101. ^ Mackinder; Wheeler, Glen; Schroeder, Declan; Riebesell, Ulf; Brownlee, Colin; et al. (2010), "Molecular Mechanisms Underlying Calcification in Coccolithophores", Geomicrobiology Journal, 27 (6–7): 585–595, Bibcode:2010GmbJ...27..585M, doi:10.1080/01490451003703014, S2CID 85403507
  102. ^ Bates; Michaels, Anthony F.; Knap, Anthony H.; et al. (1996), "Alkalinity changes in the Sargasso Sea; geochemical evidence of calfication?", Marine Chemistry, 51 (4): 347–358, Bibcode:1996MarCh..51..347B, doi:10.1016/0304-4203(95)00068-2
  103. ^ a b Marsh, M.E. (2003), "Regulation of CaCO3 formation in coccolithophores", Comparative Biochemistry and Physiology B, 136 (4): 743–754, doi:10.1016/s1096-4959(03)00180-5, PMID 14662299
  104. ^ a b Beaufort, L.; et al. (2011), "Sensitivity of coccolithophores to carbonate chemistry and ocean acidification", Nature, 476 (7358): 80–3, doi:10.1038/nature10295, PMID 21814280, S2CID 4417285
  105. ^ Tyrell, T.; et al. (1999), "Optical impacts of oceanic coccolithophore blooms", Journal of Geophysical Research, 104 (C2): 3223–3241, Bibcode:1999JGR...104.3223T, doi:10.1029/1998jc900052
  106. ^ "Can seashells save the world?". Independent.co.uk. 22 April 2008.
  107. ^ "cal.mar.o". Archived from the original on 2020-12-30. Retrieved 2021-04-24.
  108. ^ Taylor, A.R.; Chrachri, A.; Wheeler, G.; Goddard, H.; Brownlee, C. (2011). "A voltage-gated H+ channel underlying pH homeostasis in calcifying coccolithophores". PLOS Biology. 9 (6): e1001085. doi:10.1371/journal.pbio.1001085. PMC 3119654. PMID 21713028.
  109. ^ Self-Trail, J.M.; et al. (2012), "Calcareous Nannofossil Assemblage Changes Across the Paleocene-Eocene Thermal Maximum: Evidence from a Shelf Setting", Marine Micropaleontology, 92–93: 61–80, Bibcode:2012MarMP..92...61S, doi:10.1016/j.marmicro.2012.05.003
  110. ^ Lloyd, G.T.; et al. (2011), "Quantifying the deep-sea rock and fossil record bias using coccolithophores", Geological Society, London, Special Publications, 358 (1): 167–177, Bibcode:2011GSLSP.358..167L, doi:10.1144/sp358.11, S2CID 129049029
  111. ^ Charlson, Robert J.; Lovelock, James E.; Andreae, Meinrat O.; Warren, Stephen G. (1987). "Oceanic phytoplankton, atmospheric sulphur, cloud albedo and climate". Nature. 326 (6114): 655–661. Bibcode:1987Natur.326..655C. doi:10.1038/326655a0. S2CID 4321239.
  112. ^ Lovelock, James (2007). The Revenge of Gaia. Penguin. ISBN 978-0-14-102597-1.
  113. ^ Larsen, S. H. (2005). "Solar variability, dimethyl sulphide, clouds, and climate". Global Biogeochemical Cycles. 19 (1): GB1014. Bibcode:2005GBioC..19.1014L. doi:10.1029/2004GB002333. S2CID 128504924.

Sources of detailed information

Introductions to coccolithophores

Retrieved from "https://en.wikipedia.org/enwiki/w/index.php?title=Coccolithophore&oldid=1243071675"