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Aggregating anemone
Aggregating anemone
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Aggregating anemone
Scientific classification Edit this classification
Kingdom: Animalia
Phylum: Cnidaria
Subphylum: Anthozoa
Class: Hexacorallia
Order: Actiniaria
Family: Actiniidae
Genus: Anthopleura
Species:
A. elegantissima
Binomial name
Anthopleura elegantissima
(Brandt, 1835)

The aggregating anemone (Anthopleura elegantissima), or clonal anemone, is the most abundant species of sea anemone found on rocky, tide swept shores along the Pacific coast of North America.[1] This cnidarian hosts endosymbiotic algae called zooxanthellae that contribute substantially to primary productivity in the intertidal zone.[2] The aggregating anemone has become a model organism for the study of temperate cnidarian-algal symbioses. They are most well known for the ability to clone themselves.

Description

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Anthopleura elegantissima in the process of cloning itself

The polyps of the aggregating anemone reach up to eight cm across the oral disk with approximately 100 tentacles in three or four rows around the margins of the oral disk. Most are olive to bright green (depending on the species of algal symbionts present) with tentacles tipped in pink. Individuals that live in microhabitats that are deficient in photosynthetically active radiation (PAR), such as under docks or in caves, lack symbionts and are pale yellow to white in color.[3]

Range

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California sea anemone, Anthopleura elegantissima. Offshore Anacapa Island, 2016

Pacific coast of North America from Alaska, United States to Baja California, Mexico. Most common in protected waters.

Life history

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This species of anemone is capable of reproducing both sexually and asexually. As adults, aggregating anemones release gametes into the water that join to form genetically unique individuals that settle on intertidal rock. This genetically distinct individual can then proliferate through binary fission. Some argue that this is not true reproduction but actually a form of growth.[4] Fission is often prompted in the autumn by a decrease in the abundance of food and follows sexual spawning in summer.[5][6] Over time, a single individual can generate a large colony of genetically identical polyps. Because of its ability to grow in this manner, the genetic entity of a colony is potentially immortal on an ecological time scale.

Natural history

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Photosynthetic symbiosis

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Mycosporine-2-glycine, a mycosporine-like amino acid (MAA)

Aggregating anemones host endosymbiotic, photosynthetic algae in their tentacles, oral disk and column of the polyps. In addition to a chlorophyte, two species of dinoflagellate Symbiodinium, S. muscatinei and S. californium are known to inhabit the anemone.[7] These algae are generally referred to as zooxanthellae (dinoflagellates) and zoochlorellae (chlorophytes) and many polyps concurrently host more than one type of alga within their tissues. The rate of occurrence of each alga is determined by temperature and light regimes of anemone habitats.[8] Zoochlorellae are typically found at higher latitudes and in deeper intertidal habitats than zooxanthellae.[9] Of the two species of zooxanthellae that inhabit the anemone, S. californium is restricted to southern California due to its intolerance of cold temperatures whereas S. muscatinei is tolerant of a broad range of temperature and irradiance levels.

The mutualistic relationship of these organisms requires adaptations of each partner. The algal symbionts convert inorganic carbon into carbohydrates for use by each partner and release oxygen to the animal host in the process. To accommodate the algae, the anemone must provide concentrated carbon dioxide to their intracellular photosynthetic guests as well as photosynthetically active radiation (PAR) to fuel the photosynthetic process. This restricts the symbiotic organism to euphotic habitats and requires consistent exposure to high levels of ultraviolet radiation (UVR). To protect from potentially damaging UVR, the algae provide mycosporine-like amino acids (MAAs) that act as sunscreen for themselves and the host.[10] The anemones, in turn, produce antioxidants called superoxide dismutases to protect against reactive oxygen that causes oxidative stress.[11][12]

Agonism between colonies

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Territorial battle between anemones

The aggregating anemone is agonistic toward other individuals with different genetic disposition. When one colony of genetically identical polyps encounters a different genetic colony, the two will wage territorial battles. Aggregating anemones have specialized tentacles called acrorhagi that are used solely to deter other colonies from encroaching on their space. When a polyp makes physical contact with a non-clonemate, it extends the acrorhagi to attack the competing anemone with stinging cells called nematocytes. Acrorhagi of the attacking anemone leave behind a 'peel' of the ectoderm and nematocysts that causes tissue necrosis in the receiving animals.

A study of two colonies on a boulder removed from the shore and brought into a laboratory revealed that hostilities between neighboring colonies follow the tides. As water rushed into the tank, warrior polyps inflated their acrorhagi, tripled their body length and began reaching into an empty swath of rock between the colonies. Occasionally, a polyp from one of the colonies would move into the spatial zone between the two colonies, acting as a scout, and would be attacked by the warrior polyps of the other clone. If the scout polyp received enough stings, it would be attacked by its clonemates upon return to its own colony. The return of an attacked scout to the clone with acrorhagial peel may serve to communicate the presence and identity of neighboring clones to the interior of the colony.[13]

Predators

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The few known predators of the aggregating anemone include a species of nudibranch (Aeolidia papillosa), leather star, and mosshead sculpin.

See also

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Footnotes

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Revisions and contributorsEdit on WikipediaRead on Wikipedia
from Grokipedia
The aggregating anemone (Anthopleura elegantissima), also known as the clonal anemone, is a small marine belonging to the phylum and class , characterized by its tube-shaped body and ability to form dense, genetically identical colonies in intertidal habitats. Adults typically reach a column diameter of up to 2.5 inches (6.4 cm) and a crown width of 3.5 inches (8.9 cm), with a green or brown oral disk adorned by numerous tentacles tipped in white, pink, blue, or lavender, which are equipped with stinging nematocysts for capturing prey and defense. The species derives its green coloration from symbiotic algae, including (dinoflagellates) and zoochlorellae (chlorophytes), which provide nutrients through while residing in its tissues. Native to the northeastern Pacific Ocean, A. elegantissima inhabits rocky shores from Alaska to Baja California, primarily in the mid- to low-intertidal zone down to depths of about 60 feet (18.3 m), where it clings to rocks, crevices, or tide pools exposed to wave action and tidal fluctuations. These anemones often aggregate in large, contiguous masses of clones, covering extensive areas of shoreline, and enhance their camouflage by adhering small rocks, shell fragments, or debris to their pedal disks and column surfaces using adhesive structures. In these colonies, individuals exhibit territorial behavior, employing specialized acrorhagi—knob-like swellings beneath the tentacular collar packed with potent nematocysts—to engage in "clone wars" against neighboring non-clonal anemones, thereby maintaining distinct boundaries and preventing invasion. A. elegantissima sustains itself through a combination of symbiotic , which supply a significant portion of its energy needs via , and active predation on drifting planktonic organisms such as copepods, isopods, amphipods, small crabs, mussels, barnacle larvae, and occasionally . The anemones extend their tentacles to intercept food carried by currents, paralyzing prey with nematocyst stings before transporting it to the central . Reproduction occurs both asexually and sexually: during fall and winter, individuals undergo binary fission, splitting longitudinally to produce genetically identical clones that expand the ; in spring and summer, they broadcast eggs and sperm into the water column, forming free-swimming larvae that settle nearby to initiate new populations. This dual strategy contributes to the species' abundance and resilience; it is considered common with no special conservation needs, though it remains vulnerable to environmental stressors like oil spills, which can destroy habitats and affect recovery.

Taxonomy and description

Taxonomy

The aggregating anemone, scientifically known as Anthopleura elegantissima (Brandt, 1835), belongs to the phylum within the kingdom Animalia. Its full taxonomic is as follows: Kingdom: Animalia; Phylum: Cnidaria; Class: ; Order: Actiniaria; Family: Actiniidae; Genus: Anthopleura; Species: elegantissima. Historically, the species has been classified under junior synonyms such as Bunodactis elegantissima, Cribrina elegantissima, and Actinia elegantissima, but the current accepted is Anthopleura elegantissima as established by Brandt in 1835. The genus name Anthopleura derives from words anthos (flower) and pleura (side or rib), alluding to the flower-like arrangement and structure of the anemone's body. The specific epithet elegantissima is Latin for "most elegant," reflecting the species' graceful form and appearance. Among congeners, A. elegantissima is distinguished from the larger, solitary Anthopleura xanthogrammica (giant green anemone) by its smaller size (typically 2-5 cm diameter), clonal aggregating behavior in the upper , and morphological features such as branched verrucae arranged in rows and a colored oral disk with radiating lines, whereas A. xanthogrammica exhibits a firmer column, uniform green oral disk, and solitary habits in lower intertidal areas. It also differs from its sibling species A. sola, which is solitary rather than clonal and can reach larger sizes up to 25 cm across the tentacular crown, though both share similar morphological traits like radiating lines on the oral disk.

Description

The aggregating anemone (Anthopleura elegantissima) is a colonial characterized by its cylindrical polyps, which typically measure 2–5 cm in diameter across the oral disk but can reach up to 8 cm, with a column height of 4–6 cm. Each polyp features approximately 100 tentacles arranged in five rows around the margins of the oral disk, which is broad and flat, often displaying radiating lines from mesenterial insertions. The column is thick and smooth, colored olive-green to bright green with distinctive radiating white lines or streaks, and is covered in verrucae—small, sticky tubercles that facilitate attachment to substrates and collection of sand or shell fragments for and protection. The oral disk is typically green or brown, while the tentacles are bright green, often tipped in pink, purple, lavender, or blue, and are sticky due to secretions that aid in prey capture. These tentacles are equipped with nematocysts, specialized stinging cells that deliver toxins to immobilize small prey such as or intertidal . At the margin, below the tentacular crown, are acrorhagi—knob-like swellings packed with holotrichous nematocysts, serving as defensive structures. Internally, the gastrovascular cavity is divided by mesenteries, vertical partitions that extend from the body wall to the oral disk and support digestion and nutrient distribution. Color variations in A. elegantissima are influenced by pigmentation and the presence of symbiotic ; individuals in low-light, shaded microhabitats often appear pale yellow or white due to the absence of these symbionts.

Distribution and habitat

Range

The aggregating anemone (Anthopleura elegantissima) is endemic to the northeastern , with its native range extending along the Pacific coast of from southeastern to , . This distribution spans approximately 40 degrees of latitude, encompassing diverse coastal environments from temperate fjords in the north to subtropical rocky shores in the south. Within this range, A. elegantissima exhibits pronounced latitudinal variation in abundance, thriving most densely in protected embayments and estuaries where wave exposure is reduced, while occurring more sparsely on exposed outer coasts. It occupies a primarily mid-intertidal zonal distribution, forming clumped aggregations of genetically identical clones within rocky crevices and tidepools that provide shelter from and predation. Populations are particularly common in well-documented regions such as in Washington, in , and the off . First described by Brandt in 1835 based on specimens from the , A. elegantissima has no confirmed introduced populations outside its native range, remaining restricted to its original biogeographic province despite human-mediated coastal activities.

Habitat

The aggregating anemone, Anthopleura elegantissima, inhabits the mid- to low-intertidal zone on rocky shores, typically at elevations of 1.5–2.8 meters above , where it is periodically exposed to air during low . This positioning allows submersion for 5–15 hours per tidal cycle, balancing access to with tolerance for emersion stress. It forms dense clonal aggregations on hard substrates such as , boulders, or crevices, while avoiding soft sediments that could destabilize attachment. Abiotic conditions in these habitats include semi-protected wave exposure, optimal salinities of 30–35 ppt, and seasonal temperatures ranging from 10–20°C, though it can experience broader thermal fluctuations up to 28°C before physiological stress like symbiont expulsion occurs. Biotically, A. elegantissima often occurs in mussel beds or barnacle-dominated zones, where its clumped distribution enhances collective defense against competitors and predators. Adaptations supporting this niche include verrucae—adhesive tubercles on the column that facilitate strong attachment to rocks—and the ability to contract into a low-profile, hemispherical form during aerial exposure to minimize desiccation.

Life history

Reproduction

The aggregating anemone, Anthopleura elegantissima, exhibits gonochoric , with individuals developing as either males or females, though rare hermaphrodites have been observed. form in the of the mesenteries and mature progressively from winter through spring and summer, with gonad volume and number increasing in larger individuals. Spawning occurs synchronously within populations during late summer to autumn, coinciding with peak seawater temperatures, when mature gametes are broadcast into the water column through the mouth. Fertilization is external, with and eggs uniting in the to form zygotes that develop into ciliated, planktonic larvae. These larvae remain free-swimming for an extended period before settling on suitable substrates to metamorphose into juvenile polyps. in A. elegantissima occurs primarily through binary longitudinal fission, in which an individual polyp divides along its oral-aboral axis to produce two genetically identical clones, leaving a temporary that heals over weeks. Fission rates are highest from late summer through winter (August to February), often peaking in autumn shortly after sexual spawning, and are less frequent during the rapid growth phase in spring and . This process enables the formation of dense, modular clonal aggregations that can span up to 100 m² and consist of thousands of interconnected polyps, conferring potential to the clone as long as conditions permit continued division. The population maintains an approximately 1:1 sex ratio among mature individuals, supporting effective sexual reproduction. Each reproductive polyp produces numerous gametes annually, with fecundity scaling positively with body size due to increased gonad numbers.

Growth and development

The planula larva of Anthopleura elegantissima develops from the zygote as a planktonic stage measuring 150–250 μm in length, featuring an apical tuft of cilia approximately 60–75 μm long. These larvae exhibit a lobed morphology in some cases and can persist for 2–3 weeks before settling on suitable rocky substrates in the intertidal zone, where they undergo metamorphosis. Metamorphosis involves the formation of tentacles, septa, and pharynx at the aboral end, transforming the larva into a small primary polyp attached by its pedal disc. In the juvenile phase, the primary polyp grows primarily through tissue expansion, increasing in oral disc from less than 1 cm to 2–3 cm over the first one to two years post-settlement. Growth is supported by nutrient uptake and, in symbiotic individuals, contributions from endosymbiotic , with higher rates observed under illuminated conditions and regular feeding regimes that yield up to several percent weight increase monthly. Once attaining a of approximately 2–3 cm, juveniles initiate longitudinal fission, a process involving muscular elongation and transverse division that produces genetically identical daughter polyps. Colony development proceeds as the clonal polyps, capable of slow migration via pedal disc locomotion, come into contact and fuse at their basal tissues, establishing interconnected aggregations. This fusion occurs at the growing edges of expanding groups, allowing the formation of dense, clonal mats up to several in , where polyps remain physically associated but retain individual identities. Such aggregations expand radially through ongoing fission at the periphery, with peripheral polyps migrating outward to fill gaps or extend the boundary. Expansion is modulated by nutrient availability, prey capture efficiency, and symbiotic contributions that enhance overall accumulation. The clonal lineage exhibits potential immortality through continuous asexual fission, which produces new genetically identical polyps and maintains colony integrity, while individual polyps have a lifespan of approximately 2-3 years. While undisturbed colonies can persist for several decades.

Natural history

Photosynthetic symbiosis

The aggregating anemone, Anthopleura elegantissima, maintains a mutualistic relationship with endosymbiotic photosynthetic algae residing in its gastrodermal cells, primarily dinoflagellates of the genus Symbiodinium (zooxanthellae) and chlorophytes known as zoochlorellae. Specifically, it hosts Breviolum muscatinei (formerly Symbiodinium muscatinei), which is widespread along its range, and S. californium, which is restricted to central and southern California populations. The zoochlorellae are identified as Elliptochloris marina. These symbionts enable the anemone to derive a significant portion of its nutritional needs through photosynthesis, enhancing its survival in nutrient-limited intertidal environments. Latitudinal gradients influence the dominant symbiont type, with zoochlorellae (E. marina) predominating in higher-latitude populations from to , where cooler temperatures and lower light levels favor their physiology. In contrast, dinoflagellate symbionts ( spp.) are more prevalent in southern ranges, from to , aligning with warmer conditions and higher . This distribution reflects adaptive specialization, as zoochlorellae exhibit greater tolerance to low-light and cold-stress conditions compared to their dinoflagellate counterparts. Mixed symbioses occur in transitional zones, allowing flexibility in response to environmental variability. In this symbiosis, the perform to produce carbohydrates and oxygen, supplying 40-80% of the 's respiratory energy demands, with higher contributions in low-intertidal, light-exposed individuals. The host reciprocates by providing for , inorganic nutrients, and optimal positioning for exposure through behavioral adjustments like tentacle expansion. The presence of these symbionts imparts the characteristic green pigmentation to the 's tissues via ; aposymbiotic individuals, lacking algae, appear pale or white, particularly in shaded conditions. Under environmental stress such as elevated or reduced , the regulates symbiont density by expelling excess or damaged cells, a process akin to bleaching that helps maintain physiological balance but can reduce photosynthetic capacity if prolonged.

Territorial agonism

Aggregating anemones (Anthopleura elegantissima) exhibit territorial through a sophisticated allorecognition system that allows clonal polyps to distinguish between (syngeneic) and non-self (allogeneic) tissues. This recognition is mediated by genetically determined chemical markers on the surface membranes of epithelial cells, enabling polyps to identify non-clonemates with high specificity. Upon tentacular contact with non-kin, the system triggers an aggressive response exclusively toward allogeneic individuals, while syngeneic tissues elicit no reaction, preventing unnecessary intra-clonal conflict. This clone-specific discrimination ensures that aggression is directed only at potential competitors from other genetic lineages, promoting the integrity of individual colonies. The primary fighting mechanism involves the deployment of acrorhagi, specialized bulbous tentacles located around the column base, which are inflated and used to sting rivals. These acrorhagi contain holotrichous nematocysts that discharge upon contact, adhering to the opponent's tissue and injecting toxins such as phospholipases A2 (PLA2s) and cytolysins, which cause localized tissue by forming pores in cell membranes. The stinging action leads to the detachment of toxic "peels" from the acrorhagi, resulting in scarring and retreat or death of the attacked polyp if escape is not possible. This process is activated by "not-self" chemical signals detected during inter-polyp encounters, distinguishing it from nematocyst use in prey capture or predator defense. Territorial boundaries between colonies are maintained as distinct "war zones" or barren strips, typically 2-4 cm wide, where aggressive interactions prevent overlap and expansion into rival territory. Colonies expand through longitudinal fission of polyps, but boundary polyps, often specialized "warriors" with more acrorhagi, actively repel intruders to secure space. Fights intensify during low tide exposure when polyps are fully expanded and mobile, increasing contact opportunities and leading to multipolyp battles or directed attacks. Over time, repeated encounters can result in habituation, reducing aggression frequency and stabilizing boundaries, or sensitization, escalating attacks in some pairings. Outcomes of these agonistic interactions favor clones with superior fighting abilities, such as those possessing more acrorhagi or transitive hierarchies, allowing victors to monopolize space and resources like light and prey in dense intertidal aggregations. Losing polyps retreat or suffer necrosis-induced mortality, with observed deaths reinforcing clonal separation. This territorial behavior provides an evolutionary advantage by enhancing resource monopolization and preventing parasitic fusion with non-kin, thereby maintaining genetic purity and competitive fitness in crowded habitats. In turn, the inability of polyps to accurately assess opponent strength promotes clonal coexistence and diversity across populations.

Ecology

Predators

The aggregating anemone (Anthopleura elegantissima) faces predation primarily from specialized and that have evolved resistance to its nematocysts, the stinging cells used for defense and prey capture. Among the most significant predators is the Aeolidia papillosa, which selectively feeds on the anemone's tentacles, often targeting smaller colonies and capable of decimating entire aggregations in high-density outbreaks. This predator sequesters the anemone's nematocysts into its own for defense against secondary threats, rendering the anemone's primary weapon ineffective against it. In response to A. papillosa attacks, A. elegantissima exhibits defensive behaviors such as rapid tentacle retraction and column inflation to deter further contact, though these mechanisms provide limited protection once the has initiated feeding. Sea stars, particularly the leather star (Dermasterias imbricata), pose another major threat by everting their stomachs to consume entire polyps, including both small and larger individuals, due to their thick, mucus-covered epidermis that resists nematocyst penetration. Laboratory observations confirm D. imbricata's preference for A. elegantissima over other intertidal prey, contributing to localized population declines in rocky habitats. This predation can also release viable symbiotic from the anemone's tissues, potentially influencing algal dispersal in the ecosystem. The mosshead sculpin (Clinocottus globiceps), a common , opportunistically nibbles on the 's tentacles, showing a preference for those hosting certain algal symbionts and feeding more aggressively on smaller polyps. This selective predation occurs primarily in shallow intertidal zones, where sculpins make repeated body contact with the anemone despite nematocyst stings, highlighting their tolerance to . Occasional predation by birds, such as shorebirds pecking at exposed polyps during , and scavenging on detached or weakened individuals adds minor pressure, with juveniles and isolated anemones proving more vulnerable than established colonies. Overall, the anemone's colony-forming habit offers some deterrence, as larger aggregations intimidate generalist predators through sheer mass and synchronized stinging, though predators like nudibranchs and sea stars bypass these defenses effectively.

Environmental threats

The aggregating anemone (Anthopleura elegantissima) faces several environmental threats, primarily from climate change and anthropogenic activities, which can disrupt its intertidal habitats along the Pacific coast of North America. Ocean acidification, driven by increased atmospheric CO₂ absorption, has shown mixed but generally non-negative effects on this species. Studies indicate that prolonged exposure to elevated CO₂ levels (e.g., pH 7.3, equivalent to 231 Pa pCO₂) promotes growth in its symbiotic algae Breviolum muscatinei, with higher mitotic indices and increased photosynthetic rates (up to 3.30 µmol O₂ g⁻¹ h⁻¹ after six weeks) compared to ambient conditions, without significant changes in anemone mass or overall fitness. Non-calcifying anthozoans like A. elegantissima exhibit physiological plasticity that preserves the metabolic balance between host and symbionts under moderate acidification (pH down to 7.4), though extreme levels (pH 6.8) lead to symbiosis breakdown and host mortality in related species. Laboratory experiments suggest that A. elegantissima may thrive under hypercapnia, with enhanced symbiont density and productivity maintaining or improving host energy budgets. Rising temperatures pose a more direct risk, particularly through on the photosynthetic . Elevated temperatures above 28°C induce symbiont expulsion, leading to bleaching similar to that observed in corals, as anemones from both A. elegantissima and the related A. xanthogrammica lose significant portions of their algal populations under acute exposure. While the demonstrates broad tolerance (surviving up to 30°C in gradual increases), southern populations in warmer regions like are at higher risk from marine heatwaves, which exacerbate and reduce colony fitness. Recent priming studies (2023) show that short-term heat acclimation can enhance resilience in early life stages, but repeated events still impair recovery and increase mortality. Pollution from introduces multiple stressors, including hyposalinity, toxins, and , which fragment and directly harm A. elegantissima populations. events reduce to levels below 25 ppt, triggering bleaching through symbiont expulsion and altering anemone distribution in affected intertidal zones, with recovery taking weeks to months. exposure (at concentrations of 10⁴–10⁵ particles L⁻¹) reduces heterotrophic feeding efficiency and symbiont photosynthetic capacity, leading to slower growth (measured by oral disc ) over 18–30 days. Pesticides from coastal runoff, detected in waters, cause behavioral changes such as increased retraction, potentially limiting prey capture and increasing vulnerability. Coastal development exacerbates loss by fragmenting rocky substrates through armoring and , reducing available intertidal space for anemone aggregations. The conservation status of A. elegantissima remains unlisted globally, with a NatureServe rank of GNR (not ranked) and no evaluation under the , indicating it is not currently considered endangered (as of November 2025). However, local declines have been documented in polluted sites near urban outflows, where multi-stressor effects (e.g., combined low , elevated temperature, and hyposalinity from runoff) reduce colony fitness and . Post-2020 , including 2023 experiments on priming and 2025 studies on impacts, underscores the need for monitoring these interactive threats to prevent broader population shifts.

References

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