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Algae
Organisms that perform oxygenic photosynthesis, except land plants
Marine algae growing on the sea bed in shallow waters
Freshwater microscopic unicellular and colonial algae
Traditional algal divisions[1][2]
ProkaryoticCyanobacteria
Eukaryotic (primary endosymbiosis)Glaucophyta, Rhodophyta, Prasinodermophyta, Chlorophyta, Charophyta*
Eukaryotic (secondary endosymbiosis)Chlorarachniophyta, Chromeridophyta, Cryptophyta, Dinoflagellata, Euglenophyta (partially), Haptophyta, Heterokontophyta
*paraphyletic, it excludes land plants
Diversity
Living50,605 species
Fossil10,556 species

Algae (/ˈæl/ AL-jee,[3] UK also /ˈælɡ/ AL-ghee; sg.: alga /ˈælɡə/ AL-gə) is an informal term for any organisms of a large and diverse group of photosynthetic organisms that are not land plants, and includes species from multiple distinct clades. Such organisms range from unicellular microalgae, such as cyanobacteria,[a] Chlorella, and diatoms, to multicellular macroalgae such as kelp or brown algae which may grow up to 50 metres (160 ft) in length. Most algae are aquatic organisms and lack many of the distinct cell and tissue types, such as stomata, xylem, and phloem that are found in land plants. The largest and most complex marine algae are called seaweeds. In contrast, the most complex freshwater forms are the Charophyta, a division of green algae which includes, for example, Spirogyra and stoneworts. Algae that are carried passively by water are plankton, specifically phytoplankton.

Algae constitute a polyphyletic group[4] because they do not include a common ancestor, and although eukaryotic algae with chlorophyll-bearing plastids seem to have a single origin (from symbiogenesis with cyanobacteria),[5] they were acquired in different ways. Green algae are a prominent example of algae that have primary chloroplasts derived from endosymbiont cyanobacteria. Diatoms and brown algae are examples of algae with secondary chloroplasts derived from endosymbiotic red algae, which they acquired via phagocytosis.[6] Algae exhibit a wide range of reproductive strategies, from simple asexual cell division to complex forms of sexual reproduction via spores.[7]

Algae lack the various structures that characterize plants (which evolved from freshwater green algae), such as the phyllids (leaf-like structures) and rhizoids of bryophytes (non-vascular plants), and the roots, leaves and other xylemic/phloemic organs found in tracheophytes (vascular plants). Most algae are autotrophic, although some are mixotrophic, deriving energy both from photosynthesis and uptake of organic carbon either by osmotrophy, myzotrophy or phagotrophy. Some unicellular species of green algae, many golden algae, euglenids, dinoflagellates, and other algae have become heterotrophs (also called colorless or apochlorotic algae), sometimes parasitic, relying entirely on external energy sources and have limited or no photosynthetic apparatus.[8][9][10] Some other heterotrophic organisms, such as the apicomplexans, are also derived from cells whose ancestors possessed chlorophyllic plastids, but are not traditionally considered as algae. Algae have photosynthetic machinery ultimately derived from cyanobacteria that produce oxygen as a byproduct of splitting water molecules, unlike other organisms that conduct anoxygenic photosynthesis such as purple and green sulfur bacteria. Fossilized filamentous algae from the Vindhya basin have been dated to 1.6 to 1.7 billion years ago.[11]

Because of the wide range of types of algae, there is a correspondingly wide range of industrial and traditional applications in human society. Traditional seaweed farming practices have existed for thousands of years and have strong traditions in East Asian food cultures. More modern algaculture applications extend the food traditions for other applications, including cattle feed, using algae for bioremediation or pollution control, transforming sunlight into algae fuels or other chemicals used in industrial processes, and in medical and scientific applications. A 2020 review found that these applications of algae could play an important role in carbon sequestration to mitigate climate change while providing lucrative value-added products for global economies.[12]

Etymology and study

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The singular alga is the Latin word for 'seaweed' and retains that meaning in English.[13] The etymology is obscure. Although some speculate that it is related to Latin algēre, 'be cold',[14] no reason is known to associate seaweed with temperature. A more likely source is alliga, 'binding, entwining'.[15]

The Ancient Greek word for 'seaweed' was φῦκος (phŷkos), which could mean either the seaweed (probably red algae) or a red dye derived from it. The Latinization, fūcus, meant primarily the cosmetic rouge. The etymology is uncertain, but a strong candidate has long been some word related to the Biblical פוך (pūk), 'paint' (if not that word itself), a cosmetic eye-shadow used by the ancient Egyptians and other inhabitants of the eastern Mediterranean. It could be any color: black, red, green, or blue.[16]

The study of algae is most commonly called phycology (from Greek phykos 'seaweed'); the term algology is falling out of use.[17]

Description

[edit]
False-color scanning electron micrograph of the unicellular coccolithophore Gephyrocapsa oceanica

The algae are a heterogeneous group of mostly photosynthetic organisms that produce oxygen and lack the reproductive features and structural complexity of land plants. This concept includes the cyanobacteria, which are prokaryotes, and all photosynthetic protists, which are eukaryotes. They contain chlorophyll a as their primary photosynthetic pigment, and generally inhabit aquatic environments.[18][19]

However, there are many exceptions to this definition. Many non-photosynthetic protists are included in the study of algae, such as the heterotrophic relatives of euglenophytes[19] or the numerous species of colorless algae that have lost their chlorophyll during evolution (e.g., Prototheca). Some exceptional species of algae tolerate dry terrestrial habitats, such as soil, rocks, or caves hidden from light sources, although they still need enough moisture to become active.[19]

Morphology

[edit]
The kelp forest exhibit at the Monterey Bay Aquarium: A three-dimensional, multicellular thallus

A range of algal morphologies is exhibited, and convergence of features in unrelated groups is common. The only groups to exhibit three-dimensional multicellular thalli are the reds and browns, and some chlorophytes.[20] Apical growth is constrained to subsets of these groups: the florideophyte reds, various browns, and the charophytes.[20] The form of charophytes is quite different from those of reds and browns, because they have distinct nodes, separated by internode 'stems'; whorls of branches reminiscent of the horsetails occur at the nodes.[20] Conceptacles are another polyphyletic trait; they appear in the coralline algae and the Hildenbrandiales, as well as the browns.[20]

Most of the simpler algae are unicellular flagellates or amoeboids, but colonial and nonmotile forms have developed independently among several of the groups. Some of the more common organizational levels, more than one of which may occur in the lifecycle of a species, are

  • Colonial: small, regular groups of motile cells
  • Capsoid: individual non-motile cells embedded in mucilage
  • Coccoid: individual non-motile cells with cell walls
  • Palmelloid: nonmotile cells embedded in mucilage
  • Filamentous: a string of connected nonmotile cells, sometimes branching
  • Parenchymatous: cells forming a thallus with partial differentiation of tissues

In three lines, even higher levels of organization have been reached, with full tissue differentiation. These are the brown algae,[21]—some of which may reach 50 m in length (kelps)[22]—the red algae,[23] and the green algae.[24] The most complex forms are found among the charophyte algae (see Charales and Charophyta), in a lineage that eventually led to the higher land plants. The innovation that defines these nonalgal plants is the presence of female reproductive organs with protective cell layers that protect the zygote and developing embryo. Hence, the land plants are referred to as the Embryophytes.

Turfs

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The term algal turf is commonly used but poorly defined. Algal turfs are thick, carpet-like beds of seaweed that retain sediment and compete with foundation species like corals and kelps, and they are usually less than 15 cm tall. Such a turf may consist of one or more species, and will generally cover an area in the order of a square metre or more. Some common characteristics are listed:[25]

  • Algae that form aggregations that have been described as turfs include diatoms, cyanobacteria, chlorophytes, phaeophytes and rhodophytes. Turfs are often composed of numerous species at a wide range of spatial scales, but monospecific turfs are frequently reported.[25]
  • Turfs can be morphologically highly variable over geographic scales and even within species on local scales and can be difficult to identify in terms of the constituent species.[25]
  • Turfs have been defined as short algae, but this has been used to describe height ranges from less than 0.5 cm to more than 10 cm. In some regions, the descriptions approached heights which might be described as canopies (20 to 30 cm).[25]

Physiology

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Many algae, particularly species of the Characeae,[26] have served as model experimental organisms to understand the mechanisms of the water permeability of membranes, osmoregulation, salt tolerance, cytoplasmic streaming, and the generation of action potentials. Plant hormones are found not only in higher plants, but in algae, too.[27]

Life cycle

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Rhodophyta, Chlorophyta, and Heterokontophyta, the three main algal divisions, have life cycles which show considerable variation and complexity. In general, an asexual phase exists where the seaweed's cells are diploid, a sexual phase where the cells are haploid, followed by fusion of the male and female gametes. Asexual reproduction permits efficient population increases, but less variation is possible. Commonly, in sexual reproduction of unicellular and colonial algae, two specialized, sexually compatible, haploid gametes make physical contact and fuse to form a zygote. To ensure a successful mating, the development and release of gametes is highly synchronized and regulated; pheromones may play a key role in these processes.[28] Sexual reproduction allows for more variation and provides the benefit of efficient recombinational repair of DNA damages during meiosis, a key stage of the sexual cycle.[29] However, sexual reproduction is more costly than asexual reproduction.[30] Meiosis has been shown to occur in many different species of algae.[31]

Diversity

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The most recent estimate (as of January 2024) documents 50,605 living and 10,556 fossil algal species, according to the online database AlgaeBase.[b] They are classified into 15 phyla or divisions. Some phyla are not photosynthetic, namely Picozoa and Rhodelphidia, but they are included in the database due to their close relationship with red algae.[1][35]

phylum (division) described
genera
described species
living fossil total
"Charophyta" (Streptophyta without land plants) 236 4,940 704 5,644
Chlorarachniophyta 10[b] 16[b] 0 16[b]
Chlorophyta 1,513 6,851 1,083 7,934
Chromeridophyta 6 8 0 8
Cryptophyta 44 245 0 245
Cyanobacteria 866 4,669 1,054 5,723
Dinoflagellata (Dinophyta) 710 2,956 955 3,911
Euglenophyta (not all species are algae) 164 2,037 20 2,057
Glaucophyta 8 25 0 25
Haptophyta 391 517 1205 1,722
Heterokontophyta 1,781 21,052 2,262 23,314
Picozoa (Picobiliphyta) 1 1 0 1
Prasinodermophyta 5 10 0 10
Rhodelphidia 1 2 0 2
Rhodophyta 1,094 7,276 278 7,554
Incertae sedis fossils 887 0 2,995 2,995
Total 7,717 50,605 10,556 61,161

The various algal phyla can be differentiated according to several biological traits. They have distinct morphologies, photosynthetic pigmentation, storage products, cell wall composition,[19] and mechanisms of carbon concentration.[36] Some phyla have unique cellular structures.[19]

Prokaryotic algae

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Macro- and microscopic photographs of Nostoc, the most common genus of cyanobacteria.[37]

Among prokaryotes, five major groups of bacteria have evolved the ability to photosynthesize, including heliobacteria, green sulfur and nonsulfur bacteria and proteobacteria.[38] However, the only lineage where oxygenic photosynthesis has evolved is in the cyanobacteria,[39] named for their blue-green (cyan) coloration and often known as blue-green algae.[40] They are classified as the phylum Cyanobacteriota or Cyanophyta. However, this phylum also includes two classes of non-photosynthetic bacteria: Melainabacteria[41] (also called Vampirovibrionia[42] or Vampirovibrionophyceae)[43] and Sericytochromatia[44] (also known as Blackallbacteria).[45] A third class contains the photosynthetic ones, known as Cyanophyceae[43] (also called Cyanobacteriia[42] or Oxyphotobacteria).[44]

As bacteria, their cells lack membrane-bound organelles, with the exception of thylakoids. Like other algae, cyanobacteria have chlorophyll a as their primary photosynthetic pigment. Their accessory pigments include phycobilins (phycoerythrobilin and phycocyanobilin), carotenoids and, in some cases, b, d, or f chlorophylls, generally distributed in phycobilisomes found in the surface of thylakoids. They display a variety of body forms, such as single cells, colonies, and unbranched or branched filaments. Their cells are commonly covered in a sheath of mucilage, and they also have a typical gram-negative bacterial cell wall composed largely of peptidoglycan. They have various storage particles, including cyanophycin as aminoacid and nitrogen reserves, "cyanophycean starch" (similar to plant amylose) for carbohydrates, and lipid droplets. Their Rubisco enzymes are concentrated in carboxysomes. They occupy a diverse array of aquatic and terrestrial habitats, including extreme environments from hot springs to polar glaciers. Some are subterranean, living via hydrogen-based lithoautotrophy instead of photosynthesis.[40]

Three lineages of cyanobacteria, Prochloraceae, Prochlorothrix and Prochlorococcus, independently evolved to have chlorophylls a and b instead of phycobilisomes. Due to their different pigmentation, they were historically grouped in a separate division, Prochlorophyta, as this is the typical pigmentation seen in green algae (e.g., chlorophytes). Eventually, this classification became obsolete, as it is a polyphyletic grouping.[46][47]

Cyanobacteria are included as algae by most phycological sources[18][19][1] and by the International Code of Nomenclature for algae, fungi, and plants,[48] although a few authors exclude them from the definition of algae and reserve the term for eukaryotes only.[4][49]

Eukaryotic algae

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Eukaryotic algae contain chloroplasts that are similar in structure to cyanobacteria. Chloroplasts contain circular DNA like that in cyanobacteria and are interpreted as representing reduced endosymbiotic cyanobacteria. However, the exact origin of the chloroplasts is different among separate lineages of algae, reflecting their acquisition during different endosymbiotic events. Many groups contain some members that are no longer photosynthetic. Some retain plastids, but not chloroplasts, while others have lost plastids entirely.[50]

Primary algae

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These algae, grouped in the clade Archaeplastida (meaning 'ancient plastid'), have "primary chloroplasts", i.e. the chloroplasts are surrounded by two membranes and probably developed through a single endosymbiotic event with a cyanobacterium. The chloroplasts of red algae have chlorophylls a and c (often), and phycobilins, while those of green algae have chloroplasts with chlorophyll a and b without phycobilins. Land plants are pigmented similarly to green algae and probably developed from them, thus the Chlorophyta is a sister taxon to the plants; sometimes the Chlorophyta, the Charophyta, and land plants are grouped together as the Viridiplantae.[citation needed]

There is also a minor group of algae with primary plastids of different origin than the chloroplasts of the archaeplastid algae. The photosynthetic plastid of three species of the genus Paulinella (RhizariaCercozoaEuglyphida), often referred to as a 'cyanelle', was originated in the endosymbiosis of a α-cyanobacterium (probably an ancestral member of Chroococcales).[51][52]

Secondary algae

[edit]

These algae appeared independently in various distantly related lineages after acquiring a chloroplast derived from another eukaryotic alga. Two lineages of secondary algae, chlorarachniophytes and euglenophytes have "green" chloroplasts containing chlorophylls a and b.[53] Their chloroplasts are surrounded by four and three membranes, respectively, and were probably retained from ingested green algae.[54][55][56]

  • Chlorarachniophytes, which belong to the phylum Cercozoa, contain a small nucleomorph, which is a relict of the algae's nucleus.[57]
  • Euglenophytes, which belong to the phylum Euglenozoa, live primarily in fresh water and have chloroplasts with only three membranes. The endosymbiotic green algae may have been acquired through myzocytosis rather than phagocytosis.[58]
  • Another group with green algae endosymbionts is the dinoflagellate genus Lepidodinium, which has replaced its original endosymbiont of red algal origin with one of green algal origin. A nucleomorph is present, and the host genome still have several red algal genes acquired through endosymbiotic gene transfer. Also, the euglenid and chlorarachniophyte genome contain genes of apparent red algal ancestry.[59][60][61]

Other groups have "red" chloroplasts containing chlorophylls a and c, and phycobilins. The shape can vary; they may be of discoid, plate-like, reticulate, cup-shaped, spiral, or ribbon shaped. They have one or more pyrenoids to preserve protein and starch. The latter chlorophyll type is not known from any prokaryotes or primary chloroplasts, but genetic similarities with red algae suggest a relationship there.[62] In some of these groups, the chloroplast has four membranes, retaining a nucleomorph in cryptomonads, and they likely share a common pigmented ancestor, although other evidence casts doubt on whether the heterokonts, Haptophyta, and cryptomonads are in fact more closely related to each other than to other groups.[63][64]

The typical dinoflagellate chloroplast has three membranes, but considerable diversity exists in chloroplasts within the group, and a number of endosymbiotic events apparently occurred.[5] The Apicomplexa, a group of closely related parasites, also have plastids called apicoplasts, which are not photosynthetic.[5] The Chromerida are the closest relatives of apicomplexans, and some have retained their chloroplasts.[65] The three alveolate groups evolved from a common myzozoan ancestor that obtained chloroplasts.[66]

History of classification

[edit]
Title page of Gmelin's Historia Fucorum, dated 1768

Linnaeus, in Species Plantarum (1753),[67] the starting point for modern botanical nomenclature, recognized 14 genera of algae, of which only four are currently considered among algae.[68] In Systema Naturae, Linnaeus described the genera Volvox and Corallina, and a species of Acetabularia (as Madrepora), among the animals.

In 1768, Samuel Gottlieb Gmelin (1744–1774) published the Historia Fucorum, the first work dedicated to marine algae and the first book on marine biology to use the then new binomial nomenclature of Linnaeus. It included elaborate illustrations of seaweed and marine algae on folded leaves.[69][70]

W. H. Harvey (1811–1866) and Lamouroux (1813)[71] were the first to divide macroscopic algae into four divisions based on their pigmentation. This is the first use of a biochemical criterion in plant systematics. Harvey's four divisions are: red algae (Rhodospermae), brown algae (Melanospermae), green algae (Chlorospermae), and Diatomaceae.[72][73]

At this time, microscopic algae were discovered and reported by a different group of workers (e.g., O. F. Müller and Ehrenberg) studying the Infusoria (microscopic organisms). Unlike macroalgae, which were clearly viewed as plants, microalgae were frequently considered animals because they are often motile.[71] Even the nonmotile (coccoid) microalgae were sometimes merely seen as stages of the lifecycle of plants, macroalgae, or animals.[74][75]

Although used as a taxonomic category in some pre-Darwinian classifications, e.g., Linnaeus (1753),[76] de Jussieu (1789),[77] Lamouroux (1813), Harvey (1836), Horaninow (1843), Agassiz (1859), Wilson & Cassin (1864),[76] in further classifications, the "algae" are seen as an artificial, polyphyletic group.[78]

Throughout the 20th century, most classifications treated the following groups as divisions or classes of algae: cyanophytes, rhodophytes, chrysophytes, xanthophytes, bacillariophytes, phaeophytes, pyrrhophytes (cryptophytes and dinophytes), euglenophytes, and chlorophytes. Later, many new groups were discovered (e.g., Bolidophyceae), and others were splintered from older groups: charophytes and glaucophytes (from chlorophytes), many heterokontophytes (e.g., synurophytes from chrysophytes, or eustigmatophytes from xanthophytes), haptophytes (from chrysophytes), and chlorarachniophytes (from xanthophytes).[79]

With the abandonment of plant-animal dichotomous classification, most groups of algae (sometimes all) were included in Protista, later also abandoned in favour of Eukaryota. However, as a legacy of the older plant life scheme, some groups that were also treated as protozoans in the past still have duplicated classifications (see ambiregnal protists).[80]

Some parasitic algae (e.g., the green algae Prototheca and Helicosporidium, parasites of metazoans, or Cephaleuros, parasites of plants) were originally classified as fungi, sporozoans, or protistans of incertae sedis,[81] while others (e.g., the green algae Phyllosiphon and Rhodochytrium, parasites of plants, or the red algae Pterocladiophila and Gelidiocolax mammillatus, parasites of other red algae, or the dinoflagellates Oodinium, parasites of fish) had their relationship with algae conjectured early. In other cases, some groups were originally characterized as parasitic algae (e.g., Chlorochytrium), but later were seen as endophytic algae.[82] Some filamentous bacteria (e.g., Beggiatoa) were originally seen as algae. Furthermore, groups like the apicomplexans are also parasites derived from ancestors that possessed plastids, but are not included in any group traditionally seen as algae.[83][84]

Evolution

[edit]

Origin of oxygenic photosynthesis

[edit]

Prokaryotic algae, i.e., cyanobacteria, are the only group of organisms where oxygenic photosynthesis has evolved. The oldest undisputed fossil evidence of cyanobacteria is dated at 2100 million years ago,[85] although stromatolites, associated with cyanobacterial biofilms, appear as early as 3500 million years ago in the fossil record.[86]

First endosymbiosis

[edit]

Eukaryotic algae are polyphyletic thus their origin cannot be traced back to single hypothetical common ancestor. It is thought that they came into existence when photosynthetic coccoid cyanobacteria got phagocytized by a unicellular heterotrophic eukaryote (a protist),[87] giving rise to double-membranous primary plastids. Such symbiogenic events (primary symbiogenesis) are believed to have occurred more than 1.5 billion years ago during the Calymmian period, early in Boring Billion, but it is difficult to track the key events because of so much time gap.[88] Primary symbiogenesis gave rise to three divisions of archaeplastids, namely the Viridiplantae (green algae and later plants), Rhodophyta (red algae) and Glaucophyta ("grey algae"), whose plastids further spread into other protist lineages through eukaryote-eukaryote predation, engulfments and subsequent endosymbioses (secondary and tertiary symbiogenesis).[88] This process of serial cell "capture" and "enslavement" explains the diversity of photosynthetic eukaryotes.[87] The oldest undisputed fossil evidence of eukaryotic algae is Bangiomorpha pubescens, a red alga found in rocks around 1047 million years old.[89][90]

Consecutive endosymbioses

[edit]
Plastid acquisitions across eukaryotes, shown in discontinuous arrows: blue for the primary plastids derived directly from a cyanobacterium, and red and green for the secondary plastids derived from red algae and green algae, respectively. Red arrows are placed according to the 2024 hypothesis;[91] disagreements with previous hypotheses are marked '?'.[92]

Recent genomic and phylogenomic approaches have significantly clarified plastid genome evolution, the horizontal movement of endosymbiont genes to the "host" nuclear genome, and plastid spread throughout the eukaryotic tree of life.[87] It is accepted that both euglenophytes and chlorarachniophytes obtained their chloroplasts from chlorophytes that became endosymbionts.[93] In particular, euglenophyte chloroplasts share the most resemblance with the genus Pyramimonas.[94]

However, there is still no clear order in which the secondary and tertiary endosymbioses occurred for the "chromist" lineages (ochrophytes, cryptophytes, haptophytes and myzozoans).[95] Two main models have been proposed to explain the order, both of which agree that cryptophytes obtained their chloroplasts from red algae. One model, hypothesized in 2014 by John W. Stiller and coauthors,[96] suggests that a cryptophyte became the plastid of ochrophytes, which in turn became the plastid of myzozoans and haptophytes. The other model, suggested by Andrzej Bodył and coauthors in 2009,[97] describes that a cryptophyte became the plastid of both haptophytes and ochrophytes, and it is a haptophyte that became the plastid of myzozoans instead.[92] In 2024, a third model by Filip Pietluch and coauthors proposed that there were two independent endosymbioses with red algae: one that originated the cryptophyte plastids (as in the previous models), and subsequently the haptophyte plastids; and another that originated the ochrophyte plastids, where the myzozoans obtained theirs.[91]

Relationship to land plants

[edit]

Fossils of isolated spores suggest land plants may have been around as long as 475 million years ago (mya) during the Late Cambrian/Early Ordovician period,[98][99] from sessile shallow freshwater charophyte algae much like Chara,[100] which likely got stranded ashore when riverine/lacustrine water levels dropped during dry seasons.[101] These charophyte algae probably already developed filamentous thalli and holdfasts that superficially resembled plant stems and roots, and probably had an isomorphic alternation of generations. They perhaps evolved some 850 mya[102] and might even be as early as 1 Gya during the late phase of the Boring Billion.[103]

Distribution

[edit]

The distribution of algal species has been fairly well studied since the founding of phytogeography in the mid-19th century.[104] Algae spread mainly by the dispersal of spores analogously to the dispersal of cryptogamic plants by spores. Spores can be found in a variety of environments: fresh and marine waters, air, soil, and in or on other organisms.[104] Whether a spore is to grow into an adult organism depends on the species and the environmental conditions where the spore lands.

The spores of freshwater algae are dispersed mainly by running water and wind, as well as by living carriers.[104] However, not all bodies of water can carry all species of algae, as the chemical composition of certain water bodies limits the algae that can survive within them.[104] Marine spores are often spread by ocean currents. Ocean water presents many vastly different habitats based on temperature and nutrient availability, resulting in phytogeographic zones, regions, and provinces.[105]

To some degree, the distribution of algae is subject to floristic discontinuities caused by geographical features, such as Antarctica, long distances of ocean or general land masses. It is, therefore, possible to identify species occurring by locality, such as "Pacific algae" or "North Sea algae". When they occur out of their localities, hypothesizing a transport mechanism is usually possible, such as the hulls of ships. For example, Ulva reticulata and U. fasciata travelled from the mainland to Hawaii in this manner.

Mapping is possible for select species only: "there are many valid examples of confined distribution patterns."[106] For example, Clathromorphum is an arctic genus and is not mapped far south of there.[where?][107] However, scientists regard the overall data as insufficient due to the "difficulties of undertaking such studies."[108]

Regional algae checklists

[edit]
Algae on coastal rocks at Shihtiping in Taiwan

The Algal Collection of the US National Herbarium (located in the National Museum of Natural History) consists of approximately 320,500 dried specimens, which, although not exhaustive (no exhaustive collection exists), gives an idea of the order of magnitude of the number of algal species (that number remains unknown).[109] Estimates vary widely. For example, according to one standard textbook,[110] in the British Isles, the UK Biodiversity Steering Group Report estimated there to be 20,000 algal species in the UK. Another checklist reports only about 5,000 species. Regarding the difference of about 15,000 species, the text concludes: "It will require many detailed field surveys before it is possible to provide a reliable estimate of the total number of species ..."

Regional and group estimates have been made, as well:

  • 5,000–5,500 species of red algae worldwide[citation needed]
  • "some 1,300 in Australian Seas"[111]
  • 400 seaweed species for the western coastline of South Africa,[112] and 212 species from the coast of KwaZulu-Natal.[113] Some of these are duplicates, as the range extends across both coasts, and the total recorded is probably about 500 species. Most of these are listed in List of seaweeds of South Africa. These exclude phytoplankton and crustose corallines.
  • 669 marine species from California (US)[114]
  • 642 in the check-list of Britain and Ireland[115]

and so on, but lacking any scientific basis or reliable sources, these numbers have no more credibility than the British ones mentioned above. Most estimates also omit microscopic algae, such as phytoplankton.[citation needed]

Ecology

[edit]
Phytoplankton, Lake Chūzenji

Algae are prominent in bodies of water, common in terrestrial environments, and are found in unusual environments, such as on snow and ice. Seaweeds grow mostly in shallow marine waters, less than100 m (330 ft) deep; however, some such as Navicula pennata have been recorded to a depth of 360 m (1,180 ft).[116] A type of algae, Ancylonema nordenskioeldii, was found in Greenland in areas known as the 'Dark Zone', which caused an increase in the rate of melting ice sheet.[117] The same algae was found in the Italian Alps, after pink ice appeared on parts of the Presena glacier.[118]

The various sorts of algae play significant roles in aquatic ecology. Microscopic forms that live suspended in the water column (phytoplankton) provide the food base for most marine food chains. In very high densities (algal blooms), these algae may discolor the water and outcompete, poison, or asphyxiate other life forms.[119]

Algae can be used as indicator organisms to monitor pollution in various aquatic systems.[120] In many cases, algal metabolism is sensitive to various pollutants. Due to this, the species composition of algal populations may shift in the presence of chemical pollutants.[120] To detect these changes, algae can be sampled from the environment and maintained in laboratories with relative ease.[120]

On the basis of their habitat, algae can be categorized as: aquatic (planktonic, benthic, marine, freshwater, lentic, lotic),[121] terrestrial, aerial (subaerial),[122] lithophytic, halophytic (or euryhaline), psammon, thermophilic, cryophilic, epibiont (epiphytic, epizoic), endosymbiont (endophytic, endozoic), parasitic, calcifilic or lichenic (phycobiont).[123]

Symbiotic algae

[edit]

Some species of algae form symbiotic relationships with other organisms. In these symbioses, the algae supply photosynthates (organic substances) to the host organism providing protection to the algal cells. The host organism derives some or all of its energy requirements from the algae.[citation needed] Examples are:

Lichens

[edit]
Rock lichens in Ireland

Lichens are defined by the International Association for Lichenology to be "an association of a fungus and a photosynthetic symbiont resulting in a stable vegetative body having a specific structure".[124] The fungi, or mycobionts, are mainly from the Ascomycota with a few from the Basidiomycota. In nature, they do not occur separate from lichens. It is unknown when they began to associate.[125] One or more[126] mycobiont associates with the same phycobiont species, from the green algae, except that alternatively, the mycobiont may associate with a species of cyanobacteria (hence "photobiont" is the more accurate term). A photobiont may be associated with many different mycobionts or may live independently; accordingly, lichens are named and classified as fungal species.[127] The association is termed a morphogenesis because the lichen has a form and capabilities not possessed by the symbiont species alone (they can be experimentally isolated). The photobiont possibly triggers otherwise latent genes in the mycobiont.[128]

Trentepohlia is an example of a common green alga genus worldwide that can grow on its own or be lichenised. Lichen thus share some of the habitat and often similar appearance with specialized species of algae (aerophytes) growing on exposed surfaces such as tree trunks and rocks and sometimes discoloring them.[citation needed]

Animal symbioses

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Floridian coral reef

Coral reefs are accumulated from the calcareous exoskeletons of marine invertebrates of the order Scleractinia (stony corals). These animals metabolize sugar and oxygen to obtain energy for their cell-building processes, including secretion of the exoskeleton, with water and carbon dioxide as byproducts. Dinoflagellates (algal protists) are often endosymbionts in the cells of the coral-forming marine invertebrates, where they accelerate host-cell metabolism by generating sugar and oxygen immediately available through photosynthesis using incident light and the carbon dioxide produced by the host. Reef-building stony corals (hermatypic corals) require endosymbiotic algae from the genus Symbiodinium to be in a healthy condition.[129] The loss of Symbiodinium from the host is known as coral bleaching, a condition which leads to the deterioration of a reef.

Endosymbiontic green algae live close to the surface of some sponges, for example, breadcrumb sponges (Halichondria panicea). The alga is thus protected from predators; the sponge is provided with oxygen and sugars which can account for 50 to 80% of sponge growth in some species.[130]

In human culture

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In classical Chinese, the word is used both for "algae" and (in the modest tradition of the imperial scholars) for "literary talent". The third island in Kunming Lake beside the Summer Palace in Beijing is known as the Zaojian Tang Dao (藻鑒堂島), which thus simultaneously means "Island of the Algae-Viewing Hall" and "Island of the Hall for Reflecting on Literary Talent".[citation needed]

Cultivation

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A seaweed farm in Uroa, Zanzibar
Algaculture in Kibbutz Ketura, Israel

Algaculture is a form of aquaculture involving the farming of species of algae.[131]

The majority of algae that are intentionally cultivated fall into the category of microalgae (also referred to as phytoplankton, microphytes, or planktonic algae). Macroalgae, commonly known as seaweed, also have many commercial and industrial uses, but due to their size and the specific requirements of the environment in which they need to grow, they do not lend themselves as readily to cultivation (this may change, however, with the advent of newer seaweed cultivators, which are basically algae scrubbers using upflowing air bubbles in small containers, known as tumble culture).[132]

Commercial and industrial algae cultivation has numerous uses, including production of nutraceuticals such as omega-3 fatty acids (as algal oil)[133][134][135] or natural food colorants and dyes, food, fertilizers, bioplastics, chemical feedstock (raw material), protein-rich animal/aquaculture feed, pharmaceuticals, and algal fuel,[136] and can also be used as a means of pollution control and natural carbon sequestration.[137]

Global production of farmed aquatic plants, overwhelmingly dominated by seaweeds, grew in output volume from 13.5 million tonnes in 1995, to just over 30 million tonnes in 2016 and 37.8 million tonnes in 2022.[138][139] This increase was the result of production expansions led by China, followed by Malaysia, the Philippines, the United Republic of Tanzania, and the Russian Federation.[138]

Cultured microalgae already contribute to a wide range of sectors in the emerging bioeconomy.[140] Research suggests there are large potentials and benefits of algaculture for the development of a future healthy and sustainable food system.[141][137]

Seaweed farming

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Underwater Eucheuma farming in the Philippines
A seaweed farmer stands in shallow water, gathering edible seaweed that has grown on a rope
A seaweed farmer in Nusa Lembongan (Indonesia) gathers edible seaweed that has grown on a rope.

Seaweed farming or kelp farming is the practice of cultivating and harvesting seaweed. In its simplest form farmers gather from natural beds, while at the other extreme farmers fully control the crop's life cycle.

The seven most cultivated taxa are Eucheuma spp., Kappaphycus alvarezii, Gracilaria spp., Saccharina japonica, Undaria pinnatifida, Pyropia spp., and Sargassum fusiforme. Eucheuma and K. alvarezii are attractive for carrageenan (a gelling agent); Gracilaria is farmed for agar; the rest are eaten after limited processing.[142] Seaweeds are different from mangroves and seagrasses, as they are photosynthetic algal organisms[143] and are non-flowering.[142]

The largest seaweed-producing countries as of 2022 are China (58.62%) and Indonesia (28.6%); followed by South Korea (5.09%) and the Philippines (4.19%). Other notable producers include North Korea (1.6%), Japan (1.15%), Malaysia (0.53%), Zanzibar (Tanzania, 0.5%), and Chile (0.3%).[144][145] Seaweed farming has frequently been developed to improve economic conditions and to reduce fishing pressure.[146]

The Food and Agriculture Organization (FAO) reported that world production in 2019 was over 35 million tonnes. North America produced some 23,000 tonnes of wet seaweed. Alaska, Maine, France, and Norway each more than doubled their seaweed production since 2018. As of 2019, seaweed represented 30% of marine aquaculture.[147] In 2023, the global seaweed extract market was valued at $16.5 billion, with strong projected growth.[148]

Seaweed farming is a carbon negative crop, with a high potential for climate change mitigation.[149][150] The IPCC Special Report on the Ocean and Cryosphere in a Changing Climate recommends "further research attention" as a mitigation tactic.[151] World Wildlife Fund, Oceans 2050, and The Nature Conservancy publicly support expanded seaweed cultivation.[147]

Bioreactors

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A close up of microalgae – Pavlova sp.
An algae bioreactor is used for cultivating micro or macroalgae. Algae may be cultivated for the purposes of biomass production (as in a seaweed cultivator), wastewater treatment, CO2 fixation, or aquarium/pond filtration in the form of an algae scrubber.[152] Algae bioreactors vary widely in design, falling broadly into two categories: open reactors and enclosed reactors. Open reactors are exposed to the atmosphere while enclosed reactors, also commonly called photobioreactors, are isolated to varying extents from the atmosphere. Specifically, algae bioreactors can be used to produce fuels such as biodiesel and bioethanol, to generate animal feed, or to reduce pollutants such as NOx and CO2 in flue gases of power plants. Fundamentally, this kind of bioreactor is based on the photosynthetic reaction, which is performed by the chlorophyll-containing algae itself using dissolved carbon dioxide and sunlight. The carbon dioxide is dispersed into the reactor fluid to make it accessible to the algae. The bioreactor has to be made out of transparent material.

Uses

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Harvesting algae

Biofuel

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To be competitive and independent from fluctuating support from (local) policy on the long run, biofuels should equal or beat the cost level of fossil fuels. Here, algae-based fuels hold great promise,[153][154] directly related to the potential to produce more biomass per unit area in a year than any other form of biomass. The break-even point for algae-based biofuels is estimated to occur by 2025.[155]

Fertilizer

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Seaweed-fertilized gardens on Inisheer

For centuries, seaweed has been used as a fertilizer; George Owen of Henllys writing in the 16th century referring to drift weed in South Wales:[156]

This kind of ore they often gather and lay on great heapes, where it heteth and rotteth, and will have a strong and loathsome smell; when being so rotten they cast on the land, as they do their muck, and thereof springeth good corn, especially barley ... After spring-tydes or great rigs of the sea, they fetch it in sacks on horse backes, and carie the same three, four, or five miles, and cast it on the lande, which doth very much better the ground for corn and grass.

Today, algae are used by humans in many ways; for example, as fertilizers, soil conditioners, and livestock feed.[157] Aquatic and microscopic species are cultured in clear tanks or ponds and are either harvested or used to treat effluents pumped through the ponds. Algaculture on a large scale is an important type of aquaculture in some places. Maerl is commonly used as a soil conditioner.[158]

Food industry

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Dulse, a type of edible seaweed

Algae are used as foods in many countries: China consumes more than 70 species, including fat choy, a cyanobacterium considered a vegetable; Japan, over 20 species such as nori and aonori;[159] Ireland, dulse; Chile, cochayuyo.[160] Laver is used to make laverbread in Wales, where it is known as bara lawr. In Korea, green laver is used to make gim.[161]

Three forms of algae used as food:

The oils from some algae have high levels of unsaturated fatty acids. Some varieties of algae favored by vegetarianism and veganism contain the long-chain, essential omega-3 fatty acids, docosahexaenoic acid (DHA) and eicosapentaenoic acid (EPA).[165] Fish oil contains the omega-3 fatty acids, but the original source is algae (microalgae in particular), which are eaten by marine life such as copepods and are passed up the food chain.[165]

The natural pigments (carotenoids and chlorophylls) produced by algae can be used as alternatives to chemical dyes and coloring agents.[166] The presence of some individual algal pigments, together with specific pigment concentration ratios, are taxon-specific: analysis of their concentrations with various analytical methods, particularly high-performance liquid chromatography, can therefore offer deep insight into the taxonomic composition and relative abundance of natural algae populations in sea water samples.[167][168]

Carrageenan, from the red alga Chondrus crispus, is used as a stabilizer in milk products.[citation needed]

Gelling agents

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Agar, a gelatinous substance derived from red algae, has a number of commercial uses.[169] It is a good medium on which to grow bacteria and fungi, as most microorganisms cannot digest agar.[170]

Alginic acid, or alginate, is extracted from brown algae. Its uses range from gelling agents in food, to medical dressings. Alginic acid also has been used in the field of biotechnology as a biocompatible medium for cell encapsulation and cell immobilization. Molecular cuisine is also a user of the substance for its gelling properties, by which it becomes a delivery vehicle for flavours.[171]

Between 100,000 and 170,000 wet tons of Macrocystis are harvested annually in New Mexico for alginate extraction and abalone feed.[172][173]

Pollution control and bioremediation

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  • Sewage can be treated with algae,[174] reducing the use of large amounts of toxic chemicals that would otherwise be needed.
  • Algae can be used to capture fertilizers in runoff from farms. When subsequently harvested, the enriched algae can be used as fertilizer.[175]
  • Aquaria and ponds can be filtered using algae, which absorb nutrients from the water in a device called an algae scrubber, also known as an algae turf scrubber.[176][177]

Agricultural Research Service scientists found that 60–90% of nitrogen runoff and 70–100% of phosphorus runoff can be captured from manure effluents using a horizontal algae scrubber, also called an algal turf scrubber (ATS). Scientists developed the ATS, which consists of shallow, 100-foot raceways of nylon netting where algae colonies can form, and studied its efficacy for three years. They found that algae can readily be used to reduce the nutrient runoff from agricultural fields and increase the quality of water flowing into rivers, streams, and oceans. Researchers collected and dried the nutrient-rich algae from the ATS and studied its potential as an organic fertilizer. They found that cucumber and corn seedlings grew just as well using ATS organic fertilizer as they did with commercial fertilizers.[178] Algae scrubbers, using bubbling upflow or vertical waterfall versions, are now also being used to filter aquaria and ponds.[citation needed]

The alga Stichococcus bacillaris has been seen to colonize silicone resins used at archaeological sites; biodegrading the synthetic substance.[179]

Bioplastics

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Various polymers can be created from algae, which can be especially useful in the creation of bioplastics. These include hybrid plastics, cellulose-based plastics, poly-lactic acid, and bio-polyethylene.[180] Several companies have begun to produce algae polymers commercially, including for use in flip-flops[181] and in surf boards.[182] Even algae is also used to prepare various polymeric resins suitable for coating applications.[183][184][185]

Additional images

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See also

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Notes

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References

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Bibliography

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Revisions and contributorsEdit on WikipediaRead on Wikipedia
from Grokipedia

Algae comprise a polyphyletic assemblage of primarily aquatic, photosynthetic eukaryotes that perform oxygenic without the specialized vascular tissues, , stems, or leaves of embryophytes (land plants), ranging from unicellular to multicellular macroalgae including seaweeds. These organisms thrive in marine, freshwater, and damp terrestrial settings, where they function as foundational primary producers, converting into via chloroplasts containing . Oceanic algae generate roughly half of Earth's atmospheric oxygen and underpin aquatic food webs by supporting higher trophic levels through nutrient cycling and carbon fixation. Evolutionarily ancient, algae oxygenated the primordial atmosphere billions of years ago, facilitating the rise of complex aerobic life, though certain species trigger harmful blooms that deplete oxygen and release toxins, disrupting ecosystems and health. Algae also engage in symbioses, such as providing in lichens or coral reefs, and hold potential for in biofuels and remediation due to their rapid growth and metabolic versatility.

Definition and Etymology

Historical and Linguistic Origins

The term algae derives from the Latin plural algae, with singular alga signifying "seaweed" and first attested in English contexts around the mid-16th century. The precise etymology of alga is uncertain, potentially linked to Latin ulva ("grass-like or leafy seaweed") or speculatively to algēre ("to be cold"), though no causal connection to temperature explains seaweed's connotation. Classical Latin usage appears in Pliny the Elder's Naturalis Historia (c. 77 AD), where algae denotes marine plants such as phycitis algae, a type of seaweed, reflecting early descriptive rather than systematic categorization. In parallel ancient Greek literature, equivalents like phŷkos ("seaweed") occur as early as Homer's Iliad (c. 8th century BCE), often denoting marine vegetation or derived products like dyes, without formal biological grouping. Theophrastus (c. 371–287 BCE), in works like Enquiry into Plants, described marine herbaceous plants akin to modern algae among broader plant categories—trees, shrubs, and herbs—but emphasized environmental dependencies like salinity without distinct algal taxonomy. Linnaeus elevated Algae to a formal taxonomic class in Species Plantarum (1753), classifying flowerless, seedless aquatic organisms—chiefly marine seaweeds—as cryptogams within his botanical system, marking the term's adoption in systematic biology. This Linnaean framework persisted into the 18th century, influencing works like Johann Friedrich Gmelin's Historia Fucorum (1768), which detailed seaweed morphology. The English plural algae emerged scientifically by 1794, while the discipline of phycology—study of algae—stems from Greek phŷkos.

Contemporary Taxonomic Definition

In contemporary , algae are regarded as an informal, polyphyletic grouping of primarily aquatic organisms capable of oxygenic , encompassing both prokaryotic and eukaryotic lineages but excluding embryophytes (land plants), which possess protected embryos, vascular tissues, and specialized organs such as roots, stems, and leaves. This definition emphasizes functional and ecological convergence rather than shared ancestry, as algal lineages derive from multiple independent evolutionary origins, including primary endosymbiosis of in the supergroup (yielding , , and glaucophytes) and secondary or tertiary endosymbioses in diverse groups. Prokaryotic algae, specifically (formerly blue-green algae), are included due to their photosynthetic role and superficial resemblance to eukaryotic algae, though they lack nuclei and organelles; these organisms represent an ancient lineage dating back over 2.4 billion years, foundational to global oxygen production. Eukaryotic algae span at least 14 phyla across kingdoms such as Plantae, , and , with pigmentation (e.g., chlorophylls a and b in , chlorophyll c in stramenopiles) and structure serving as key diagnostic traits, but has revealed their non-monophyletic nature, rendering traditional divisions like divisions or classes artificial for cladistic purposes. Modern classifications employ a polyphasic approach integrating morphology, , biochemistry, and genomic data, recognizing algae as a pragmatic assemblage for phycological study rather than a formal ; this shift, accelerated since the 1990s with sequencing, underscores that no single unites all algae, as they are interspersed across the with non-photosynthetic relatives. For instance, (Chlorophyta and charophytes) form a paraphyletic grade sister to embryophytes within , while ochrophytes (e.g., diatoms, ) belong to the SAR , highlighting convergent adaptations to aquatic niches over deep phylogenetic divergence.

Morphology and Physiology

Cellular Structure and Morphology

Algae exhibit a wide range of cellular structures, predominantly eukaryotic, characterized by membrane-bound organelles including a nucleus enclosing linear chromosomes, chloroplasts derived from endosymbiotic , and mitochondria for respiration. Unlike cells, algal cells typically possess a external to the plasma , providing structural support and protection, with composition varying by taxonomic group to adapt to aquatic environments. Chloroplasts in most algae feature membranes stacked into grana for efficient light harvesting, surrounded by a double envelope , and contain in some species for carbon fixation enhancement. Cell wall architecture differs significantly across algal divisions: (Chlorophyta) often feature microfibrils embedded in pectin-like matrices or hydroxyproline-rich glycoproteins, enabling flexibility in unicellular and filamentous forms. In brown algae (Phaeophyceae), walls consist primarily of alginates—copolymers of mannuronic and guluronic acids—cross-linked with fucose-containing sulfated polysaccharides, contributing to the mechanical strength of large multicellular thalli up to 60 meters in species. (Rhodophyta) walls include semicrystalline fibrils interwoven with sulfated glucans, mannans, and glucomannans, often impregnated with for rigidity in coralline forms. Diatoms (Bacillariophyta) possess unique silica-based frustules—two overlapping valves formed via specialized vesicles—providing precise geometric shapes for and . Morphologically, algae span unicellular forms (e.g., with spherical cells 2–10 μm in diameter) to complex multicellular organizations, reflecting evolutionary adaptations for nutrient uptake and reproduction in aquatic niches. Unicellular types include motile flagellates like , equipped with two anterior flagella and an eyespot for phototaxis, and non-motile coccoids or amoeboids. Colonial morphologies aggregate cells into spheres (e.g., with somatic and reproductive cells) or plates, maintaining division of labor without true tissues. Filamentous algae form unbranched (e.g., ) or branched chains, while multicellular macroalgae develop differentiated structures: holdfasts for attachment, stipes for support, and blades for , as in with air bladders for flotation. These forms lack vascular tissues but achieve size through coenocytic growth or apical meristems in advanced groups, with cell sizes ranging from 1 μm in to centimeters in macroalgal blades.

Photosynthetic Processes

Algae perform oxygenic photosynthesis, utilizing water as an electron donor to generate oxygen, ATP, and NADPH through two linked photosystems, photosystem II (PSII) and photosystem I (PSI). This process mirrors that in cyanobacteria and higher plants, where light energy drives electron transport chains embedded in thylakoid membranes, ultimately reducing NADP+ and producing O2 from water oxidation at PSII. In prokaryotic algae such as cyanobacteria, thylakoids occur freely in the cytoplasm, whereas eukaryotic algae house them within chloroplasts derived from endosymbiotic events. The carbon fixation phase follows the Calvin-Benson-Bassham cycle in the stroma or cytoplasm, converting CO2 into carbohydrates. All algae contain chlorophyll a as the primary pigment, absorbing light maximally at wavelengths around 430 nm and 680 nm to initiate charge separation in reaction centers. Accessory pigments expand the spectral range: chlorophyll b in green algae enhances absorption in the 450-500 nm and 600-650 nm regions; chlorophyll c in chromalveolates like diatoms and brown algae targets blue-green light; while phycobilins in red algae and cyanobacteria capture green to orange wavelengths (500-650 nm) via phycobilisomes attached to thylakoids. These pigments funnel energy to reaction centers via light-harvesting complexes (LHCs), with green algae employing LHCII trimers similar to plants, and ochrophytes using fucoxanthin-chlorophyll a/ c proteins (FCPs) optimized for underwater light penetration. Carotenoids like beta-carotene and fucoxanthin provide photoprotection and additional light harvesting, dissipating excess energy as heat under high irradiance. Algal photosynthesis contributes approximately 50% of global , predominantly from marine , due to their vast oceanic distribution and efficient capture in low-light aquatic environments. Adaptations include state transitions regulating LHC distribution between for balanced electron flow, and mechanisms that prevent photodamage, varying by algal group—e.g., diatom FCPs exhibit rapid energy-dependent quenching. In , phycobilisomes enable complementary , adjusting pigment ratios to ambient . These processes underscore algae's role in oxygenating Earth's atmosphere since their around 2.5 billion years ago.

Metabolic and Reproductive Cycles

Algae exhibit diverse metabolic processes dominated by oxygenic , in which drives the splitting of molecules to produce oxygen, electrons for NADPH reduction, and ATP via , ultimately fixing through the Calvin-Benson-Bassham cycle in chloroplasts or thylakoids. This process supports , with algae contributing approximately 50-85% of Earth's oxygen and fixing vast amounts of carbon, though rates vary by and environmental conditions such as light intensity and CO2 availability. Many algae, including like , also perform aerobic respiration to break down carbohydrates and for under dark conditions, balancing photosynthetic gains, while some switch to anaerobic producing lactate or when oxygen is limited. Nutrient metabolism in algae involves active uptake of macronutrients like nitrogen (often as nitrate or ammonium) and phosphorus (as phosphate), which are assimilated into , nucleic acids, and phospholipids essential for growth and division. Optimal nitrogen-to-phosphorus ratios, typically around 16:1 by atoms (), maximize biomass accumulation, but deficiencies redirect metabolism toward lipid or carbohydrate storage, enhancing resilience to environmental stress. Carbon metabolism features high flux through pathways like phosphoenolpyruvate (PEP) carboxylase, exceeding rates in higher and supporting rapid protein synthesis and metabolite production. often employ CO2-concentrating mechanisms (CCMs) to enhance efficiency in low-CO2 environments, involving carbonic anhydrases and inorganic carbon transporters. Reproductive cycles in algae encompass both asexual and sexual modes, enabling to fluctuating conditions; predominates in favorable environments for rapid population growth, while promotes during stress. Asexual mechanisms include binary fission in unicellular forms like , fragmentation in filamentous species such as , and spore formation (zoospores or aplanospores) that germinate into new individuals without . involves fusion, ranging from (equal flagellated gametes in ) to oogamy (large non-motile eggs and small sperm in ), with zygotes often developing protective walls to overwinter. Algal life cycles vary across taxa: haplontic cycles feature haploid dominance with zygotic meiosis post-fertilization (e.g., many ), diplontic cycles maintain diploidy except for gametes via gametic meiosis (e.g., some ), and isomorphic or heteromorphic occurs in groups like , where haploid gametophytes alternate with diploid sporophytes producing spores via meiotic reduction. The interplay of these cycles influences , with asexual phases favoring clonal expansion and sexual phases countering inbreeding through outcrossing, though the balance shifts based on density, nutrient availability, and predation pressures. In cyanobacteria (prokaryotic algae), reproduction is strictly asexual via binary fission or formation, lacking true sexual cycles but exhibiting genetic exchange via conjugation-like processes.

Classification and Diversity

Prokaryotic Algae

Prokaryotic algae consist of the , a of photosynthetic in the domain that conduct oxygenic , splitting water to release oxygen and fix . These organisms, often called blue-green algae due to their pigmentation, represent the only prokaryotes capable of this process, distinguishing them from other and aligning them traditionally with algal groups despite their prokaryotic nature lacking nuclei and membrane-bound organelles. Cyanobacteria display morphological diversity including unicellular, colonial, and multicellular filamentous forms, with photosynthetic apparatus organized in thylakoids containing chlorophyll a and accessory phycobiliproteins for light harvesting. Many species form heterocysts, specialized cells that provide an anaerobic microenvironment for activity, enabling biological from atmospheric N₂ even in oxygen-rich settings. This capability supports their role in nutrient cycling, as heterocysts separate oxygenic from to protect the enzyme. Taxonomically, the Cyanobacteria encompasses numerous lineages, with genomic analyses revealing 18 orders and 42 families as of 2024, reflecting high genetic and functional diversity adapted to aquatic, terrestrial, and extreme environments. This diversity underpins their ecological significance as primary producers in oceans and lakes, where blooms can contribute substantially to and nitrogen inputs, though excessive growth may lead to toxic production affecting water quality. Evolutionarily, diverged from other around 3.4 billion years ago, with their oxygenic driving the circa 2.4 billion years ago, which oxygenated Earth's atmosphere and enabled aerobic life while reshaping biogeochemical cycles. evidence and molecular clocks indicate their ancient origins, with multicellularity emerging in parallel with diversification that amplified their environmental impact.

Eukaryotic Algae Groups

Eukaryotic algae form a polyphyletic group of photosynthetic protists spanning multiple eukaryotic supergroups, distinguished by plastids acquired through primary endosymbiosis in Archaeplastida or secondary/tertiary endosymbioses in other lineages such as stramenopiles and alveolates. Primary plastids, bounded by two membranes, characterize Archaeplastida, while secondary plastids typically feature three or four membranes from engulfed red or green algae. These organisms range from unicellular microalgae to complex multicellular seaweeds, contributing substantially to global primary production. The Rhodophyta, or , encompass approximately 5,000 to 6,000 species, predominantly marine and multicellular, with phycoerythrins enabling absorption of light in deeper waters. Lacking flagella in most stages and containing unstacked thylakoids, they produce like and in cell walls, supporting roles in food, industry, and calcification. Chlorophyta and Charophyta constitute the green algal lineages within Archaeplastida, with including over 4,500 described species (potentially up to 100,000 total) of unicellular to filamentous forms storing starch and featuring chlorophylls a and b akin to land plants. Charophyta, with fewer species, include conjugating algae and charophytes, the sister group to embryophytes, exhibiting oogamous reproduction and phragmoplasts. These groups inhabit freshwater, marine, and terrestrial environments, with some forming symbiotic lichens. Stramenopile algae, part of the Heterokontophyta, feature secondary plastids from and include Phaeophyceae () with about 1,500 to 2,000 species of large, multicellular marine forms pigmented by and storing ; notable examples are (Laminariales) forming underwater forests up to 50 meters tall. Bacillariophyta (diatoms), exceeding 20,000 described species, possess silica-impregnated frustules for structural support, dominate , and undergo auxospore formation for size restoration in asexual divisions. Dinophyta (dinoflagellates), within Alveolata, comprise around 2,000 photosynthetic among 2,500 total, characterized by two dissimilar flagella in transverse and longitudinal grooves enabling spinning motility, thecal plates, and peridinin-chlorophyll proteins. Many are marine , with some producing toxins causing red tides and , as in genera like Alexandrium and . Additional groups include Haptophyta (e.g., coccolithophores with scales) and Cryptophyta, both with secondary red-derived plastids and mixotrophic capabilities, alongside excavate-derived Euglenophyta featuring green secondary plastids in flexible, euglenoid cells. These diverse lineages reflect multiple endosymbiotic events shaping algal .00604-6)

Historical Shifts in Classification

In 1753, Carl Linnaeus included algae within the plant kingdom in Species Plantarum, classifying them under the class Cryptogamia alongside other non-flowering plants, based primarily on reproductive characteristics rather than phylogenetic relationships. This approach treated algae as a heterogeneous assemblage of thalloid organisms lacking vascular tissue. Subsequent 19th-century classifications expanded on pigmentation and morphology, establishing major divisions such as Chlorophyceae (green algae), Phaeophyceae (brown algae), and Rhodophyceae (red algae), as proposed by botanists like William Henry Harvey in 1836, who arranged them into color-based groups reflecting dominant pigments like chlorophyll, fucoxanthin, and phycoerythrins. These systems were artificial, prioritizing observable traits over evolutionary descent, and initially focused on macroscopic marine forms while gradually incorporating freshwater and unicellular species. Mid-20th-century advancements in revealed fundamental cellular differences, prompting the separation of prokaryotic "blue-green algae" from eukaryotic algae. micrographs in the 1950s demonstrated the absence of membrane-bound organelles in blue-green forms, leading Roger Stanier and to redefine in 1962 to encompass these organisms, reclassifying them as within the prokaryotic domain rather than algae. This shift, formalized in subsequent taxonomic works like Bergey's Manual, excluded prokaryotes from algal groupings, recognizing cyanobacteria's closer relation to based on , peptidoglycan walls, and 70S ribosomes. By the 1970s, five-kingdom systems by Robert Whittaker further delineated algae as eukaryotic protists, emphasizing their polyphyletic origins across multiple lineages.00553-3) The advent of in the 1980s and 1990s revolutionized algal taxonomy through sequencing and analyses, overturning morphology-based schemes. Carl Woese's work confirmed cyanobacteria's bacterial affinity, while small subunit rRNA trees revealed eukaryotic algae's dispersal among supergroups: (Chlorophyta and Streptophyta) as sister to land plants, (Rhodophyta) in , and (Phaeophyceae) within Stramenopiles. These data highlighted algae's non-monophyly, with groups like diatoms and dinoflagellates deriving from secondary endosymbioses, prompting revisions such as the dissolution of chromalveolate hypotheses and recognition of diverse clades like Haptophyta and Cryptophyta. By the 2000s, genomic studies refined these relationships, emphasizing endosymbiotic events and transfers as drivers of diversity, though debates persist on deep-branching resolutions due to long-branch attraction artifacts. Contemporary classifications prioritize clade-based systems, continuously updated with multi- phylogenies to reflect evolutionary history over traditional groupings.

Evolutionary History

Origins of Oxygenic Photosynthesis

Oxygenic photosynthesis, characterized by the splitting of molecules to generate oxygen as a byproduct while fixing into organic compounds, first evolved in , a group of prokaryotic photoautotrophs. This innovation combined two photosystems—Photosystem I and II—allowing the use of abundant as an rather than scarce reductants like or iron used in earlier anoxygenic forms. Phylogenetic analyses indicate that the lineage leading to diverged from other approximately 3.4 billion years ago, with the core machinery of oxygenic assembling prior to the last common ancestor of extant . Molecular clock estimates place the emergence of oxygenic photosynthesis between 3.5 and 2.7 billion years ago during the Archean Eon, supported by genomic comparisons of cyanobacterial genes involved in photosystem assembly and oxygen evolution. Geological proxies, such as banded iron formations and sulfur isotope excursions, suggest localized oxygen production predated the Great Oxidation Event (GOE) by hundreds of millions of years, though atmospheric accumulation only occurred around 2.4 billion years ago due to sinks like reduced iron and methane. Fossil evidence, including microbially induced sedimentary structures and thiopurine biomarkers from 2.7 Ga rocks, corroborates early cyanobacterial activity, but direct morphological fossils of cyanobacteria date to about 1.75 billion years ago, reflecting preservation biases rather than origination timing. Debates persist on whether oxygenic photosynthesis arose de novo or via lateral gene transfer from anoxygenic bacteria, with favoring an endogenous within a proto-cyanobacterial lineage adapting to low-sulfide environments. The GOE, triggered by cyanobacterial proliferation and the oxidation of oceanic reductants, marked a causal shift from an anoxic to oxygenated world, enabling aerobic respiration but initially devastating anaerobic ecosystems. These origins underscore cyanobacteria's pivotal role in transforming Earth's , with empirical constraints from independent isotopic and phylogenetic datasets converging on a pre-2.7 Ga timeline despite uncertainties in early rock records.

Endosymbiotic Events

The primary endosymbiotic event established oxygenic photosynthesis in eukaryotes through the engulfment of a free-living cyanobacterium by a heterotrophic protist host, leading to the endosymbiont's integration as the progenitor of chloroplasts. This singular occurrence produced primary plastids—bounded by two membranes—in the Archaeplastida clade, which includes glaucophytes, rhodophytes (red algae), and chlorophytes (green algae, ancestral to land plants). Molecular divergence estimates place the origin of photosynthetic eukaryotes before 1,558 million years ago (MYA), with the divergence of red and green algal lineages around 1,500 MYA. Supporting evidence encompasses the double-membrane structure of primary plastids (inner cyanobacterial-derived, outer phagosomal), circular plastid DNA akin to bacterial chromosomes, 70S ribosomes, and nuclear genes of cyanobacterial phylogenetic affinity encoding organelle-targeted proteins. Secondary endosymbioses ensued when eukaryotic predators engulfed primary plastid-bearing algae, retaining the and yielding complex plastids typically enclosed by three or four membranes, often with vestigial nucleomorphs in lineages like cryptophytes and chlorarachniophytes. These events diversified algal groups beyond ; red algal-derived secondary plastids characterize chromalveolates (e.g., diatoms, , haptophytes, and some dinoflagellates), while green algal-derived ones appear in euglenozoans and chlorarachniophytes, with independent acquisitions inferred from phylogenetic incongruences. transfers from endosymbiont nuclei to the host accompanied these integrations, shrinking plastid genomes to 0.1–1% of cyanobacterial sizes and necessitating sophisticated protein import via endoplasmic reticulum-derived membranes. Tertiary and higher-order endosymbioses, rarer and lineage-specific, involved engulfment of secondary or tertiary algae, as in peridinin-lacking dinoflagellates acquiring or green algal plastids, evidenced by chimeric membrane topologies and phylogenies. These serial events, spanning from the to , underscore endosymbiosis's role in algal diversification, though host-endosymbiont compatibility constraints limited primary events to one major success, with secondary occurrences numbering at least four to six independently. A parallel, recent primary endosymbiosis (~120 MYA) in the amoeboid Paulinella chromatophora exemplifies ongoing potential, featuring chromorelicts with reduced but functional photosynthetic .

Connections to Land Plants and Anoxic Events

Land plants, or , evolved from a lineage of streptophyte within the clade, sharing derived traits such as phragmoplast-mediated , rosette-shaped cellulose-synthesizing complexes, and similar compositions including fucosylated xyloglucans. This ancestral alga was likely a freshwater-dwelling, filamentous or branched multicellular form capable of zygote retention, a precursor to the . estimates place the divergence of streptophytes from chlorophyte around 700–1,000 million years ago, with the lineage emerging approximately 500–470 million years ago during the mid-Ordovician period.01028-9) The transition to terrestrial life involved adaptations for resistance, such as cuticle-like secretions and upright growth, building on algal precursors like hormone signaling pathways (e.g., responses) present in streptophytes prior to land colonization. evidence, including sporangia from the (~450 million years ago), supports this timeline, indicating that early embryophytes radiated in freshwater habitats before fully exploiting subaerial environments. Phylogenetic analyses consistently position land plants as a monophyletic group nested within streptophytes, with closest algal relatives including orders like Charales and Zygnematales, though the precise remains debated due to incomplete sampling of extant diversity. The proliferation of early vascular land plants during the period (~419–359 million years ago) indirectly influenced marine algal dynamics and contributed to oceanic anoxic events through enhanced nutrient delivery. Root systems and forest formation increased of continental silicates, elevating fluxes of and other bioavailable nutrients into coastal oceans, which fueled and explosive algal productivity. This nutrient pulse promoted widespread blooms, particularly of and eukaryotic algae, leading to high export to seafloors, where microbial respiration depleted bottom-water oxygen and expanded anoxic zones. Multiple Late anoxic episodes, coinciding with Kellwasser and Hangenberg events (~372 and 359 million years ago), correlate with peaks in biomass and associated biotic crises, including marine extinctions. carbon burial during these events, driven by algal-derived organic sediments, drew down atmospheric CO2 and may have amplified , though primary drivers included and sea-level changes. In later oceanic anoxic events (e.g., OAE2 ~94 million years ago), diversified eukaryotic , such as coccolithophores and dinoflagellates descended from algal lineages, sustained high under warm, stratified oceans, further linking algal evolution to anoxia through carbon cycling feedbacks. These events selected for resilient algal groups adapted to low-oxygen niches, shaping modern communities.

Habitats and Distribution

Primary Aquatic Environments

![Kelp forest in Monterey][float-right] The oceans constitute the primary aquatic environment for algae, hosting the majority of global algal through communities. These microscopic algae, including diatoms, dinoflagellates, and coccolithophores, dominate the open ocean's , where they account for approximately half of Earth's total despite comprising less than 1% of global photosynthetic . Annually, oceanic fix between 30 and 50 billion metric tons of carbon, underscoring their outsized role in marine ecosystems and global biogeochemical cycles. Macroalgae, or seaweeds, primarily inhabit shallow coastal marine waters, typically less than 100 deep, where penetration supports their growth on substrata or sediments. Species such as (e.g., in the order Laminariales) form extensive underwater forests in temperate and polar regions, while tropical reefs feature coralline and turf-forming species that stabilize substrates and contribute to habitat complexity. These benthic macroalgal communities represent the largest vegetated habitats in the sea, with productivity concentrated in nutrient-rich zones and estuaries. Freshwater environments, including lakes, rivers, and ponds, support significant algal populations, particularly of (Chlorophyta) and , though they encompass a smaller fraction of global algal biomass compared to marine systems. Approximately 80% of green algal occur in freshwater habitats, thriving in planktonic, periphytic, or benthic forms adapted to varying nutrient levels and flow regimes. In lotic systems like streams, periphyton-dominated algae drive food webs, while lentic waters such as lakes host blooms influenced by seasonal stratification. Brackish waters in estuaries bridge marine and freshwater realms, fostering transitional algal assemblages resilient to fluctuations.

Extreme and Symbiotic Habitats

Algae inhabit a range of extreme environments characterized by conditions lethal to most eukaryotic life, including high temperatures, low , hypersalinity, and subzero temperatures. Thermophilic algae, such as the red alga Cyanidioschyzon merolae from the class Cyanidiophyceae, thrive in acidic volcanic hot springs with temperatures exceeding 50°C and values below 2, where they dominate microbial biomass through adaptations like heat-stable enzymes and unique metabolic pathways for carbon fixation. In geothermal sites like , form colorful mats in waters from 40°C to 70°C, contributing to despite . Acidophilic algae persist in acid mine drainage (AMD) sites, where pH drops below 3 and heavy metals like iron and aluminum abound; species such as the green alga Ulothrix and euglenoids proliferate by tolerating dissolved metals and utilizing them for growth, often forming biofilms that influence metal cycling. Hypersaline environments, including salt lakes and evaporation ponds, host halophilic green algae like Dunaliella salina, which accumulate compatible solutes such as glycerol to counter osmotic stress at NaCl concentrations up to 3.5 mol/L, enabling survival where water activity is low. Cryophilic algae, including snow algae like Chlamydomonas nivalis and diatoms in Antarctic sea ice, endure temperatures near 0°C with high salinity and limited light by producing antifreeze proteins and pigments that enhance light harvesting under snow cover, forming visible red or green patches that accelerate ice melt through albedo reduction. These adaptations underscore algae's physiological resilience, often involving membrane modifications and osmoprotectant synthesis verified through genomic and proteomic studies. In symbiotic habitats, algae form mutualistic associations that expand their ecological niches beyond free-living states. Lichens represent a terrestrial symbiosis where fungal partners (typically ascomycetes) provide structural support and mineral access, while algal photobionts—often green algae like Trebouxia or cyanobacteria—supply fixed carbon via photosynthesis, enabling colonization of nutrient-poor substrates such as rocks and bark in arid or cold regions. Marine symbioses include dinoflagellate algae (zooxanthellae, e.g., Symbiodinium spp.) within scleractinian corals, where algae translocate up to 90% of photosynthetic products to the host for calcification and growth, in exchange for inorganic nutrients and a protected environment; this partnership, originating in the Triassic period around 240 million years ago, underpins reef ecosystems but is vulnerable to thermal stress causing bleaching. Similar associations occur with cnidarians like sea anemones and jellyfish, where algae enhance host nutrition in oligotrophic waters. These symbioses demonstrate causal dependencies, with algal photosynthesis driving host metabolism, as evidenced by stable isotope tracing and controlled exclusion experiments.

Ecological Roles

Primary Production and Oxygen Dynamics

Phytoplankton, dominated by eukaryotic and prokaryotic algae, account for approximately 50% of global net despite comprising less than 1% of photosynthetic . Annual marine by is estimated at 45-50 gigatons of carbon. This productivity, driven by oxygenic in sunlit surface waters, forms the base of oceanic food webs and influences through the . Algae fix carbon dioxide using the enzyme ribulose-1,5-bisphosphate carboxylase/oxygenase (Rubisco), which catalyzes the incorporation of CO₂ into organic compounds. Microalgae benefit from high surface area-to-volume ratios that enable rapid CO₂ uptake during photosynthesis. Temperature influences these processes, with low temperatures inhibiting Rubisco activity and reducing carbon fixation rates, while optimal ranges enhance enzymatic efficiency and overall productivity. Marine algae contribute roughly 50% of Earth's atmospheric oxygen through , with the remainder primarily from terrestrial . and eukaryotic such as diatoms and dinoflagellates release oxygen as a while fixing , maintaining long-term atmospheric levels via burial of that prevents re-oxidation. Estimates attributing over 70% to algae exceed empirical measurements and overlook net balances from respiration and . Oxygen dynamics in algal-dominated systems exhibit diurnal fluctuations: supersaturation during daylight from photosynthetic release contrasts with depletion at night due to community respiration. Intense blooms can elevate dissolved oxygen to 190% of saturation midday but foster hypoxia upon senescence as bacterial decomposition consumes oxygen faster than replenishment, contributing to dead zones in eutrophic waters. Such events underscore causal links between nutrient enrichment, algal proliferation, and localized anoxia, independent of broader atmospheric trends.

Nutrient Cycling and Symbioses

Algae, particularly , drive nutrient cycling in aquatic ecosystems by assimilating dissolved inorganic nutrients such as (N) and (P) into via , with subsequent remineralization by heterotrophic microbes recycling these elements to support ongoing . In ocean surface waters, recycling alone sustains roughly 80% of phytoplankton , equivalent to approximately 6,800 teragrams of per year, primarily through the where bacteria decompose algal exudates and detritus, releasing bioavailable forms like . cycles similarly, though often more constrained by slower regeneration rates and sinking export, limiting algal growth in vast oligotrophic regions and influencing community composition toward species with efficient uptake strategies. This internal recycling minimizes reliance on external inputs from or rivers, stabilizing in stratified waters but rendering systems vulnerable to disruptions like stratification intensification under . Symbiotic associations amplify algal contributions to nutrient cycling by facilitating localized retention and exchange in nutrient-scarce habitats. In lichens, fungi partner with (e.g., Trebouxia spp.) or (e.g., spp.), where photobionts supply fixed carbon and the mycobiont absorbs atmospheric or soil-derived minerals, enabling these composites to thrive on barren rocks and recycle nutrients at microscales unavailable to free-living algae. This , ancient and widespread, covers about 8% of Earth's land surface and enhances by substrates, indirectly bolstering terrestrial nutrient inputs to aquatic systems. In marine settings, algae ( ) symbiose with cnidarians like corals and sea anemones, translocating up to 90% of photosynthates to hosts while receiving and waste products for reuse, which sustains high productivity in phosphorus-limited reefs despite low ambient concentrations. Sponges similarly host algal or cyanobacterial symbionts that fix carbon and , filtering and retaining nutrients from currents to support sponge growth and export-resistant cycling in benthic environments. These partnerships exemplify causal efficiency: algal autotrophy subsidizes heterotrophic hosts, reducing nutrient leakage and buffering ecosystems against scarcity, though bleaching events from thermal stress disrupt this balance, releasing unused nutrients and altering local cycles.

Harmful Algal Blooms and Disruptions

Harmful algal blooms (HABs) consist of rapid proliferations of certain species, often or dinoflagellates, that produce toxins or cause oxygen depletion in aquatic environments. These events disrupt ecosystems by releasing potent such as microcystins, anatoxins, and saxitoxins, which inhibit in other organisms and bioaccumulate in food webs. HABs form when imbalances—primarily excess and from agricultural runoff, discharge, and urban —fuel , enabling algae to outcompete other species under favorable conditions like warm temperatures and calm waters. The primary driver of HABs is anthropogenic nutrient pollution rather than natural variability alone, as evidenced by correlations between application rates and bloom intensity in watersheds. For instance, loading from nonpoint agricultural sources has historically triggered blooms in systems like , where 1960s-1970s led to widespread hypoxia and nuisance growths covering up to 20% of the lake's surface area. of algal following blooms consumes dissolved oxygen, creating hypoxic "dead zones" that suffocate and , collapsing local and altering trophic structures by favoring toxin-tolerant species. In marine settings, HABs like those from produce brevetoxins that cause mass strandings and contamination, disrupting coastal food chains. Human health risks from HABs include acute neurotoxic and hepatotoxic effects from cyanotoxins and saxitoxins, manifesting as , , bloody , muscle , , and liver damage upon ingestion or inhalation. In the 2014 water crisis, levels from a bloom exceeded safe thresholds, forcing a two-day shutdown of for 500,000 residents and highlighting vulnerabilities in municipal supplies. Economically, HABs impose costs through fishery closures, declines, and expenses; the same event resulted in $43 million in lost recreational revenue. In the , seasonal dead zones—hypoxic areas exceeding 6,705 square miles in 2024—reduce shrimp and fish yields by displacing commercial stocks, with five-year averages surpassing 4,298 square miles due to nutrient flux. These disruptions extend to long-term ecological shifts, such as persistent anoxia fostering dominance and eroding for native fisheries, with global HAB frequency rising alongside intensified since the mid-20th century. While warmer stratification may prolong blooms, empirical data underscore reduction as the causal leverage point, as reductions in point-source in the 1980s temporarily curbed events before nonpoint sources reversed gains. Monitoring via and toxin assays has documented over 300 HAB events annually in U.S. waters, emphasizing the need for to mitigate recurrent hypoxic expansions.

Human Uses and Cultivation

Traditional and Cultural Applications

Algae have been utilized by various cultures for food and medicinal purposes over millennia, with evidence from archaeological dental remains indicating consumption in as early as 6400 BCE, where provided essential vitamins, nutrients, and protein before widespread animal agriculture. In prehistoric coastal sites from to , starch granules and molecular biomarkers in dental confirm regular intake of species like and Palmaria, suggesting it served as a staple rather than occasional . In , the harvested spirulina ( platensis) from starting around the , drying it into tecuitlatl cakes consumed by warriors for endurance and traded in markets, as documented in Spanish colonial accounts by chroniclers like . This cyanobacterium, rich in protein, supported populations in nutrient-scarce regions. In , consumption dates to the 4th century in and 6th century in , where species like () and () became dietary staples, often prepared as delicacies or everyday foods for their iodine and mineral content. Traditional Chinese medicine employed seaweeds such as for treating , goiter, and inflammation, attributing efficacy to their and properties observed empirically. European coastal communities, particularly in Ireland and , traditionally gathered dulse () for direct consumption or as a , with records from the onward noting its role in sustaining populations during shortages like the Irish Potato Famine of the 1840s, where it provided caloric relief amid crop failure. In , limu (various algae) held cultural importance in indigenous diets and rituals, used for flavoring, against infections, and as offerings, with over 100 identified in traditional knowledge systems predating European contact. These applications reflect algae's accessibility in aquatic environments and their nutritional density, though efficacy claims in often rely on anecdotal rather than controlled historical trials.

Modern Cultivation Techniques

Modern algae cultivation techniques distinguish between , often grown in controlled terrestrial systems for biofuels, nutraceuticals, and , and macroalgae (seaweeds), primarily farmed in open marine environments for and industrial uses. Microalgal cultivation relies on optimizing , nutrients, CO2 supply, and mixing to achieve high densities, with systems scaled from flasks to commercial hectares. Macroalgal farming emphasizes vegetative and spatial arrangement to maximize growth in nutrient-rich coastal or offshore waters, with global production reaching over 35 million metric tons wet weight annually as of 2020, dominated by species like and Kappaphycus in tropical regions. For , open raceway ponds represent the most economical large-scale method, featuring shallow (0.2-0.3 m deep) channels with paddlewheels for circulation, covering areas up to several s and achieving areal productivities of 10-30 g/m²/day under optimal conditions like 25-30°C temperatures and continuous nutrient dosing. These systems, operational since the and refined through improvements in liners and , incur capital costs of approximately $50,000-100,000 per but face challenges from , predation, and by unwanted , limiting yields to 0.1-0.3 g/L/day. Closed photobioreactors (PBRs), such as tubular or flat-panel designs, offer superior control over parameters like (7-9) and dissolved oxygen, enabling higher densities (1-5 g/L) and productivities up to 1-2 g/L/day, particularly for strains like or , but at 2-10 times the capital expense ($300,000-1,000,000 per equivalent) due to materials like or plastics and energy demands for pumping and cooling.
Cultivation SystemKey AdvantagesKey DisadvantagesTypical ProductivityEstimated Production Cost (Lipids, $/gal)
Open Raceway PondsLow construction and operational costs; scalable High risk; dependence; lower densities10-50 g/m²/day9-13
Closed PBRs resistance; precise environmental control; higher yieldsHigh capital and energy costs; ; maintenance intensive0.5-2 g/L/day20-32
Hybrid approaches, integrating PBRs for seed culture with for bulk growth, have gained traction since the to balance costs and , as demonstrated in pilot facilities achieving 20-40% cost reductions through optimized inoculum scaling. Recent innovations from 2020-2025 include attached-growth biofilms on surfaces to simplify harvesting (reducing energy by 50-90% compared to ) and LED-illuminated vertical PBRs for indoor cultivation, enhancing yields by 2-3 fold via spectral tuning to photosynthetic peaks at 620-680 nm, though remains constrained by costs exceeding $0.05/kWh. Macroalgal cultivation employs offshore longline systems, where juvenile fronds (seeded via vegetative cuttings or spores) are attached to buoyant ropes (50-200 m lengths) suspended 1-5 m below the surface, facilitating water flow and nutrient uptake for species like Saccharina latissima or Gracilaria, with harvest cycles of 4-8 months yielding 10-20 kg wet weight per meter of line. In Asia, grid or raft methods using bamboo or synthetic nets support high-density farming, as in Indonesia's Eucheuma operations producing over 10 million tons yearly, with modern refinements including automated tensioners and GPS-monitored arrays to withstand currents up to 1 m/s. Emerging offshore techniques since 2020, such as submerged grids in deeper waters (10-30 m) integrated with wind farms or IMTA (co-cultured with shellfish to recycle nutrients), mitigate nearshore overcrowding and storm risks while accessing upwelled nutrients, though biofouling and permitting delays limit expansion to pilot scales in Europe and the U.S. Both micro- and macroalgal systems incorporate real-time monitoring via sensors for parameters like turbidity (for microalgae) or growth metrics (via image analysis for seaweeds), with CO2 enrichment from industrial flue gases boosting productivities by 20-50% in closed setups, though algal strains must tolerate impurities like SOx to avoid toxicity thresholds above 100 ppm. Economic viability hinges on multi-product biorefineries extracting lipids, proteins, and polysaccharides sequentially, yet open systems predominate commercially due to costs below $500/ton dry biomass versus $2,000-10,000/ton for PBRs, underscoring trade-offs in yield versus reliability.

Biofuel Production: Achievements and Limitations

Microalgae species such as and Neochloris oleoabundans exhibit lipid contents exceeding 74% of dry biomass under optimized conditions, enabling potential yields far surpassing terrestrial crops like soybeans, which average around 20% oil content. Cultivation systems have demonstrated biomass productivities up to 0.27 g/L/day for Chlorella sp., with lipid productivities reaching 0.11 g/L/day. The U.S. Department of Energy-funded Cornell Consortium achieved a milestone of 1,500 gallons of per acre per year by 2014, advancing toward targeted yields of 2,500 gallons/acre/year. Additionally, microalgae can fix CO2 at rates up to 1.5 g/L/day in optimized photobioreactors, as seen with Nannochloropsis gaditana, positioning them as candidates for integrating production with carbon capture from industrial emissions. Genetic engineering has further enhanced lipid accumulation, with modifications in Nannochloropsis gaditana doubling lipid production and strains like Chlamydomonas reinhardtii mutants reaching 50% lipid content. Pilot-scale demonstrations, such as Renewable Algal Energy's 2014 off-take agreement with Neste Oil for algae crude, highlight progress in commercialization pathways. Recent innovations, including a 2025 nanotechnology method that boosted biofuel yields from microalgae by 300%, underscore laboratory-scale breakthroughs in extraction efficiency. Despite these advances, production costs remain prohibitive, estimated at $2.5–$5 per kg of compared to approximately $0.5 per kg for fuels, rendering algae uneconomical at $2.5–$5.5 per versus $1–$2 per for diesel. Harvesting and , which account for up to 50% of costs, involve energy-intensive steps like and drying, often resulting in a negative net ratio below 1, where input exceeds output. Life-cycle assessments indicate that algae can emit more gases than conventional diesel due to high demands in cultivation and . Scalability challenges persist, as laboratory yields fail to replicate outdoors owing to contamination, inconsistent environmental conditions, and infrastructure demands, leading to the abandonment of numerous commercial ventures, including ExxonMobil's algae program in 2023. While integrated biorefineries co-producing high-value products could mitigate costs, current economic models show algae biofuels require subsidies or technological leaps to compete without relying on overstated environmental benefits that ignore full life-cycle impacts.

Food, Fertilizer, and Bioremediation Uses

Macroalgae, commonly known as seaweeds, serve as a primary source of edible algae, with global aquaculture production reaching approximately 35.8 million tonnes annually as of recent estimates, predominantly for direct human consumption in forms such as nori, wakame, and kombu. These seaweeds provide high dietary fiber content, ranging from 23.5% to 64% of dry weight, along with minerals like iodine and phytochemicals, while remaining low in calories, fats, and sugars. Microalgae such as spirulina and chlorella contribute smaller volumes, with annual dry production around 12,000 tonnes for spirulina and 6,600 tonnes for chlorella, valued for their protein content up to 70% in spirulina and use as dietary supplements. Algae function as biofertilizers due to their rich profiles, including , , and , enabling efficient cycling and atmospheric particularly by . Field trials have demonstrated yield improvements, such as a 21% increase in output with algae-based fertilizers and up to 7% higher seed yields in soybeans and mungbeans when combined with sulfur-coated . applications enhance and microbial activity, reducing reliance on synthetic fertilizers while promoting plant growth through bioactive compounds. In , algae excel at by assimilating nutrients and adsorbing , with achieving over 70% removal efficiencies for and . Specific studies report up to 98% removal and heavy metal rates such as 90% for lead and 83% for using like . Mechanisms include cell surface adsorption and intracellular accumulation, rendering algae a low-cost, eco-friendly option for , though efficacy varies with , metal concentration, and algal .

Controversies and Critical Assessments

Overstated Environmental Benefits

Claims that oceanic algae, particularly , generate 50 to 80 percent of Earth's atmospheric oxygen through overstate their net environmental role, as this metric reflects gross production rather than the minimal net flux to the atmosphere after oceanic respiration consumes nearly all output. Annual biological oxygen production and consumption in the balance closely, with atmospheric oxygen levels sustained primarily by long-term geological carbon from ancient eras rather than contemporary algal activity. Such portrayals, common in environmental , ignore this steady-state dynamic and imply a disproportionate dependence on current algal populations for breathable air, which empirical models do not support. Algae-based biofuels have been promoted as a low-carbon alternative capable of substantial CO2 , with cultivation systems touted for absorbing emissions while yielding . However, life-cycle assessments accounting for full production chains frequently demonstrate net equivalent to or higher than conventional diesel, driven by energy-intensive steps like fertilization, biomass dewatering, and extraction. A 2023 study highlighted that microalgae can exceed diesel's when indirect emissions from and inputs are included. Similarly, analyses of pathways for algal renewable diesel show emissions reductions of only 63 to 68 percent under optimistic conditions, often eroded by real-world inefficiencies in scaling open ponds or photobioreactors. These findings underscore how initial in peer-reviewed projections, sometimes from grant-funded research, overlooks downstream energy penalties that diminish purported sequestration gains. Direct algal carbon capture and utilization schemes face analogous overstatements, as high CO2 dissolution rates in cultivation media are constrained by limitations and sensitivity to impurities, yielding inconsistent absorption efficiencies below 50 percent in pilot systems. While can theoretically sequester 1.83 kilograms of CO2 per kilogram of , practical deployments require substantial freshwater, nutrients, and for mixing and harvesting, inflating the system's overall and hindering beyond niche applications. Environmental claims in and industry reports often prioritize gross uptake figures without rigorous net , potentially influenced by incentives favoring bio-based solutions over proven alternatives like or with mineralization.

Economic and Scalability Challenges

Large-scale algae production faces substantial economic barriers, primarily due to elevated capital and operational expenditures that exceed those of conventional biofuels or terrestrial crops. Techno-economic analyses indicate minimum selling prices ranging from $674 to $1,063 per dry ton for open-pond systems, far higher than targets of under $400 per ton needed for competitiveness. These costs stem from intensive requirements for nutrients, CO2 supplementation, and energy for and mixing, which can constitute 30-50% of operational expenses in photobioreactors or raceway ponds. Harvesting and dewatering represent a disproportionate share of expenses, often 20-30% of total production costs, owing to the low biomass densities (typically 0.5 g/L in ponds) and small cell sizes necessitating energy-intensive methods such as centrifugation or flocculation. Downstream processing for lipid extraction or biorefining further amplifies these hurdles, with minimum fuel selling prices for algal biofuels modeled at $4.7 to $5.42 per gasoline gallon equivalent as of 2022-2024, rendering them uncompetitive against fossil diesel priced around $3 per gallon without subsidies. Optimistic projections in equatorial regions suggest potential drops to $1.89-$2.15 per liter gasoline-equivalent, but these assume idealized conditions and low-carbon electricity, which real-world implementations rarely achieve. Scalability is impeded by biological and engineering constraints, including contamination risks in open systems from grazers, , or , which can crash cultures and necessitate costly mitigation like high-salinity strains or sterilization. Productivity declines at larger volumes due to inadequate light penetration, from mixing, and uneven distribution, with pond yields often limited to 0.01-0.12 g/L/day versus laboratory rates exceeding 1 g/L/day. Transitioning to closed photobioreactors improves control but escalates by factors of 5-10 times over s, deterring widespread adoption. Commercialization remains elusive for biofuel applications, with investor skepticism rooted in historical failures—such as major consortia abandoning projects post-2010s pilots due to persistent cost overruns—and a lack of profitable facilities as of 2023. While niche markets for high-value products like sustain limited operations, bulk algae for fuels or feeds struggles against cheaper alternatives, highlighting the gap between laboratory promise and industrial reality.

Health and Ecological Risks

Harmful algal blooms (HABs) release potent toxins such as microcystins, produced primarily by , which pose significant risks to through ingestion, inhalation, or dermal contact. These hepatotoxins can cause acute symptoms including , , , and liver inflammation, with severe exposures leading to organ damage or hemorrhage. In marine environments, toxins like those causing accumulate in filter-feeding organisms, resulting in neurotoxic effects such as and upon consumption. Chronic low-level exposure to microcystins has been linked to potential carcinogenic effects and disruption of cellular processes, though long-term remain limited. Vulnerable populations, including children and those with pre-existing liver conditions, face heightened risks during recreational water exposure. Ecological risks from algal overproliferation often stem from nutrient-driven , leading to hypoxic conditions and dead zones where dissolved oxygen levels drop below 2 mg/L, suffocating and benthic organisms. HABs contribute to massive kills by direct action, which damages gills and nervous systems, or indirectly through decay that exacerbates oxygen depletion; for instance, events in have caused widespread aquatic mortality. These blooms disrupt food webs by favoring toxin-producing species over native , reducing and altering primary production dynamics. In freshwater systems, cyanobacterial dominance inhibits grazing and shifts microbial communities, impairing nutrient cycling. Invasive algal species amplify these threats by rapidly colonizing habitats, outcompeting natives through and resource monopolization, which erodes stability. For example, species in Mediterranean and coastal waters smother seagrasses and corals, reducing habitat complexity and supporting fewer native species. Such invasions can trigger secondary HABs by altering water chemistry and promoting toxin persistence, with cascading effects on fisheries and . exacerbates spread via warmer waters and altered currents, increasing the frequency and scale of these disruptions.

Recent Developments

Biotechnology and Genetic Advances

Genetic engineering of algae has advanced significantly, with transformation techniques established for over 50 microalgal species by 2025, enabling targeted modifications for enhanced bioproduct yields. These methods include , Agrobacterium-mediated delivery, and biolistic particle bombardment, which have improved efficiency in species like and Phaeodactylum tricornutum. approaches further integrate engineering to redirect carbon flux toward desirable compounds, such as or pigments, bypassing native limitations in . CRISPR/Cas9 has emerged as a pivotal tool, with the first successful application in reported in 2014 using C. reinhardtii. By March 2025, innovations like optimized variants doubled gene-editing frequencies in algae, addressing previous hurdles in low transformation rates and off-target effects. In Parachlorella kessleri, CRISPR/Cas9-mediated knockouts achieved in 2024 enhanced industrial strain potential by disrupting specific genes without compromising growth. Complementary tools such as zinc-finger nucleases (ZFNs), TALENs, and (RNAi) provide alternatives for precise insertions or silencing, particularly in species resistant to . These technologies have generated strains with elevated triacylglycerol and contents, verifiable through lipid productivity assays showing up to 2-3 fold increases in select mutants. For biofuel applications, genetic modifications target biosynthesis pathways, engineering algae to accumulate fatty acids suitable for , with studies from 2024-2025 demonstrating optimized profiles via overexpression of and thioesterases. In Nannochloropsis species, edits improved yields by 50% under nutrient stress, as quantified in controlled experiments. Beyond fuels, advances extend to bioactive compounds; engineered strains produce higher levels for nutraceuticals, with metabolic flux analysis confirming redirected isoprenoid pathways. also enables novel pathway expression, such as bacterial hydrogenases in for , advancing yields reported in 2025 reviews. Regulatory and scalability challenges persist, yet integrated with these tools accelerates strain selection, as seen in the 2023-2025 AlgaePrize initiatives focusing on genetic for . delivery of components, developed by 2023, enhances editing in non-model algae, broadening applicability. Overall, these genetic advances position algae as versatile platforms for sustainable , supported by empirical data from peer-reviewed transformations yielding quantifiable productivity gains.

Market Growth and Policy Initiatives

The global algae products market, encompassing applications in biofuels, nutraceuticals, food additives, and bioplastics, was valued at approximately USD 5.20 billion in 2024 and is projected to grow at a (CAGR) of 6.3% through 2032, driven by increasing demand for sustainable sources and alternative proteins. Specific segments show varied trajectories; for instance, the market reached USD 782.59 million in 2024 and is expected to expand to USD 841.30 million in 2025, fueled by applications in feed and . Algae biofuels, a key growth area, were valued at USD 10.4 billion in 2024, with forecasts indicating USD 19.0 billion by 2034 at a 6.4% CAGR, supported by advancements in cultivation efficiency despite historical scalability hurdles. Policy initiatives have accelerated market expansion through targeted government funding and incentives. In the United States, the Department of Energy allocated USD 20.2 million in November 2024 to ten projects advancing mixed algae systems for low-carbon biofuels and bioproducts, emphasizing integrated cultivation and conversion technologies. Earlier in April 2024, USD 18.8 million was awarded for innovations in algae-derived and biofuels to support decarbonization efforts. Complementary programs like the AlgaePrize competition, running from 2023 to 2025, challenge participants to develop commercial algae technologies, fostering innovation in biomass production. These initiatives, alongside tax incentives and research grants from agencies such as the DOE and USDA, create opportunities for industry scaling, though their long-term impact depends on overcoming economic barriers like high production costs.

References

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