Rhodolith

Last updated
Characteristic mauve coloured rhodolith Hydrolithon reinboldii - characteristic mauve coloured rhodolith in Fiji (7341794518).jpg
Characteristic mauve coloured rhodolith

Rhodoliths (from Greek for red rocks) are colorful, unattached calcareous nodules, composed of crustose, benthic marine red algae that resemble coral. Rhodolith beds create biogenic habitat for diverse benthic communities. The rhodolithic growth habit has been attained by a number of unrelated coralline red algae, [1] organisms that deposit calcium carbonate within their cell walls to form hard structures or nodules that resemble beds of coral.

Contents

Rhodoliths do not attach themselves to the rocky seabed. Rather, they roll like tumbleweeds along the seafloor until they become too large in size to be mobilised by the prevailing wave and current regime. They may then become incorporated into a semi-continuous algal mat or form an algal build-up. [2] [3] While corals are animals that are both autotrophic (photosynthesize via their symbionts) or heterotrophic (feeding on plankton), rhodoliths produce energy solely through photosynthesis (i.e. they can only grow and survive in the photic zone of the ocean).

Scientists believe rhodoliths have been present in the world's oceans since at least the Eocene epoch, some 55 million years ago. [4]

Overview

Rhodoliths (including maërl) have been defined as calcareous nodules composed of more than 50% of coralline red algal material and consisting of one to several coralline species growing together. [5] [6]

Habitat

Benthic communities found in rhodolith beds
Example of the seaweed and zoobenthic communities found in rhodolith beds on the Brazilian coast. This picture highlights the presence of gastropods, echinoderms and a turf algae assemblage. Communities found in rhodolith beds.jpg
Benthic communities found in rhodolith beds
Example of the seaweed and zoobenthic communities found in rhodolith beds on the Brazilian coast. This picture highlights the presence of gastropods, echinoderms and a turf algae assemblage.
Vertical and latitudinal changes observed in the size and density of rhodoliths on the floor of the continental shelf off Espirito Santo in Brazil Vertical and latitudinal changes in rhodoliths on the seafloor.jpg
Vertical and latitudinal changes observed in the size and density of rhodoliths on the floor of the continental shelf off Espírito Santo in Brazil

Rhodolith beds have been found throughout the world's oceans, including in the Arctic near Greenland, in waters off British Columbia, Canada, the Gulf of California, Mexico, [7] the Mediterranean [8] as off New Zealand [9] and eastern Australia. [10] Globally, rhodoliths fill an important niche in the marine ecosystem, serving as a transition habitat between rocky areas and barren, sandy areas. Rhodoliths provide a stable and three-dimensional habitat onto and into which a wide variety of species can attach, including other algae, commercial species such as clams and scallops, and true corals. [4] Rhodoliths are resilient to a variety of environmental disturbances, but can be severely impacted by harvesting of commercial species. For these reasons, rhodolith beds deserve specific actions for monitoring and conservation. [11] [12] [13] [14] Rhodoliths come in many shapes, including laminar, branching and columnar growth forms. [15] In shallow water and high-energy environments, rhodoliths are typically mounded, thick or unbranched; branching is also rarer in deeper water, and most profuse in tropical, mid-depth waters. [1]

Geological significance

Rhodoliths are a common feature of modern and ancient carbonate shelves worldwide. [16] Rhodolith communities contribute significantly to the global calcium carbonate budget, and fossil rhodoliths are commonly used to obtain paleoecologic and paleoclimatic information. [17] [18] [19] Under the right circumstances, rhodoliths can be the main carbonate sediment producers, [20] [21] often forming rudstone or floatstone beds consisting of rhodoliths and their fragments in grainy matrix.

Climate change and the rhodolith holobiont

A view of rhodolith beds impacted by the warmer and more acidified oceans predicted by the IPPC. Rhodolith bed physiognomy impacted by warmer and more acidified waters.jpg
A view of rhodolith beds impacted by the warmer and more acidified oceans predicted by the IPPC.

Rhodoliths are significant photosynthesizers, calcifiers, and ecosystem engineers, which raises an issue about how they might respond to ocean acidification. [23]

Changes in ocean carbonate chemistry driven by increasing anthropogenic carbon dioxide emissions promotes ocean acidification. Increasing the ocean carbon dioxide uptake results in increases in pCO2 (the partial pressure of carbon dioxide in the ocean) as well as lower pH levels and a lower carbonate saturation in the seawater. These affect the calcification process. [24] Organisms like rhodoliths accrete carbonate as part of their physical structure, since precipitating CaCO3 would be less efficient. [25] [26] Ocean acidification presents a threat by potentially affecting their growth and reproduction. [27] [28] Coralline algae are particularly sensitive to ocean acidification because they precipitate high magnesium-calcite carbonate skeletons, the most soluble form of CaCO3. [29] [30] [23]

Calcification rates in coralline algae are thought to be directly related to their photosynthetic rates, but it is not clear how a high-CO2 environment might affect rhodoliths. [31] Elevated CO2 levels might impair biomineralization due to decreased seawater carbonate (CO2−
3
) availability as pH falls, but photosynthesis could be promoted as the availability of bicarbonate (HCO
3
) increases. [32] This would result in a parabolic relationship between declining pH and coralline algal fitness, which could explain why varied responses to declining pH and elevated pCO2 have been recorded to date. [33] [23]

Climate change and the rhodolith holobiont
Expected parabolic relationship between climate change stressors and rhodolith holobiont fitness. Under normal conditions healthy rhodoliths possess stable microbiomes, important to holobiont function. However, beyond the thresholds of algal physiological tolerance, disruption of positive host-microbiome interactions occurs, detrimentally affecting holobiont fitness. Climate change stressors and rhodolith holobiont fitness.webp
Climate change and the rhodolith holobiont
Expected parabolic relationship between climate change stressors and rhodolith holobiont fitness. Under normal conditions healthy rhodoliths possess stable microbiomes, important to holobiont function. However, beyond the thresholds of algal physiological tolerance, disruption of positive host-microbiome interactions occurs, detrimentally affecting holobiont fitness.

The widespread distribution of rhodoliths hints at the resilience of this algal group, which have persisted as chief components of benthic marine communities through considerable environment changes over geologic times. [34] [23]

In 2018 the first metagenomic analysis of live rhodoliths was published. Whole genome shotgun sequencing was performed on a variety of rhodolith bed constituents. This revealed a stable live rhodolith microbiome thriving under elevated pCO2 conditions, with positive physiological responses such as increased photosynthetic activity and no calcium carbonate biomass loss over time. However, the seawater column and coralline skeleton biofilms showed significant microbial shifts. These findings reinforce the existence of a close host-microbe functional entity, where the metabolic crosstalk within the rhodolith as a holobiont could be exerting reciprocal influence over the associated microbiome. [23]

While the microbiome associated with live rhodoliths remained stable and resembled a healthy holobiont, the microbial community associated with the water column changed after exposure to elevated pCO2. [23]

See also

Related Research Articles

<span class="mw-page-title-main">Coccolithophore</span> Unicellular algae responsible for the formation of chalk

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. Coccolithophores are almost exclusively marine, are photosynthetic, and exist in large numbers throughout the sunlight zone of the ocean.

<span class="mw-page-title-main">Coralline algae</span> Order of algae (Corallinales)

Coralline algae are red algae in the order Corallinales. They are characterized by a thallus that is hard because of calcareous deposits contained within the cell walls. The colors of these algae are most typically pink, or some other shade of red, but some species can be purple, yellow, blue, white, or gray-green. Coralline algae play an important role in the ecology of coral reefs. Sea urchins, parrot fish, and limpets and chitons feed on coralline algae. In the temperate Mediterranean Sea, coralline algae are the main builders of a typical algal reef, the Coralligène ("coralligenous"). Many are typically encrusting and rock-like, found in marine waters all over the world. Only one species lives in freshwater. Unattached specimens may form relatively smooth compact balls to warty or fruticose thalli.

<span class="mw-page-title-main">Ocean acidification</span> Decrease of pH levels in the ocean

Ocean acidification is the ongoing decrease in the pH of the Earth's ocean. Between 1950 and 2020, the average pH of the ocean surface fell from approximately 8.15 to 8.05. Carbon dioxide emissions from human activities are the primary cause of ocean acidification, with atmospheric carbon dioxide levels exceeding 410 ppm. CO2 from the atmosphere is absorbed by the oceans. This produces carbonic acid which dissociates into a bicarbonate ion and a hydrogen ion. The presence of free hydrogen ions lowers the pH of the ocean, increasing acidity. Marine calcifying organisms, such as mollusks and corals, are especially vulnerable because they rely on calcium carbonate to build shells and skeletons.

<span class="mw-page-title-main">Maerl</span> Coralline red algae

Maerl is a collective name for non-geniculate coralline red algae with a certain growth habit. Maerl grows at a rate of c. 1 mm per year. It accumulates as unattached particles and forms extensive beds in suitable sublittoral sites. The term maerl originally refers to the branched growth form of Lemoine (1910) and rhodolith is a sedimentological or genetic term for both the nodular and branched growth forms.

<i>Aplysia punctata</i> Species of gastropod

The spotted sea hare is a species of sea slug in the family Aplysiidae, the sea hares. It reaches a length of up to 20 cm (7.9 in) and is found in the northeast Atlantic, ranging from Greenland and Norway to the Mediterranean Sea.

Marine chemistry, also known as ocean chemistry or chemical oceanography, is influenced by plate tectonics and seafloor spreading, turbidity currents, sediments, pH levels, atmospheric constituents, metamorphic activity, and ecology. The field of chemical oceanography studies the chemistry of marine environments including the influences of different variables. Marine life has adapted to the chemistries unique to Earth's oceans, and marine ecosystems are sensitive to changes in ocean chemistry.

<span class="mw-page-title-main">Effects of climate change on oceans</span> Overview of all the effects of climate change on oceans

There are many effects of climate change on oceans. One of the main ones is an increase in ocean temperatures. More frequent marine heatwaves are linked to this. The rising temperature contributes to a rise in sea levels. Other effects include ocean acidification, sea ice decline, increased ocean stratification and reductions in oxygen levels. Changes to ocean currents including a weakening of the Atlantic meridional overturning circulation are another important effect. All these changes have knock-on effects which disturb marine ecosystems. The main cause of these changes is climate change due to human emissions of greenhouse gases. Carbon dioxide and methane are examples of greenhouse gases. This leads to ocean warming, because the ocean takes up most of the additional heat in the climate system. The ocean absorbs some of the extra carbon dioxide in the atmosphere. This causes the pH value of the ocean to drop. Scientists estimate that the ocean absorbs about 25% of all human-caused CO2 emissions.

<span class="mw-page-title-main">Oceanic carbon cycle</span> Ocean/atmosphere carbon exchange process

The oceanic carbon cycle is composed of processes that exchange carbon between various pools within the ocean as well as between the atmosphere, Earth interior, and the seafloor. The carbon cycle is a result of many interacting forces across multiple time and space scales that circulates carbon around the planet, ensuring that carbon is available globally. The Oceanic carbon cycle is a central process to the global carbon cycle and contains both inorganic carbon and organic carbon. Part of the marine carbon cycle transforms carbon between non-living and living matter.

<span class="mw-page-title-main">Shell growth in estuaries</span>

Shell growth in estuaries is an aspect of marine biology that has attracted a number of scientific research studies. Many groups of marine organisms produce calcified exoskeletons, commonly known as shells, hard calcium carbonate structures which the organisms rely on for various specialized structural and defensive purposes. The rate at which these shells form is greatly influenced by physical and chemical characteristics of the water in which these organisms live. Estuaries are dynamic habitats which expose their inhabitants to a wide array of rapidly changing physical conditions, exaggerating the differences in physical and chemical properties of the water.

Estuarine acidification happens when the pH balance of water in coastal marine ecosystems, specifically those of estuaries, decreases. Water, generally considered neutral on the pH scale, normally perfectly balanced between alkalinity and acidity. While ocean acidification occurs due to the ongoing decrease in the pH of the Earth's oceans, caused by the absorption of carbon dioxide (CO2) from the atmosphere, pH change in estuaries is more complicated than in the open ocean due to direct impacts from land run-off, human impact, and coastal current dynamics. In the ocean, wave and wind movement allows carbon dioxide (CO2) to mixes with water (H2O) forming carbonic acid (H2CO3). Through wave motion this chemical bond is mixed up, allowing for the further break of the bond, eventually becoming carbonate (CO3) which is basic and helps form shells for ocean creatures, and two hydron molecules. This creates the potential for acidic threat since hydron ions readily bond with any Lewis Structure to form an acidic bond. This is referred to as an oxidation-reduction reaction.

<span class="mw-page-title-main">Ocean acidification in the Great Barrier Reef</span> Threat to the reef which reduces the viability and strength of reef-building corals

Ocean acidification threatens the Great Barrier Reef by reducing the viability and strength of coral reefs. The Great Barrier Reef, considered one of the seven natural wonders of the world and a biodiversity hotspot, is located in Australia. Similar to other coral reefs, it is experiencing degradation due to ocean acidification. Ocean acidification results from a rise in atmospheric carbon dioxide, which is taken up by the ocean. This process can increase sea surface temperature, decrease aragonite, and lower the pH of the ocean. The more humanity consumes fossil fuels, the more the ocean absorbs released CO₂, furthering ocean acidification.

<span class="mw-page-title-main">Marine biogenic calcification</span> Shell formation mechanism

Marine biogenic calcification is the process by which marine organisms such as oysters and clams form calcium carbonate. Seawater is full of dissolved compounds, ions and nutrients that organisms can use for energy and, in the case of calcification, to build shells and outer structures. Calcifying organisms in the ocean include molluscs, foraminifera, coccolithophores, crustaceans, echinoderms such as sea urchins, and corals. The shells and skeletons produced from calcification have important functions for the physiology and ecology of the organisms that create them.

<span class="mw-page-title-main">Justin B. Ries</span> American marine scientist

Justin Baker Ries is an American marine scientist, best known for his contributions to ocean acidification, carbon sequestration, and biomineralization research.

<span class="mw-page-title-main">Ocean acidification in the Arctic Ocean</span>

The Arctic ocean covers an area of 14,056,000 square kilometers, and supports a diverse and important socioeconomic food web of organisms, despite its average water temperature being 32 degrees Fahrenheit. Over the last three decades, the Arctic Ocean has experienced drastic changes due to climate change. One of the changes is in the acidity levels of the ocean, which have been consistently increasing at twice the rate of the Pacific and Atlantic oceans. Arctic Ocean acidification is a result of feedback from climate system mechanisms, and is having negative impacts on Arctic Ocean ecosystems and the organisms that live within them.

Sporolithon ptychoides is a species of crustose red seaweed with a hard, calcareous skeleton in the family Corallinaceae. It has a widespread distribution, being present in the Pacific and Indian Oceans, the Mediterranean Sea and the southwestern Atlantic Ocean.

<span class="mw-page-title-main">Human impact on marine life</span>

Human activities affect marine life and marine habitats through overfishing, habitat loss, the introduction of invasive species, ocean pollution, ocean acidification and ocean warming. These impact marine ecosystems and food webs and may result in consequences as yet unrecognised for the biodiversity and continuation of marine life forms.

<span class="mw-page-title-main">Jean-Pierre Gattuso</span> French ocean scientist (born 1958)

Jean-Pierre Gattuso is a French ocean scientist conducting research globally, from the pole to the tropics and from nearshore to the open ocean. His research addresses the biology of reef-building corals, the biogeochemistry of coastal ecosystems, and the response of marine plants, animals and ecosystems to global environmental change. He is also interested in transdisciplinary research, collaborating with social scientists to address ocean-based solutions to minimize climate change and its impacts. He is currently a CNRS Research Professor at Sorbonne University.

<span class="mw-page-title-main">Particulate inorganic carbon</span>

Particulate inorganic carbon (PIC) can be contrasted with dissolved inorganic carbon (DIC), the other form of inorganic carbon found in the ocean. These distinctions are important in chemical oceanography. Particulate inorganic carbon is sometimes called suspended inorganic carbon. In operational terms, it is defined as the inorganic carbon in particulate form that is too large to pass through the filter used to separate dissolved inorganic carbon.

<span class="mw-page-title-main">Great Calcite Belt</span> High-calcite region of the Southern Ocean

The Great Calcite Belt (GCB) refers to a region of the ocean where there are high concentrations of calcite, a mineral form of calcium carbonate. The belt extends over a large area of the Southern Ocean surrounding Antarctica. The calcite in the Great Calcite Belt is formed by tiny marine organisms called coccolithophores, which build their shells out of calcium carbonate. When these organisms die, their shells sink to the bottom of the ocean, and over time, they accumulate to form a thick layer of calcite sediment.

Brenda Konar is a marine scientist, and professor at University of Alaska Fairbanks.

References

  1. 1 2 Steneck, R. S. (1986). "The Ecology of Coralline Algal Crusts: Convergent Patterns and Adaptative Strategies". Annual Review of Ecology and Systematics. 17: 273–303. doi:10.1146/annurev.es.17.110186.001421. JSTOR   2096997.
  2. Basso, Daniela; Nalin, Ronald; Massari, Francesco (2007-05-01). "Genesis and composition of the Pleistocene Coralligène de plateau of the Cutro Terrace (Calabria, southern Italy)". Neues Jahrbuch für Geologie und Paläontologie - Abhandlungen. 244 (2): 173–182. doi:10.1127/0077-7749/2007/0244-0173.
  3. Aguirre, Julio; Braga, Juan Carlos; Bassi, Davide (2017). "Rhodoliths and Rhodolith Beds in the Rock Record". Rhodolith/Maërl Beds: A Global Perspective. Coastal Research Library. Vol. 15. Springer. pp. 105–138. doi:10.1007/978-3-319-29315-8_5. ISBN   978-3-319-29315-8.
  4. 1 2 Science Daily, September 23, 2004
  5. 1 2 3 4 Horta, Paulo Antunes; Riul, Pablo; Amado Filho, Gilberto M.; Gurgel, Carlos Frederico D.; Berchez, Flávio; Nunes, José Marcos de Castro; Scherner, Fernando; Pereira, Sonia; Lotufo, Tito; Peres, Letícia; Sissini, Marina; Bastos, Eduardo de Oliveira; Rosa, João; Munoz, Pamela; Martins, Cintia; Gouvêa, Lidiane; Carvalho, Vanessa; Bergstrom, Ellie; Schubert, Nadine; Bahia, Ricardo G.; Rodrigues, Ana Claudia; Rörig, Leonardo; Barufi, José Bonomi; Figueiredo, Marcia (2016). "Rhodoliths in Brazil: Current knowledge and potential impacts of climate change". Brazilian Journal of Oceanography. 64: 117–136. doi: 10.1590/S1679-875920160870064sp2 .. CC-BY icon.svg Material was copied from this source, which is available under a Creative Commons Attribution 4.0 International License
  6. Bosellini, Alfonso; Ginsburg, Robert N. (1971). "Form and Internal Structure of Recent Algal Nodules (Rhodolites) from Bermuda". The Journal of Geology. 79 (6): 669–682. Bibcode:1971JG.....79..669B. doi:10.1086/627697. S2CID   225041671.
  7. Steller, D. L.; Riosmena‐Rodríguez, R.; Foster, M. S.; Roberts, C. A. (2003). "Rhodolith bed diversity in the Gulf of California: the importance of rhodolith structure and consequences of disturbance". Aquatic Conservation: Marine and Freshwater Ecosystems. 13 (S1): S5–S20. doi:10.1002/aqc.564. ISSN   1099-0755.
  8. Basso, Daniela; Babbini, Lorenza; Ramos-Esplá, Angel Alfonso; Salomidi, Maria (2017), Riosmena-Rodríguez, Rafael; Nelson, Wendy; Aguirre, Julio (eds.), "Mediterranean Rhodolith Beds", Rhodolith/Maërl Beds: A Global Perspective, Coastal Research Library, Cham: Springer International Publishing, vol. 15, pp. 281–298, doi:10.1007/978-3-319-29315-8_11, ISBN   978-3-319-29313-4 , retrieved 2021-01-01
  9. Nelson, W. A. (2012). Rhodolith beds in northern New Zealand: characterisation of associated biodiversity and vulnerability to environmental stressors. Wellington, NZ: Ministry for Primary Industries. ISBN   978-0-478-40077-9. OCLC   812180715.
  10. Harris, P.T., Tsuji, Y., Marshall, J.F., Davies, P.J., Honda, N., Matsuda, H., 1996. Sand and rhodolith-gravel entrainment on the mid- to outer-shelf under a western boundary current: Fraser Island continental shelf, eastern Australia. Marine Geology 129, 313-330
  11. Basso, D.; Babbini, L.; Kaleb, S.; Bracchi, V.A.; Falace, A. (2016). "Monitoring deep Mediterranean rhodolith beds". Aquatic Conservation: Marine and Freshwater Ecosystems. 26 (3): 549–561. doi: 10.1002/aqc.2586 . hdl: 11368/2849200 . ISSN   1052-7613.
  12. Barbera, C.; Bordehore, C.; Borg, J.A.; Glémarec, M.; Grall, J.; Hall-Spencer, J. M.; de la Huz, Ch.; Lanfranco, E.; Lastra, M.; Moore, P.G.; Mora, J. (2003). "Conservation and management of northeast Atlantic and Mediterranean maerl beds". Aquatic Conservation: Marine and Freshwater Ecosystems. 13 (S1): S65–S76. doi:10.1002/aqc.569. ISSN   1052-7613.
  13. Horta, P.A.; Riul, P.; Amado Filho, G-M.; Gurgel, C.F.D.; Berchez, F.; Nunes, J.M. de Castro; Scherner, F.; Pereira, S.; Lotufo, T.; Peres, L.; Sissini, M. (2016). "Rhodoliths in Brazil: Current knowledge and potential impacts of climate change". Brazilian Journal of Oceanography. 64 (SPE2): 117–136. doi: 10.1590/S1679-875920160870064sp2 . ISSN   1679-8759.
  14. Bassi, D.; Braga, J.C.; Owada, M.; Aguirre, J.; Lipps, J.H.; Takayanagi, H.; Iryu, Y. (2020). "Boring bivalve traces in modern reef and deeper water macroid and rhodolith beds". Progress in Earth and Planetary Science. 7 (1): 41. Bibcode:2020PEPS....7...41B. doi: 10.1186/s40645-020-00356-w . hdl: 10481/64249 . ISSN   2197-4284.
  15. Bosence, D. W. (1983). "Description and Classification of Rhodoliths (Rhodoids, Rhodolites)". Coated Grains. Berlin: Springer. pp. 217–224. doi:10.1007/978-3-642-68869-0_19. ISBN   9783642688690.
  16. Pomar, L.; Baceta, J.I.; Hallock, P.; Mateu-Vicens, G.; Basso, D. (2017). "Reef building and carbonate production modes in the west-central Tethys during the Cenozoic". Marine and Petroleum Geology. 83: 261–304. Bibcode:2017MarPG..83..261P. doi:10.1016/j.marpetgeo.2017.03.015. hdl: 10281/148633 .
  17. Basso, D. (1998). "Deep rhodolith distribution in the Pontian Islands, Italy: a model for the paleoecology of a temperate sea". Palaeogeography, Palaeoclimatology, Palaeoecology. 137 (1): 173–187. Bibcode:1998PPP...137..173B. doi:10.1016/S0031-0182(97)00099-0. ISSN   0031-0182.
  18. Halfar, J.; Zack, T.; Kronz, A.; Zachos, J.C. (2000). "Growth and high-resolution paleoenvironmental signals of rhodoliths (coralline red algae): A new biogenic archive". Journal of Geophysical Research: Oceans. 105 (C9): 22107–22116. Bibcode:2000JGR...10522107H. doi: 10.1029/1999JC000128 .
  19. Ragazzola, F.; Caragnano, A.; Basso, D.; Schmidt, D.N.; Fietzke, J. (2020). "Establishing temperate crustose early Holocene coralline algae as archives for palaeoenvironmental reconstructions of the shallow water habitats of the Mediterranean Sea". Palaeontology. 63 (1): 155–170. Bibcode:2020Palgy..63..155R. doi: 10.1111/pala.12447 . hdl: 1983/ab309cb5-6b7a-4d3f-b1ef-b4f3cde74579 . ISSN   1475-4983.
  20. Basso, D. (2012). "Carbonate production by calcareous red algae and global change". Geodiversitas. 34 (1): 13–33. doi:10.5252/g2012n1a2. ISSN   1280-9659. S2CID   86112464.
  21. Schubert, N.; Salazar, V. W.; Rich, W. A.; Vivanco Bercovich, M.; Almeida Saá, A. C.; Fadigas, S. D.; Silva, J.; Horta, P. A. (2019-08-01). "Rhodolith primary and carbonate production in a changing ocean: The interplay of warming and nutrients". Science of the Total Environment. 676: 455–468. Bibcode:2019ScTEn.676..455S. doi:10.1016/j.scitotenv.2019.04.280. hdl: 10754/632548 . ISSN   0048-9697. PMID   31048175. S2CID   143435207.
  22. IPPC (2014) Climate change 2014 impacts, adaptation, and vulnerability, Part B. ISBN   978-1-107-05816-3
  23. 1 2 3 4 5 6 7 Cavalcanti, Giselle S.; Shukla, Priya; Morris, Megan; Ribeiro, Bárbara; Foley, Mariah; Doane, Michael P.; Thompson, Cristiane C.; Edwards, Matthew S.; Dinsdale, Elizabeth A.; Thompson, Fabiano L. (2018). "Rhodoliths holobionts in a changing ocean: Host-microbes interactions mediate coralline algae resilience under ocean acidification". BMC Genomics. 19 (1): 701. doi: 10.1186/s12864-018-5064-4 . PMC   6154897 . PMID   30249182.. CC-BY icon.svg Material was copied from this source, which is available under a Creative Commons Attribution 4.0 International License
  24. Millero, Frank J.; Graham, Taylor B.; Huang, Fen; Bustos-Serrano, Héctor; Pierrot, Denis (2006). "Dissociation constants of carbonic acid in seawater as a function of salinity and temperature". Marine Chemistry. 100 (1–2): 80–94. Bibcode:2006MarCh.100...80M. doi:10.1016/j.marchem.2005.12.001.
  25. Orr, James C.; Fabry, Victoria J.; Aumont, Olivier; Bopp, Laurent; Doney, Scott C.; Feely, Richard A.; Gnanadesikan, Anand; Gruber, Nicolas; Ishida, Akio; Joos, Fortunat; Key, Robert M.; Lindsay, Keith; Maier-Reimer, Ernst; Matear, Richard; Monfray, Patrick; Mouchet, Anne; Najjar, Raymond G.; Plattner, Gian-Kasper; Rodgers, Keith B.; Sabine, Christopher L.; Sarmiento, Jorge L.; Schlitzer, Reiner; Slater, Richard D.; Totterdell, Ian J.; Weirig, Marie-France; Yamanaka, Yasuhiro; Yool, Andrew (2005). "Anthropogenic ocean acidification over the twenty-first century and its impact on calcifying organisms" (PDF). Nature. 437 (7059): 681–686. Bibcode:2005Natur.437..681O. doi:10.1038/nature04095. PMID   16193043. S2CID   4306199.
  26. Hoegh-Guldberg, O.; Mumby, P. J.; Hooten, A. J.; Steneck, R. S.; Greenfield, P.; Gomez, E.; Harvell, C. D.; Sale, P. F.; Edwards, A. J.; Caldeira, K.; Knowlton, N.; Eakin, C. M.; Iglesias-Prieto, R.; Muthiga, N.; Bradbury, R. H.; Dubi, A.; Hatziolos, M. E. (2007). "Coral Reefs Under Rapid Climate Change and Ocean Acidification". Science. 318 (5857): 1737–1742. Bibcode:2007Sci...318.1737H. doi:10.1126/science.1152509. hdl: 1885/28834 . PMID   18079392. S2CID   12607336.
  27. Kroeker, Kristy J.; Kordas, Rebecca L.; Crim, Ryan; Hendriks, Iris E.; Ramajo, Laura; Singh, Gerald S.; Duarte, Carlos M.; Gattuso, Jean‐Pierre (2013). "Impacts of ocean acidification on marine organisms: Quantifying sensitivities and interaction with warming". Global Change Biology. 19 (6): 1884–1896. Bibcode:2013GCBio..19.1884K. doi:10.1111/gcb.12179. PMC   3664023 . PMID   23505245.
  28. Riebesell, Ulf; Gattuso, Jean-Pierre (2015). "Lessons learned from ocean acidification research". Nature Climate Change. 5 (1): 12–14. Bibcode:2015NatCC...5...12R. doi:10.1038/nclimate2456.
  29. Bischoff, W.D., Bishop, F.C. and Mackenzie, F.T. (1983) "Biogenically produced magnesian calcite; inhomogeneities in chemical and physical properties; comparison with synthetic phases". American Mineralogist, 68(11–12): 1183–1188
  30. Martin, Sophie; Gattuso, Jean-Pierre (2009). "Response of Mediterranean coralline algae to ocean acidification and elevated temperature". Global Change Biology. 15 (8): 2089–2100. Bibcode:2009GCBio..15.2089M. doi:10.1111/j.1365-2486.2009.01874.x. S2CID   55942151.
  31. McCoy, Sophie J.; Kamenos, Nicholas A. (2015). "Coralline algae (Rhodophyta) in a changing world: Integrating ecological, physiological, and geochemical responses to global change". Journal of Phycology. 51 (1): 6–24. doi:10.1111/jpy.12262. PMC   4964943 . PMID   26986255.
  32. Johnson, Maggie Dorothy; Price, Nichole N.; Smith, Jennifer E. (2014). "Contrasting effects of ocean acidification on tropical fleshy and calcareous algae". PeerJ. 2: e411. doi: 10.7717/peerj.411 . PMC   4045329 . PMID   24918033.
  33. Ries, J. B.; Cohen, A. L.; McCorkle, D. C. (2009). "Marine calcifiers exhibit mixed responses to CO2-induced ocean acidification". Geology. 37 (12): 1131–1134. Bibcode:2009Geo....37.1131R. doi:10.1130/G30210A.1.
  34. Weiss, Anna; Martindale, Rowan C. (2017). "Crustose coralline algae increased framework and diversity on ancient coral reefs". PLOS ONE. 12 (8): e0181637. Bibcode:2017PLoSO..1281637W. doi: 10.1371/journal.pone.0181637 . PMC   5544230 . PMID   28783733.

Other references