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Mycorrhiza
Mycorrhiza
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Many conspicuous fungi such as the fly agaric (upper left) form ectomycorrhiza (upper right) with tree rootlets. Arbuscular mycorrhiza (lower left) are very common in plants, including crop species such as wheat (lower right)
Introductory video animation providing some basic information about mycorrhizas.

A mycorrhiza (from Ancient Greek μύκης (múkēs) 'fungus' and ῥίζα (rhíza) 'root'; pl.mycorrhizae, mycorrhiza, or mycorrhizas)[1] is a symbiotic association between a fungus and a plant.[2] The term mycorrhiza refers to the role of the fungus in the plant's rhizosphere, the plant root system and its surroundings. Mycorrhizae play important roles in plant nutrition, soil biology, and soil chemistry.

In a mycorrhizal association, the fungus colonizes the host plant's root tissues, either intracellularly as in arbuscular mycorrhizal fungi, or extracellularly as in ectomycorrhizal fungi.[3] The association is normally mutualistic. In particular species, or in particular circumstances, mycorrhizae may have a parasitic association with host plants.[4]

Definition

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A mycorrhiza is a symbiotic association between a green plant and a fungus. The plant makes organic molecules by photosynthesis and supplies them to the fungus in the form of sugars or lipids, while the fungus supplies the plant with water and mineral nutrients, such as phosphorus, taken from the soil. Mycorrhizas are located in the roots of vascular plants, but mycorrhiza-like associations also occur in bryophytes[5] and there is fossil evidence that early land plants that lacked roots formed arbuscular mycorrhizal associations.[6] Most plant species form mycorrhizal associations, though some families like Brassicaceae and Chenopodiaceae cannot. Different forms for the association are detailed in the next section. The most common is the arbuscular type that is present in 70% of plant species, including many crop plants such as cereals and legumes.[7]

Evolution

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Emergence alongside terrestrial plants

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Fossil and genetic evidence indicate that mycorrhizae emerged as early as 450-500 million years ago, potentially between fungus-like protists and algae. Arbuscular mycorrhizal relationships appeared earliest, coinciding with the terrestrialization of plants.[8] Genetic evidence indicates that all land plants share a single common ancestor,[9] which appears to have quickly adopted mycorrhizal symbiosis, and research suggests that proto-mycorrhizal fungi were a key factor enabling plant terrestrialization.[10] There is a strong consensus among paleomycologists that mycorrhizal fungi served as a primitive root system for early terrestrial plants.[11] This is because, prior to plant colonization of land, soils were nutrient sparse and plants had yet to develop root systems. Without complex root systems, early terrestrial plants would have been incapable of absorbing recalcitrant ions from mineral substrates, such as phosphate, a key nutrient for plant growth.[12]

Fossil record and genomic analysis

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The 400 million year old Rhynie chert contains an assemblage of fossil plants preserved in sufficient detail that arbuscular mycorrhizae have been observed in the stems of Aglaophyton major, giving a lower bound for how recently arbuscular mycorrhizal symbiosis may have developed.[6] The earliest root-confined arbuscular mycorrhizae observed come from a fossil where hyphae are seen colonizing the rootlet of an arborescent clubmoss, forming arbuscules.[13]

Ectomycorrhizae developed substantially later, during the Jurassic period, while most other modern forms of mycorrhizal symbiosis, including orchid and ericoid mycorrhizae, date to the period of angiosperm radiation in the Cretaceous period.[14] The earliest confirmed ectomycorrhizal fossil dates back to the Eocene approximately 48 million years ago,[15] However, it is believed that the first ectomycorrhizal relationships evolved in the stem group Pinaceae around the radiation of the Pinaceae crown group in the mid Jurassic, 175 million or so years ago.[16]

Ericoid mycorrhizae have the most recent evolutionary origins of mycorrhizal types, evolving around 118 million years ago from free-living saprotrophic ancestors.[17] Ericoid mycorrhizal fungi evolved from multiple lineages of fungi, primarily ascomycetes from the Leotiomycetes, as well as basidiomycetes from the family Serendipitaceae.[18]

Origins in plants

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In plants, the genes for forming mycorrhizal symbiosis are highly conserved and originate from a common ancestor, meaning that the ability to form mycorrhizae is ancestral to all land plants.[19] Non-mycorrhizal plant lineages, such as the Brassicaceae, lost the ability to form mycorrhizae at some point in their evolution. [20] The earliest mycorrhizae were arbuscular mycorrhizae, and other forms, such as ectomycorrhizae and orchid mycorrhizae, evolved when plant hosts switched from symbiosis with Glomeromycotina to symbiosis with different fungal lineages.[21]

There is genetic evidence that the symbiosis between legumes and nitrogen-fixing bacteria is derived from mycorrhizal symbiosis.[22] The modern distribution of mycorrhizal fungi appears to reflect an increasing complexity and competition in root morphology associated with the dominance of angiosperms in the Cenozoic Era, characterized by complex ecological dynamics between species.[23]

Origins in fungi

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In fungi, mycorrhizal symbiosis had multiple independent origins among different lineages of fungi. Arbuscular mycorrhizal fungi form their own monophyletic phylum, whereas other mycorrhizal fungi convergently evolved similar lifestyles.

Arbuscular mycorrhizae

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The phylum Glomeromycota, which forms the arbuscular mycorrhizal symbiosis, is the oldest mycorrhizal lineage. The arbuscular mycorrhizal symbiosis evolved only once in fungi; all arbuscular mycorrhizal fungi belong to Glomeromycota and share a common ancestor.[24] 244 species have been identified based on differences in the appearance of their spores, but genetic studies suggest that 300-1600 species may exist in Glomeromycota.[25] All members of Glomeromycota are obligate biotrophs, entirely dependent upon their plant hosts for survival.[26] Arbuscular mycorrhizal fungi are considered to be generalists, with minimal host plant specificity. AM symbiosis has been observed in almost every seed plant taxonomic division, or around 67% of species.[27] Arbuscular mycorrhizae take on most angiosperms, some gymnosperms, pteridophytes, and nonvascular plants as plant hosts.[28] Arbuscular mycorrhizae have been observed in the seedling stage of otherwise ectomycorrhizal partners, suggesting that arbuscular mycorrhizal fungi may be able to infect almost any land plant given proper circumstances.[29]

Other forms of mycorrhizal symbiosis, such as ectomycorrhizae, orchid mycorrhizae, and ericoid mycorrhizae, emerged multiple times in different lineages of fungi through convergent evolution. Unlike arbuscular mycorrhizal fungi, some of these fungi are only facultatively symbiotic, and can live by themselves without a plant host under some conditions.

Ectomycorrhizae

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Ectomycorrhizal fungi evolved from free-living saprotrophs, mostly in Basidiomycota and Ascomycota, and some became dependent on plant hosts when they lost genes necessary for decaying lignin and other plant materials.[30] There are 20,000 to 25,000 species of ectomycorrhizal fungi, but only 6,000 to 7,000 plant species that form ectomycorrhizal symbiosis.[31] In angiosperms, it is believed that ectomycorrhizal partnerships have developed independently at least 18 times, and in fungi, around 80 times.[32][33] The main evolutionary driver for ectomycorrhizae is switching of nutritional modes from saprotrophs.[34] Phylogenomic analysis of various ectomycorrhizal fungal genomes has confirmed the convergent evolution of ectomycorrhizal fungi from white and brown-rot fungi, as well as from soil saprotrophs.[35][36] Some lineages of ectomycorrhizae have likely evolved from endophytic ancestors, fungi that live within plants without damaging them.[37] Some ectomycorrhizal fungi have gone through apparent evolutionary reversal back into saprotrophic ecology. This is possible because some lineages of ectomycorrhizal fungi retain enzymes for breaking down lignin.[38]

Orchid mycorrhizae

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Orchid mycorrhizal fungi, which mostly originate from Ascomycota and Basidiomycota, are less understood. Some fungi that participate in orchid mycorrhizal symbiosis can also form ectomycorrhizal symbiosis with other plants, or live independently of a plant host. Some orchid mycorrhizal fungi can also live as plant pathogens.[39][40]

Ericoid mycorrhizae

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Ericoid mycorrhizal associations have the most recent origins and the lowest species richness among both plant and fungal partners.[41] This specialization suggests that ericoid mycorrhizal partners evolved in parallel with one another in response to environmental change, rather than through reciprocal species-to-species level selection.[42] Ericoid mycorrhizal relationships are found in extremely nutrient poor soils in the northern and southern hemispheres.[43] These environments of low mineral nutrient availability have led to native plants developing sclerophylly, where plants become high in lignin and low in phosphorus and nitrogen.[44] As a result, decaying plant matter in these areas has an abnormally high carbon to nitrogen ratio, making it resistant to microbial decay. Ericoid mycorrhizae have apparently evolved to conserve minerals in nutrient deficient sclerophyllous litter by directly cycling these nutrients throughout the mycorrhiza system.[45] Ericoid mycorrhizae also retain saprotrophic abilities, allowing them to extract nitrogen and phosphorus from unmineralized organic material, and resist negative outcomes from high concentrations of toxic cations in the acidic soil environment.[46]

Types

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The mycorrhizal lifestyle has independently convergently evolved multiple times in the history of Earth.[47] There are multiple ways to categorize mycorrhizal symbiosis. The largest division is between ectomycorrhizas and endomycorrhizas. The two types are differentiated by the fact that the hyphae of ectomycorrhizal fungi do not penetrate individual cells within the root, while the hyphae of endomycorrhizal fungi penetrate the cell wall and invaginate the cell membrane.[48][49]

Similar symbiotic relationships

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Some forms of plant-fungal symbiosis are similar to mycorrhizae, but considered distinct. One example is fungal endophytes. Endophytes are defined as organisms that can live within plant cells without causing harm to the plant. They are distinguishable from mycorrhizal fungi by the absence of nutrient-transferring structures for bringing in nutrients from outside the plant.[47] Some lineages of mycorrhizal fungi may have evolved from endophytes into mycorrhizal fungi,[50] and some fungi can live as mycorrhizae or as endophytes.

Ectomycorrhiza

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Beech is ectomycorrhizal
Leccinum aurantiacum, an ectomycorrhizal fungus

Ectomycorrhizae are distinct in that they do not penetrate into plant cells, but instead form a structure called a Hartig net that penetrates between cells.[51] Ectomycorrhizas consist of a hyphal sheath, or mantle, covering the root tip and the Hartig net of hyphae surrounding the plant cells within the root cortex. In some cases the hyphae may also penetrate the plant cells, in which case the mycorrhiza is called an endomycorrhiza. Outside the root, ectomycorrhizal extramatrical mycelium forms an extensive network within the soil and leaf litter. Other forms of mycorrhizae, including arbuscular, ericoid, arbutoid, monotropoid, and orchid mycorrhizas, are considered endomycorrhizae.[52]

Ectomycorrhizas, or EcM, are symbiotic associations between the roots of around 10% of plant families, mostly woody plants including the birch, dipterocarp, eucalyptus, oak, pine, and rose[53] families, orchids,[54] and fungi belonging to the Basidiomycota, Ascomycota, and Zygomycota. Ectomycorrhizae associate with relatively few plant species, only about 2% of plant species on Earth, but the species they associate with are mostly trees and woody plants that are highly dominant in their ecosystems, meaning plants in ectomycorrhizal relationships make up a large proportion of plant biomass.[55] Some EcM fungi, such as many Leccinum and Suillus, are symbiotic with only one particular genus of plant, while other fungi, such as the Amanita, are generalists that form mycorrhizas with many different plants.[56] An individual tree may have 15 or more different fungal EcM partners at one time.[57] While the diversity of plants involved in EcM is low, the diversity of fungi involved in EcM is high. Thousands of ectomycorrhizal fungal species exist, hosted in over 200 genera. A recent study has conservatively estimated global ectomycorrhizal fungal species richness at approximately 7750 species, although, on the basis of estimates of knowns and unknowns in macromycete diversity, a final estimate of ECM species richness would probably be between 20,000 and 25,000.[58] Ectomycorrhizal fungi evolved independently from saprotrophic ancestors many times in the group's history.[59]

Nutrients can be shown to move between different plants through the fungal network. Carbon has been shown to move from paper birch seedlings into adjacent Douglas-fir seedlings, although not conclusively through a common mycorrhizal network,[60] thereby promoting succession in ecosystems.[61] The ectomycorrhizal fungus Laccaria bicolor has been found to lure and kill springtails to obtain nitrogen, some of which may then be transferred to the mycorrhizal host plant. In a study by Klironomos and Hart, Eastern White Pine inoculated with L. bicolor was able to derive up to 25% of its nitrogen from springtails.[62][63] When compared with non-mycorrhizal fine roots, ectomycorrhizae may contain very high concentrations of trace elements, including toxic metals (cadmium, silver) or chlorine.[64]

The first genomic sequence for a representative of symbiotic fungi, the ectomycorrhizal basidiomycete L. bicolor, was published in 2008.[65] An expansion of several multigene families occurred in this fungus, suggesting that adaptation to symbiosis proceeded by gene duplication. Within lineage-specific genes those coding for symbiosis-regulated secreted proteins showed an up-regulated expression in ectomycorrhizal root tips suggesting a role in the partner communication. L. bicolor is lacking enzymes involved in the degradation of plant cell wall components (cellulose, hemicellulose, pectins and pectates), preventing the symbiont from degrading host cells during the root colonisation. By contrast, L. bicolor possesses expanded multigene families associated with hydrolysis of bacterial and microfauna polysaccharides and proteins. This genome analysis revealed the dual saprotrophic and biotrophic lifestyle of the mycorrhizal fungus that enables it to grow within both soil and living plant roots. Since then, the genomes of many other ectomycorrhizal fungal species have been sequenced further expanding the study of gene families and evolution in these organisms.[66]

Arbutoid mycorrhiza

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This type of mycorrhiza involves plants of the Ericaceae subfamily Arbutoideae. It is however different from ericoid mycorrhiza and resembles ectomycorrhiza, both functionally and in terms of the fungi involved.[67] It differs from ectomycorrhiza in that some hyphae actually penetrate into the root cells, making this type of mycorrhiza an ectendomycorrhiza.[68]

Arbuscular mycorrhiza

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Wheat has arbuscular mycorrhiza.

Arbuscular mycorrhizas, (formerly known as vesicular-arbuscular mycorrhizas), have hyphae that penetrate plant cells, producing branching, tree-like structures called arbuscules within the plant cells for nutrient exchange. Often, balloon-like storage structures, termed vesicles, are also produced. In this interaction, fungal hyphae do not in fact penetrate the protoplast (i.e. the interior of the cell), but invaginate the cell membrane, creating a so-called peri-arbuscular membrane. The structure of the arbuscules greatly increases the contact surface area between the hypha and the host cell cytoplasm to facilitate the transfer of nutrients between them. Arbuscular mycorrhizas are obligate biotrophs, meaning that they depend upon the plant host for both growth and reproduction; they have lost the ability to sustain themselves by decomposing dead plant material.[69] Twenty percent of the photosynthetic products made by the plant host are consumed by the fungi, the transfer of carbon from the terrestrial host plant is then exchanged by equal amounts of phosphate from the fungi to the plant host.[70]

Contrasting with the pattern seen in ectomycorrhizae, the species diversity of AMFs is very low, but the diversity of plant hosts is very high; an estimated 78% of all plant species associate with AMFs.[55] Arbuscular mycorrhizas are formed only by fungi in the division Glomeromycota. Fossil evidence[6] and DNA sequence analysis[71] suggest that this mutualism appeared 400-460 million years ago, when the first plants were colonizing land. Arbuscular mycorrhizas are found in 85% of all plant families, and occur in many crop species.[53] The hyphae of arbuscular mycorrhizal fungi produce the glycoprotein glomalin, which may be one of the major stores of carbon in the soil.[72] Arbuscular mycorrhizal fungi have (possibly) been asexual for many millions of years and, unusually, individuals can contain many genetically different nuclei (a phenomenon called heterokaryosis).[73]

Mucoromycotina fine root endophytes

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Mycorrhizal fungi belonging to Mucoromycotina, known as "fine root endophytes" (MFREs), were mistakenly identified as arbuscular mycorrhizal fungi until recently. While similar to AMF, MFREs are from subphylum Mucoromycotina instead of Glomeromycotina. Their morphology when colonizing a plant root is very similar to AMF, but they form fine textured hyphae.[51] Effects of MFREs may have been mistakenly attributed to AMFs due to confusion between the two, complicated by the fact that AMFs and MFREs often colonize the same hosts simultaneously. Unlike AMFs, they appear capable of surviving without a host. This group of mycorrhizal fungi is little understood, but appears to prefer wet, acidic soils and forms symbiotic relationships with liverworts, hornworts, lycophytes, and angiosperms.[74]

Ericoid mycorrhiza

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An ericoid mycorrhizal fungus isolated from Woollsia pungens[75]

Ericoid mycorrhizae, or ErMs, involve only plants in Ericales and are the most recently evolved of the major mycorrhizal relationships. Plants that form ericoid mycorrhizae are mostly woody understory shrubs; hosts include blueberries, bilberries, cranberries, mountain laurels, rhododendrons, heather, neinei, and giant grass tree. ErMs are most common in boreal forests, but are found in two-thirds of all forests on Earth.[55] Ericoid mycorrhizal fungi belong to several different lineages of fungi. Some species can live as endophytes entirely within plant cells even within plants outside the Ericales, or live independently as saprotrophs that decompose dead organic matter. This ability to switch between multiple lifestyle types makes ericoid mycorrhizal fungi very adaptable.[47]

Plants that participate in these symbioses have specialized roots with no root hairs, which are covered with a layer of epidermal cells that the fungus penetrates into and completely occupies.[51] The fungi have a simple intraradical (growth in cells) phase, consisting of dense coils of hyphae in the outermost layer of root cells. There is no periradical phase and the extraradical phase consists of sparse hyphae that don't extend very far into the surrounding soil. They might form sporocarps (probably in the form of small cups), but their reproductive biology is poorly understood.[49]

Plants participating in ericoid mycorrhizal symbioses are found in acidic, nutrient-poor conditions.[47] Whereas AMFs have lost their saprotrophic capabilities, and EcM fungi have significant variation in their ability to produce enzymes needed for a saprotrophic lifestyle,[55] fungi involved in ErMs have fully retained the ability to decompose plant material for sustenance. Some ericoid mycorrhizal fungi have actually expanded their repertoire of enzymes for breaking down organic matter. They can extract nitrogen from cellulose, hemicellulose, lignin, pectin, and chitin. This would increase the benefit they can provide to their plant symbiotic partners.[76]

Orchid mycorrhiza

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All orchids are myco-heterotrophic at some stage during their lifecycle, meaning that they can survive only if they form orchid mycorrhizae. Orchid seeds are so small that they contain no nutrition to sustain the germinating seedling, and instead must gain the energy to grow from their fungal symbiont.[51] The OM relationship is asymmetric; the plant seems to benefit more than the fungus, and some orchids are entirely mycoheterotrophic, lacking chlorophyll for photosynthesis. It is actually unknown whether fully autotrophic orchids that do not receive some of their carbon from fungi exist or not.[77] Like fungi that form ErMs, OM fungi can sometimes live as endophytes or as independent saprotrophs. In the OM symbiosis, hyphae penetrate into the root cells and form pelotons (coils) for nutrient exchange.

Monotropoid mycorrhiza

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This type of mycorrhiza occurs in the subfamily Monotropoideae of the Ericaceae, as well as several genera in the Orchidaceae. These plants are heterotrophic or mixotrophic and derive their carbon from the fungus partner. This is thus a non-mutualistic, parasitic type of mycorrhizal symbiosis.[citation needed]

Function

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Nutrient exchanges and communication between a mycorrhizal fungus and plants.

Mycorrhizal fungi form a mutualistic relationship with the roots of most plant species. In such a relationship, both the plants themselves and those parts of the roots that host the fungi, are said to be mycorrhizal. Relatively few of the mycorrhizal relationships between plant species and fungi have been examined to date, but 95% of the plant families investigated are predominantly mycorrhizal either in the sense that most of their species associate beneficially with mycorrhizae, or are absolutely dependent on mycorrhizae. The Orchidaceae are notorious as a family in which the absence of the correct mycorrhizae is fatal even to germinating seeds.[78]

Recent research into ectomycorrhizal plants in boreal forests has indicated that mycorrhizal fungi and plants have a relationship that may be more complex than simply mutualistic. This relationship was noted when mycorrhizal fungi were unexpectedly found to be hoarding nitrogen from plant roots in times of nitrogen scarcity. Researchers argue that some mycorrhizae distribute nutrients based upon the environment with surrounding plants and other mycorrhizae. They go on to explain how this updated model could explain why mycorrhizae do not alleviate plant nitrogen limitation, and why plants can switch abruptly from a mixed strategy with both mycorrhizal and nonmycorrhizal roots to a purely mycorrhizal strategy as soil nitrogen availability declines.[79] It has also been suggested that evolutionary and phylogenetic relationships can explain much more variation in the strength of mycorrhizal mutualisms than ecological factors.[80]

Within mycorrhiza, the plant gives carbohydrates (products of photosynthesis) to the fungus, while the fungus gives the plant water and minerals.

Formation

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To successfully engage in mutualistic symbiotic relationships with other organisms, such as mycorrhizal fungi and any of the thousands of microbes that colonize plants, plants must discriminate between mutualists and pathogens, allowing the mutualists to colonize while activating an immune response towards the pathogens. Plant genomes code for potentially hundreds of receptors for detecting chemical signals from other organisms. Plants dynamically adjust their symbiotic and immune responses, changing their interactions with their symbionts in response to feedbacks detected by the plant.[81] In plants, the mycorrhizal symbiosis is regulated by the common symbiosis signaling pathway (CSSP), a set of genes involved in initiating and maintaining colonization by endosymbiotic fungi and other endosymbionts such as Rhizobia in legumes. The CSSP has origins predating the colonization of land by plants, demonstrating that the co-evolution of plants and arbuscular mycorrhizal fungi is over 500 million years old.[82] In arbuscular mycorrhizal fungi, the presence of strigolactones, a plant hormone, secreted from roots induces fungal spores in the soil to germinate, stimulates their metabolism, growth and branching, and prompts the fungi to release chemical signals the plant can detect.[83] Once the plant and fungus recognize one another as suitable symbionts, the plant activates the common symbiotic signaling pathway, which causes changes in the root tissues that enable the fungus to colonize.[84]

Experiments with arbuscular mycorrhizal fungi have identified numerous chemical compounds to be involved in the "chemical dialog" that occurs between the prospective symbionts before symbiosis is begun. In plants, almost all plant hormones play a role in initiating or regulating AMF symbiosis, and other chemical compounds are also suspected to have a signaling function. While the signals emitted by the fungi are less understood, it has been shown that chitinaceous molecules known as Myc factors are essential for the formation of arbuscular mycorrhizae. Signals from plants are detected by LysM-containing receptor-like kinases, or LysM-RLKs. AMF genomes also code for potentially hundreds of effector proteins, of which only a few have a proven effect on mycorrhizal symbiosis, but many others likely have a function in communication with plant hosts as well.[85]

Many factors are involved in the initiation of mycorrhizal symbiosis, but particularly influential is the plant's need for phosphorus. Experiments involving rice plants with a mutation disabling their ability to detect P starvation show that arbuscular mycorrhizal fungi detection, recruitment and colonization is prompted when the plant detects that it is starved of phosphorus.[86] Nitrogen starvation also plays a role in initiating AMF symbiosis.[87]

Mechanisms

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The mechanisms by which mycorrhizae increase absorption include some that are physical and some that are chemical. Physically, most mycorrhizal mycelia are much smaller in diameter than the smallest root or root hair, and thus can explore soil material that roots and root hairs cannot reach, and provide a larger surface area for absorption. Chemically, the cell membrane chemistry of fungi differs from that of plants. For example, they may secrete organic acids that dissolve or chelate many ions, or release them from minerals by ion exchange.[88] Mycorrhizae are especially beneficial for the plant partner in nutrient-poor soils.[89]

Sugar-water/mineral exchange

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In this mutualism, fungal hyphae (E) increase the surface area of the root and uptake of key nutrients while the plant supplies the fungi with fixed carbon (A=root cortex, B=root epidermis, C=arbuscle, D=vesicle, F=root hair, G=nuclei).

The mycorrhizal mutualistic association provides the fungus with relatively constant and direct access to carbohydrates, such as glucose and sucrose.[90] The carbohydrates are translocated from their source (usually leaves) to root tissue and on to the plant's fungal partners. In return, the plant gains the benefits of the mycelium's higher absorptive capacity for water and mineral nutrients, partly because of the large surface area of fungal hyphae, which are much longer and finer than plant root hairs, and partly because some such fungi can mobilize soil minerals unavailable to the plants' roots. The effect is thus to improve the plant's mineral absorption capabilities.[91]

Unaided plant roots may be unable to take up nutrients that are chemically or physically immobilised; examples include phosphate ions and micronutrients such as iron. One form of such immobilization occurs in soil with high clay content, or soils with a strongly basic pH. The mycelium of the mycorrhizal fungus can, however, access many such nutrient sources, and make them available to the plants they colonize.[92] Thus, many plants are able to obtain phosphate without using soil as a source. Another form of immobilisation is when nutrients are locked up in organic matter that is slow to decay, such as wood, and some mycorrhizal fungi act directly as decay organisms, mobilising the nutrients and passing some onto the host plants; for example, in some dystrophic forests, large amounts of phosphate and other nutrients are taken up by mycorrhizal hyphae acting directly on leaf litter, bypassing the need for soil uptake.[93] Inga alley cropping, an agroforestry technique proposed as an alternative to slash and burn rainforest destruction,[94] relies upon mycorrhiza within the root system of species of Inga to prevent the rain from washing phosphorus out of the soil.[95]

In some more complex relationships, mycorrhizal fungi do not just collect immobilised soil nutrients, but connect individual plants together by mycorrhizal networks that transport water, carbon, and other nutrients directly from plant to plant through underground hyphal networks.[96]

Suillus tomentosus, a basidiomycete fungus, produces specialized structures known as tuberculate ectomycorrhizae with its plant host lodgepole pine (Pinus contorta var. latifolia). These structures have been shown to host nitrogen fixing bacteria which contribute a significant amount of nitrogen and allow the pines to colonize nutrient-poor sites.[97]


Disease, drought and salinity resistance and its correlation to mycorrhizae

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Mycorrhizal plants are often more resistant to diseases, such as those caused by microbial soil-borne pathogens. These associations have been found to assist in plant defense both above and belowground. Mycorrhizas have been found to excrete enzymes that are toxic to soil borne organisms such as nematodes.[98] More recent studies have shown that mycorrhizal associations result in a priming effect of plants that essentially acts as a primary immune response. When this association is formed a defense response is activated similarly to the response that occurs when the plant is under attack. As a result of this inoculation, defense responses are stronger in plants with mycorrhizal associations.[99] Ecosystem services provided by mycorrhizal fungi may depend on the soil microbiome.[100] Furthermore, mycorrhizal fungi was significantly correlated with soil physical variable, but only with water level and not with aggregate stability[101][102] and can lead also to more resistant to the effects of drought.[103][104][105] Moreover, the significance of mycorrhizal fungi also includes alleviation of salt stress and its beneficial effects on plant growth and productivity. Although salinity can negatively affect mycorrhizal fungi, many reports show improved growth and performance of mycorrhizal plants under salt stress conditions.[106]

Resistance to insects

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Plants connected by mycorrhizal fungi in mycorrhizal networks can use these underground connections to communicate warning signals.[107][108] For example, when a host plant is attacked by an aphid, the plant signals surrounding connected plants of its condition. Both the host plant and those connected to it release volatile organic compounds that repel aphids and attract parasitoid wasps, predators of aphids.[107] This assists the mycorrhizal fungi by conserving its food supply.[107]

Colonization of barren soil

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Plants grown in sterile soils and growth media often perform poorly without the addition of spores or hyphae of mycorrhizal fungi to colonise the plant roots and aid in the uptake of soil mineral nutrients.[109] The absence of mycorrhizal fungi can also slow plant growth in early succession or on degraded landscapes.[110] The introduction of alien mycorrhizal plants to nutrient-deficient ecosystems puts indigenous non-mycorrhizal plants at a competitive disadvantage.[111] This aptitude to colonize barren soil is defined by the category Oligotroph.

Resistance to toxicity

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Fungi have a protective role for plants rooted in soils with high metal concentrations, such as acidic and contaminated soils. Pine trees inoculated with Pisolithus tinctorius planted in several contaminated sites displayed high tolerance to the prevailing contaminant, survivorship and growth.[112] One study discovered the existence of Suillus luteus strains with varying tolerance of zinc. Another study discovered that zinc-tolerant strains of Suillus bovinus conferred resistance to plants of Pinus sylvestris. This was probably due to binding of the metal to the extramatricial mycelium of the fungus, without affecting the exchange of beneficial substances.[111]

Occurrence of mycorrhizal associations

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Mycorrhizas are present in 92% of plant families studied (80% of species),[53] with arbuscular mycorrhizas being the ancestral and predominant form,[53] and the most prevalent symbiotic association found in the plant kingdom.[90] The structure of arbuscular mycorrhizas has been highly conserved since their first appearance in the fossil record,[6] with both the development of ectomycorrhizas and the loss of mycorrhizas, evolving convergently on multiple occasions.[53]

Associations of fungi with the roots of plants have been known since at least the mid-19th century. However, early observers simply recorded the fact without investigating the relationships between the two organisms.[113] This symbiosis was studied and described by Franciszek Kamieński in 1879–1882.[114][115]

Climate change

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CO2 released by human activities is causing climate change and possible damage to mycorrhizae, but the direct effect of an increase in the gas should be to benefit plants and mycorrhizae.[116] In Arctic regions, nitrogen and water are harder for plants to obtain, making mycorrhizae crucial to plant growth.[117] Since mycorrhizae tend to do better in cooler temperatures, warming could be detrimental to them.[118] Gases such as SO2, NOx, and O3 produced by human activity may harm mycorrhizae, causing reduction in "propagules, the colonization of roots, degradation in connections between trees, reduction in the mycorrhizal incidence in trees, and reduction in the enzyme activity of ectomycorrhizal roots."[119]

A company in Israel, Groundwork BioAg, has discovered a method of using mycorrhizal fungi to increase agricultural crops while sequestering greenhouse gases and eliminating CO2 from the atmosphere.[120]

Conservation and mapping

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In 2021, the Society for the Protection of Underground Networks was launched. SPUN is a science-based initiative to map and protect the mycorrhizal networks regulating Earth's climate and ecosystems. Its stated goals are mapping, protecting, and harnessing mycorrhizal fungi.

See also

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References

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Revisions and contributorsEdit on WikipediaRead on Wikipedia
from Grokipedia
Mycorrhiza denotes the mutualistic symbiotic relationship between fungi and the roots of vascular , wherein fungal hyphae extend the root system's reach to enhance uptake of and immobile nutrients, such as , in exchange for carbohydrates derived from photosynthesis. These associations, integral to and survival, occur in over 80% of species and underpin productivity by facilitating nutrient cycling and structure maintenance. The primary types include ectomycorrhizae, which form extracellular sheaths and Hartig nets around root tips without penetrating cortical cells, predominantly associating with woody plants like conifers and oaks; and endomycorrhizae, encompassing arbuscular mycorrhizae that intracellularly form arbuscules for nutrient exchange, prevalent in most herbaceous and crop plants. Less common variants, such as ericoid and orchid mycorrhizae, adapt to specific host groups in nutrient-poor or specialized habitats. Empirical studies confirm the mutualistic nature through enhanced plant growth and fungal reproduction under controlled conditions, with disruptions leading to reduced biomass and soil fertility. Mycorrhizae influence broader ecological dynamics, including via extraradical mycelia that stabilize soil aggregates and , and interplant nutrient transfer through common mycelial networks, which can alter competitive hierarchies among . In agricultural contexts, with mycorrhizal propagules boosts yields under low-input conditions by improving efficiency and resilience, underscoring their practical significance beyond natural ecosystems.

Definition and Fundamentals

Definition and Symbiotic Nature

Mycorrhiza denotes the symbiotic association between the of and the of vascular , where the term originates from words mykēs (fungus) and rhiza (). This relationship is predominantly mutualistic, enabling bidirectional nutrient exchange that enhances and fungal carbon acquisition. colonize plant either ectopically, forming a sheath around the cortex, or endophytically, penetrating cortical cells to develop specialized structures such as arbuscules or vesicles. Approximately 80 to 90 percent of engage in such associations, underscoring their prevalence across ecosystems from forests to agricultural fields. In the symbiotic exchange, fungi extend their hyphal networks into the , vastly increasing the absorptive surface area—up to hundreds of times that of hairs alone—and accessing immobile nutrients like and micronutrients in depleted zones beyond reach. Empirical studies demonstrate that this facilitates up to 80 percent of uptake in some mycorrhizal , particularly in -limited s where diffusion rates limit direct absorption. In return, allocate 4 to 20 percent of their photosynthetically fixed carbon, primarily as sugars and , to the via specialized interfaces like arbuscules, fueling fungal growth and . This carbon transfer is regulated by plant- signaling, with disruptions in transporters reducing establishment, as shown in mutants. The mutualistic nature is evidenced by reciprocal benefits: non-mycorrhizal plants exhibit and deficiencies in infertile soils, while mycorrhizal boosts by 20 to 100 percent in controlled experiments across species like and . Fungi also improve by enhancing water uptake through hyphae and potentially modulating hormone signaling. However, can shift toward under high availability or incompatible partners, where fungi drain carbon without commensurate benefits, highlighting context-dependent dynamics grounded in resource gradients. These interactions underpin to nutrient-poor environments, with evidence tracing origins to over 400 million years ago.

Historical Discovery and Terminology

The symbiotic associations between fungi and plant roots, now known as mycorrhizae, were first systematically described in the mid-19th century by European botanists observing morphological changes in . German forest pathologist Albert Bernhard Frank provided the foundational characterization in , reporting widespread fungal colonization of fine roots in and trees during investigations into cultivation commissioned by the Prussian government. Frank distinguished these structures from pathogenic infections, proposing instead a mutually beneficial relationship where fungi enhanced nutrient uptake in exchange for plant-derived carbohydrates, a that contradicted dominant parasitic paradigms of the era. Frank coined the term mycorrhiza—derived from the mýkēs (μύκης, meaning "") and rhíza (ῥίζα, meaning "")—in his 1885 publication Über die Beziehungen der Mikorrhizapilze zu den Wirtspflanzen, applying it specifically to the ectotrophic associations he observed enveloping root tips without penetrating cortical cells. This encapsulated the non-pathogenic, intimate fungal-root interface, emphasizing over mere adjacency. Subsequent researchers, such as Pierre Dangeard in 1896, extended similar terminology to endotrophic forms (now arbuscular mycorrhizae) involving intracellular hyphae and arbuscules in herbaceous plants like poplars. Early terminological distinctions evolved to classify types: "ectomycorrhiza" for external sheaths (from Greek ektos, "outside"), formalized by Frank's followers, and "endomycorrhiza" for internal penetrations, later subdivided into arbuscular, ericoid, and variants based on host specificity and hyphal morphology. These terms reflected empirical observations of anatomical differences, with Frank's original mycorrhiza serving as the umbrella concept for all root-fungus symbioses. By the early 20th century, fossil evidence from strata (circa 315–350 million years ago) corroborated ancient origins, but modern recognition stemmed from Frank's integration of field pathology with symbiotic theory.

Evolution

Ancient Origins

The earliest fossil evidence suggestive of mycorrhizal associations dates to the period, approximately 460 million years ago, where fossilized fungal hyphae and spores from strongly resemble those of modern arbuscular mycorrhizal (AM) fungi within the Glomeromycota phylum. These findings indicate that glomeromycotan-like fungi predated the widespread colonization of land by vascular plants, potentially existing in aquatic or semi-terrestrial environments. However, direct evidence of symbiotic integration with plant roots appears later, in the deposits of , dated to around 407-396 million years ago. In these Devonian fossils, particularly from the early land plant Aglaophyton major (formerly Rhynia gwynne-vaughanii), intracellular fungal structures including arbuscules—diagnostic features of AM symbiosis—have been identified within root-like axes, confirming the presence of functional mycorrhizal associations by this time. Similar vesicular-arbuscular mycorrhizae, characterized by vesicles and arbuscules in cortical cells, occur in other Lower Devonian plant fossils, such as those from concretions, supporting an origin between 462 and 353 million years ago. These ancient AM symbioses likely facilitated nutrient uptake, especially , enabling early to transition from aquatic to terrestrial habitats amid nutrient-poor soils. Phylogenetic and paleontological data align on AM fungi as the ancestral mycorrhizal type, with estimates placing their divergence from other fungi around 500-600 million years ago, though fossil-calibrated trees refine the onset to the Ordovician-Devonian boundary. Ectomycorrhizal (ECM) associations, by contrast, emerged much later, with the oldest ECM fossils from Eocene pine roots around 48.7 million years ago, underscoring the primacy of endomycorrhizal forms in deep history. This timeline posits mycorrhizae as a key innovation in evolution, predating vascular tissues in some lineages and coevolving through three major waves of diversification.

Phylogenetic Development and Co-Evolution

The arbuscular mycorrhizal (AM) symbiosis represents the most ancient form of mycorrhizal association, originating over 450 million years ago during the Ordovician-Devonian transition, contemporaneous with the colonization of land by early vascular . Fossil evidence from the in , dated to approximately 407 million years ago, reveals well-preserved AM-like structures in early land such as Aglaophyton major and Horneophyton lignieri, featuring intracellular hyphal coils and vesicles akin to modern AM fungi in Glomeromycota. Phylogenetically, Glomeromycota form a monophyletic sister to Mucoromycota and Mortierellomycota, with genomic analyses indicating two independent transitions to obligate mutualism predating terrestrial around 475 million years ago; AM fungi exhibit genomic signatures of biotrophy, including the loss of genes (FAS1 and FAS2) and reduced plant cell wall-degrading enzymes, reflecting dependence on host-derived carbon. Co-evolution between AM fungi and plants involved the parallel development of conserved molecular toolkits, enabling recognition and nutrient exchange. Plants evolved the common symbiosis signaling pathway (CSSP), involving genes like SYMRK (symbiosis receptor-like kinase) and calcium-calmodulin-dependent kinases, which regulate both AM and rhizobial symbioses and trace back to the liverwort stage of plant evolution. In fungi, symbiosis-specific gene families expanded for effector proteins that suppress plant defenses and facilitate arbuscule formation, with comparative genomics showing these traits as ancestral within Glomeromycota rather than derived from saprotrophy. This reciprocal adaptation drove mutual benefits—fungi supplying phosphorus and nitrogen in exchange for photosynthates—facilitating plant terrestrialization in nutrient-poor soils, as evidenced by the ubiquity of AM associations in 72% of vascular plant species across major lineages. Subsequent mycorrhizal types arose through multiple independent evolutionary innovations, marking distinct phylogenetic developments. Ectomycorrhizae (EcM) emerged later, with the earliest in during the to (around 200-150 million years ago), followed by diversification in angiosperms and other gymnosperms during the (approximately 100-66 million years ago), involving over 30 fungal lineages primarily in and . Ericoid (ErM), (OrM), and nutrient-manipulating (NM) mycorrhizae also originated in the , often via transitions from AM ancestors, with genomic evidence of in effector secretion and hyphal networking to access organic in acidic or nutrient-impoverished habitats. Co-evolution here featured host-specificity shifts, with frequent gains and losses of EcM capability in plant families like and , correlating with woody habit diversification and reduced reliance on AM in boreal and temperate forests. These symbioses exhibit three evolutionary waves: the initial AM dominance (>450 Ma), Cretaceous expansions of EcM/NM/ErM/OrM, and ongoing Palaeogene-present radiations linked to shifts and specialization, influencing global diversity patterns such as EcM overrepresentation in Australian hotspots. While strict co-speciation is rare due to horizontal host-switching, phylogenetic congruence in some clades (e.g., AM fungi with ) underscores causal mutualism in driving , as multifunctional roots in transitional lineages enhanced adaptability to heterogeneous environments.

Types of Mycorrhizae

Ectomycorrhiza

Ectomycorrhizae represent a mutualistic symbiosis between fungi and the fine roots of approximately 10% of plant families, predominantly woody perennials such as trees in the Pinaceae, Betulaceae, Fagaceae, and Salicaceae families. In this association, the fungus forms a dense hyphal mantle enveloping the root tip and a Hartig net of hyphae penetrating intercellular spaces of the root cortex, without invading living cells. This extracellular colonization distinguishes ectomycorrhizae from endomycorrhizal types, enabling efficient nutrient foraging via extraradical mycelium that extends into the soil. The fungal partners are primarily from the and phyla, encompassing over 5,000 described species, many of which produce visible fruiting bodies like mushrooms. These fungi, including genera such as , , and , originate from saprotrophic ancestors and retain enzymatic capabilities for , supplementing inorganic nutrient uptake. Host specificity varies; some fungi associate with broad ranges of trees, while others are restricted, influencing forest composition and diversity. Formation begins with fungal hyphae contacting susceptible root tips, triggered by chemical signals like strigolactones from and sesquiterpenes from fungi, leading to where roots swell and branch dichotomously. The mantle develops from aggregated hyphae, providing a protective barrier, while the facilitates bidirectional transfer: fungi deliver soil-derived , , and , receiving up to 20% of the plant's photosynthate carbon in return. This exchange is regulated by source-sink dynamics, with transfer rates adapting to environmental availability. Ecologically, ectomycorrhizae underpin forest resilience by enhancing host nutrient acquisition in nutrient-poor soils, suppressing root pathogens through and antimicrobial compounds, and connecting communities via common mycelial networks for resource sharing. They contribute to soil aggregation, , and tolerance to stressors like , , and , with disruptions linked to reduced tree vigor and productivity. In boreal and temperate forests, where ectomycorrhizal trees dominate, these associations drive biogeochemical cycles, supporting and timber production.

Arbuscular Mycorrhiza

Arbuscular mycorrhiza (AM) constitutes a mutualistic symbiosis between fungi primarily from the phylum Glomeromycota and the roots of approximately 72-80% of terrestrial vascular plant species, including crops like wheat and maize. These fungi colonize the root cortex intracellularly, extending extraradical hyphae into the soil to enhance nutrient uptake while receiving photosynthetically derived carbohydrates from the host plant. The association dates back over 400 million years, predating many modern plant lineages, and persists across diverse ecosystems due to its role in phosphorus acquisition under low-soil-fertility conditions. Key structural features include arbuscules, highly branched hyphal structures that form within cortical cells and serve as the primary sites for bidirectional exchange. Arbuscules, resembling small trees, interface intimately with the via the peri-arbuscular membrane, facilitating the transfer of fungal-acquired minerals such as and to the in exchange for up to 20% of the 's fixed carbon, often as or sugars. Vesicles, globular storage organs filled with , also develop in the cortex, aiding fungal and reserves, though not all AM fungi produce them consistently. transfer mechanisms involve specific transporters; for instance, fungal proton-coupled transporters release inorganic into the arbuscular interface, while SWEET and MST transporters export hexoses and to the . The enhances plant uptake by extending the absorptive surface area through hyphae, which can explore volumes inaccessible to alone, particularly in -deficient soils where AM colonization increases plant growth by 20-50% in controlled experiments. Regulation occurs via signaling pathways, including the common pathway involving calcium oscillations that trigger nuclear-associated protein kinases for arbuscule accommodation. While mutually beneficial under natural conditions, the exchange can become parasitic if fungal carbon demands exceed plant benefits, as evidenced by studies showing dynamic reciprocity. AM fungi lack , relying on asexual spores for dispersal, which contributes to their ancient, clonal-like lineages within Glomeromycota.

Ericoid, Orchid, and Monotropoid Mycorrhizae

Ericoid mycorrhizae form mutualistic associations between plants in the family, such as species, and primarily ascomycetous fungi, characterized by the penetration of fungal hyphae into epidermal cells of fine "hair roots," forming compact intracellular hyphal coils without arbuscules or vesicles. These coils facilitate nutrient exchange, particularly enabling the mobilization of and from nutrient-poor, acidic soils like those in heathlands and bogs. Fungal partners belong to diverse lineages including Oidiodendron, Rhizoscyphus, and Meliniomyces, which exhibit saprotrophic capabilities for decomposing , enhancing plant access to recalcitrant nutrients. This supports plant survival in harsh environments by improving tolerance to and , though the fungi receive carbon from the host in return. Orchid mycorrhizae establish symbiotic relationships between Orchidaceae plants and basidiomycete fungi, essential for seed germination, protocorm development, and adult nutrition, as orchid seeds lack and require fungal provisioning of carbohydrates and minerals. Fungal associates predominantly include genera such as Tulasnella, Ceratobasidium, and Serendipita, some of which exhibit saprotrophic or ectomycorrhizal lifestyles, forming pelotons—clumped hyphae within cortical cells—that degrade upon nutrient transfer. These associations vary by orchid life stage and environment, with specificity influencing distribution; for instance, Tulasnella species often dominate in terrestrial orchids sensitive to changes. While typically mutualistic in early stages, adult orchids may exploit fungi as carbon sources in mycoheterotrophic species, blurring the boundary with . Monotropoid mycorrhizae occur in achlorophyllous plants of the subfamily , such as , linking to ectomycorrhizal basidiomycetes like those in , featuring an extracellular mantle, paraepidermal , and distinctive intracellular "fungal pegs" in cortical cells for nutrient uptake. These mycoheterotrophic plants derive carbon and nutrients via "third-party" transfer from photosynthetically active hosts connected through shared fungal networks, with peg formation peaking seasonally during root elongation. The associations enable survival in shaded forest understories lacking for autotrophy, though fungal specificity varies, with some evidence of exploitation where plants drain resources without full reciprocity. This type bridges ericoid and ectomycorrhizal morphologies, highlighting evolutionary adaptations for heterotrophy in nutrient-limited niches.

Other Endophytic and Similar Associations

Dark septate endophytes (DSE) represent a polyphyletic group of root-colonizing fungi, primarily , characterized by dark-pigmented, septate hyphae that form melanized structures such as microsclerotia within root cortical cells. Unlike typical mycorrhizae, DSE lack arbuscules, vesicles, or external mantles, instead achieving intracellular and intercellular starting from superficial hyphae that penetrate the . Their associations with range from mutualistic to neutral or weakly antagonistic, depending on fungal strain, host species, and environmental conditions, with empirical studies demonstrating benefits like improved uptake in via enhanced soil exploration and production. DSE are prevalent in stressful habitats, including arid, high-altitude, and metal-contaminated , where they confer tolerance to , , , and pathogens by bolstering nutrient acquisition (e.g., and ) and activating defense responses. Mucoromycotina fine root endophytes (MFRE), a distinct within the Mucoromycotina subphylum, form intracellular hyphal networks in fine of vascular , facilitating bidirectional exchange without the coarse structures of arbuscular mycorrhizae. These fungi acquire and , transferring them to hosts in exchange for photosynthetically fixed carbon, as evidenced by stable tracing in lycophytes and angiosperms. MFRE symbioses are nutritionally mutualistic and widespread, often co-occurring with arbuscular mycorrhizae, though they do not rely on the canonical common symbiotic signaling pathway (CSSP) for root colonization. Recent experiments confirm their role in preferential nitrogen-for-carbon trades, enhancing host fitness in nutrient-poor environments. Beyond DSE and MFRE, diverse non-mycorrhizal root endophytes, predominantly , inhabit root tissues without forming specialized symbiotic organs, contributing to soil carbon sequestration and metal tolerance in hosts like alpine forbs. Inoculation trials show these fungi increase belowground and stabilization, independent of mycorrhizal pathways, underscoring their complementary ecological roles in plant-fungal networks. Such associations highlight functional convergence with mycorrhizae in nutrient cycling, though their impacts vary by context, with some strains promoting growth via modulation or antagonism.

Formation and Mechanisms

Establishment Processes

The establishment of mycorrhizal symbioses initiates with the germination of fungal propagules, such as spores or hyphal fragments, in the soil, often triggered by chemical signals exuded from host plant roots, including strigolactones that promote hyphal branching in arbuscular mycorrhizal (AM) fungi. This presymbiotic phase involves bidirectional signaling, where fungal molecules like Myc factors (lipochitooligosaccharides) elicit calcium oscillations in plant cells, facilitating recognition and directed hyphal growth toward the root surface. In AM associations, hyphae adhere to the root epidermis via appressoria-like structures, penetrate the cell wall without breaching the plasma membrane, and colonize the cortical cells intracellularly, culminating in the formation of transient arbuscules for nutrient exchange. This penetration is mediated by fungal chitinases and plant-derived cues, with the process typically requiring 7-14 days under optimal soil moisture and temperature conditions (e.g., 20-25°C). For ectomycorrhizae (ECM), establishment differs by forming extracellular structures: hyphae from germinated basidiospores or soil mycelium aggregate around the root apex, creating a fungal mantle that envelops short roots and inhibits elongation, while the Hartig net—a labyrinthine network of hyphae—penetrates intercellular spaces of the epidermis and cortex for nutrient transfer without entering cells. This process relies on plant signals like flavonoids and fungal responses involving hydrophobins for surface attachment, often completing mantle formation within 3-7 days post-contact in compatible host-fungus pairs, such as Pinus with Pisolithus species. Host specificity influences success, with ECM fungi showing narrower compatibility than AM fungi, which associate with ~80% of land plants across phyla. Across types, microbial helpers like mycorrhization helper bacteria (MHB) can enhance establishment by stimulating germination or suppressing antagonists, increasing colonization rates by up to 50% in some soil systems. Environmental factors, including (optimal 5.5-7.0 for most), phosphorus availability, and absence of fungicides, modulate these processes, with low often accelerating hyphal extension toward . Failed establishments occur if signaling mismatches, such as incompatible receptor kinases in the , prevent penetration, underscoring the co-evolutionary tuning of molecular dialogues.

Molecular Signaling and Recognition

The establishment of mycorrhizal symbioses begins with reciprocal molecular signaling between the host and , enabling mutual recognition and initiating developmental programs. In arbuscular mycorrhizae (AM), exude strigolactones (SLs) from , particularly under limitation, which stimulate fungal and promote extensive hyphal branching toward the host, as demonstrated in species like Rhizophagus irregularis. These SLs activate fungal mitochondrial function and metabolism, enhancing pre-symbiotic growth. In response, AM fungi release Myc factors, including lipochitooligosaccharides (Myc-LCOs) and short-chain oligomers (Myc-COs), which are perceived by LysM receptor-like kinases such as LYK3 or NFR1, triggering calcium oscillations in cells. This perception activates the common symbiosis signaling pathway (CSSP), conserved across AM and rhizobial symbioses, involving nuclear calcium spiking decoded by calcium/calmodulin-dependent protein kinase (CCaMK/DMI3) and the transcription factor CYCLOPS/IPD3. Downstream, GRAS family transcription factors like RAM1 regulate arbuscule formation and nutrient transporter expression, ensuring intracellular accommodation of fungal structures. Autoregulation of mycorrhization (AOM) integrates signals via CLE peptides (e.g., MtCLE53) and receptor kinases (e.g., /RDN1), feedback-inhibiting SL biosynthesis to prevent over-colonization once symbiosis is established. In ectomycorrhizae (ECM), signaling is less characterized and lacks a fully conserved CSSP equivalent, with evidence suggesting divergence in conifers like Pinaceae. Plant roots release flavonoids (e.g., rutin, quercitrin), which induce fungal hyphal extension and effector gene expression, such as MiSSP7 in Laccaria bicolor, facilitating Hartig net formation by modulating plant jasmonic acid signaling via interaction with JAZ6. Fungal signals may include chitooligosaccharides from cell wall remodeling and potential LCOs, supported by fungal genomes encoding homologs of Nod-factor biosynthetic genes (e.g., chitin synthases, deacetylases in L. bicolor and Tuber melanosporum). Unlike AM, SLs show no consistent stimulatory effect on ECM fungal growth, indicating type-specific recognition mechanisms. Ericoid and orchid mycorrhizae exhibit analogous but adapted signaling, often involving fungal effectors for nutrient mobilization in nutrient-poor soils, though detailed molecular exchanges remain understudied compared to AM and ECM. Overall, these pathways underscore causal dependencies on nutrient status and environmental cues, with disruptions (e.g., SL mutants) abolishing symbiosis formation, affirming their necessity for reciprocal benefits.

Structural Features and Nutrient Exchange Pathways

Mycorrhizal associations exhibit distinct structural adaptations that facilitate intimate contact between fungal hyphae and host plant roots, enabling efficient bidirectional nutrient transfer. In ectomycorrhizae (EM), fungi form a dense hyphal mantle enveloping the root tip, typically 20-50 μm thick, which serves as a protective barrier and primary absorption surface for soil nutrients. Intruding between epidermal and cortical cells is the Hartig net, a labyrinthine network of hyphae that penetrates up to 100-200 μm into the root cortex without invading cells, maximizing interfacial surface area—often exceeding 200 cm² per cm³ of root volume—for solute exchange. This structure, first described by Theodor Hartig in 1841, contrasts with arbuscular mycorrhizae (AM), where fungi colonize root interiors via intracellular hyphae and form arbuscules: highly branched, tree-like haustoria within cortical cells that occupy 20-80% of the host cell volume and degrade after 4-10 days to allow continuous renewal. AM also produce vesicles for lipid storage and extraradical hyphae extending up to 10-20 cm into soil, enhancing exploration beyond root depletion zones. Nutrient exchange pathways rely on specialized transporters at symbiotic interfaces. In EM, extraradical hyphae uptake (Pi) via high-affinity transporters like those in the Pht1 family, translocating it through the mantle and to cells via fungal aquaporins and symplastic , while export hexoses through SWEET transporters into the for fungal uptake by MST1-like permeases. , primarily as , follows similar hyphal transport routes, with exchange ratios favoring 5-20% of photosynthate allocated to fungi in return for 80-90% of Pi acquisition in nutrient-poor soils. For AM, arbuscules host the periarbuscular membrane, a -derived enriched with transporters (e.g., PT4 in ) that unload Pi from fungal hyphae into the cytoplasm, regulated by transcription factors like RAM1 to prevent premature arbuscule collapse. Carbon flows inversely via fungal hexose transporters (e.g., ) retrieving -derived sugars from the interfacial , with AM fungi acquiring up to 20% of host photosynthates, as quantified in stable labeling studies showing rapid 13C transfer within hours. These pathways are modulated by gradients, with fungal and strigolactones signaling reciprocity to sustain mutualism. In both EM and AM, water and micronutrients like traverse hyphal networks via aquaglyceroporins, with mass flow and dominating short-distance transfer at interfaces, while long-distance hyphal transport involves at rates of 1-5 μm/s. Ericoid and mycorrhizae adapt similar principles but with coiled hyphae or pelotons emphasizing organic mineralization, reflecting host-specific evolutionary tweaks to nutrient-poor habitats. Empirical models, such as those simulating two-membrane barriers in AM, predict exchange efficiencies up to 10-fold higher than non-mycorrhizal , underscoring causal links between structural intimacy and enhanced uptake kinetics.

Benefits and Ecological Roles

Nutrient Acquisition and Transfer

Mycorrhizal associations enhance nutrient acquisition by extending fungal hyphae into regions inaccessible to roots, thereby increasing the effective absorptive surface area. These hyphae access immobile s such as (P) and (N), which fungi solubilize through acid production, enzyme secretion, and modulation before transferring to host plants via specialized interfaces like arbuscules in arbuscular mycorrhizae (AM) or Hartig nets in ectomycorrhizae (ECM). In exchange, plants supply fungi with photosynthetically derived carbon, typically 4-20% of total fixed carbon, supporting fungal growth and nutrient-foraging activities. In AM symbioses, fungi predominantly facilitate uptake, contributing up to 80% of plant requirements under low-soil- conditions by deploying extraradical hyphae that explore soil micropores and mobilize sparingly soluble forms via phosphatases and organic acid exudation. Studies on crops like and demonstrate that AM inoculation under deficiency boosts acquisition efficiency by 20-50%, correlating with hyphal length density and upregulated plant transporter genes. For nitrogen, AM fungi acquire both inorganic (e.g., ) and organic forms, though less dominantly than ECM, with transfer occurring across the peri-arbuscular membrane where fungal MST1 transporters facilitate movement to . ECM fungi excel in N acquisition, particularly organic N from soil organic matter, decomposing complex polymers like proteins and chitin using extracellular proteases and peptidases, which supply ammonium or amino acids to hosts in N-limited boreal forests. ECM hyphae can access N in mineral soil horizons, with species-specific enzyme profiles determining efficiency; for instance, fungi like Suillus spp. dominate in acidic soils where organic N prevails. Transfer involves fungal uptake via high-affinity transporters followed by export through the symbiotic interface, enhancing host N status by 30-100% in field trials. Common mycorrhizal networks (CMNs) enable inter-plant nutrient transfer, allowing donor plants to shuttle carbon, P, or N to recipients, such as shading-stressed neighbors, via anastomosed hyphae spanning up to several meters. Experiments with isotopically labeled nutrients confirm bidirectional flow, with AM networks facilitating 10-40% of transferred P or N between connected plants, influenced by sink strength and fungal identity rather than mere connectivity. This transfer underscores causal nutrient redistribution in plant communities, though net benefits depend on environmental gradients like .

Stress Tolerance and Plant Defense

Mycorrhizal symbioses confer enhanced tolerance to abiotic stresses such as , , extremes, and heavy metal contamination by improving water and uptake, modulating osmotic balance, and activating defenses in host . Arbuscular mycorrhizal fungi (AMF), for instance, alleviate stress in seedlings by optimizing photochemistry and elevating levels of protective metabolites like and soluble sugars, leading to higher relative and photosynthetic rates compared to non-mycorrhizal controls. Similarly, AMF mitigates effects across diverse species by enhancing selective transport (e.g., increased +/Na+ ratios) and root , with meta-analyses of over 100 studies demonstrating 20-50% improvements in biomass and survival under salt stress relative to uninoculated . Ectomycorrhizal (ECM) associations, prevalent in trees, provide robust protection against like , lead, and ; ECM fungi such as Pisolithus tinctorius bind toxic ions in extraradical hyphae and mantles, reducing translocation to shoots by up to 70% in hosts like seedlings exposed to 100-500 mg/kg metal concentrations. These mechanisms stem from fungal physiological adaptations, including metal via metallothioneins and , which prevent oxidative damage while maintaining symbiotic exchange. Biotic stress resistance is bolstered through mycorrhiza-induced resistance (MIR), where fungal colonization primes plant immune responses without constitutive activation, enabling faster and stronger defenses upon challenge. AMF trigger systemic priming of (JA) and ethylene signaling pathways, enhancing resistance to foliar s like species in by 30-60% through upregulated expression of defense genes such as PR-1 and PDF1.2, independent of nutrient status in some cases. This priming effect involves mobile signals from roots to shoots, potentially lipochitooligosaccharides or strigolactones, and is genotype-specific; for example, MIR against root s like is more pronounced in phosphorus-limited soils due to competitive exclusion and direct fungal antagonism via compounds. ECM fungi similarly inhibit soil-borne s in forest trees by altering microbiomes and producing extracellular enzymes that degrade cell walls, reducing incidence by 40-80% in metal-contaminated sites. Overall, these benefits arise from reciprocal signaling and resource partitioning, where fungi invest in stress-responsive structures like extraradical hyphae, which extend access to and dilute exposure, while allocate carbohydrates to sustain fungal vitality under duress. Empirical field trials, such as those with AMF-inoculated crops under combined drought-salinity, report yield increases of 15-35% over controls, underscoring practical . However, efficacy varies with fungal , host compatibility, and stress intensity; not all associations yield benefits, as high metal loads can overwhelm fungal sequestration, leading to breakdown.

Soil Stabilization and Ecosystem Engineering

Mycorrhizal fungi contribute to primarily through the production of extraradical hyphae that physically enmesh soil particles, forming stable aggregates resistant to . These hyphal networks bind microaggregates into larger macroaggregates, enhancing and water infiltration while reducing susceptibility to water and wind . Arbuscular mycorrhizal fungi (AMF) further promote aggregation via glomalin-related soil proteins (GRSP), exudates that act as adhesive agents, with concentrations correlating positively with aggregate stability in diverse . Laboratory experiments demonstrate that AMF increases the proportion of water-stable aggregates by up to 20-30% compared to non-mycorrhizal controls, particularly in sandy or disturbed soils. In erosion-prone environments, such as agricultural fields or post-mining sites, mycorrhizae mitigate nutrient losses by stabilizing ; for instance, AMF reduce erosion-induced and runoff by enhancing aggregate integrity under simulated rainfall. This stabilization extends to zero-tillage systems, where preserved mycorrhizal networks maintain higher glomalin levels and lower rates than tilled soils, preserving up to 15-25% more . Field studies in grasslands show that AMF hyphae and synergistically increase large macroaggregate formation (>2 mm) during succession, slowing aggregate disintegration and supporting long-term cohesion. As engineers, mycorrhizal fungi reshape habitats by altering physicochemical properties, facilitating assembly and succession. Their hyphal networks connect plant roots, enabling resource sharing that influences competitive dynamics and ; for example, in degraded lands, AMF accelerates revegetation by improving and structure, reducing barren patch persistence by 40-60% in restoration trials. In coastal wetlands, AMF enhance aggregation and nutrient retention, promoting establishment and mitigating salinity-induced degradation. Globally, these fungi regulate through necromass incorporation into aggregates, contributing an estimated 36% of organic carbon in some temperate forests via stabilized fungal residues. Such engineering effects underscore mycorrhizae's role in maintaining resilience against disturbances like or land-use change.

Limitations and Potential Costs

Parasitic or Neutral Outcomes

Mycorrhizal associations, while typically mutualistic, can shift toward when the carbon cost to the host exceeds the benefits received from the , resulting in reduced growth or compared to non-colonized controls. This outcome is particularly evident in nutrient-rich environments, such as soils with high availability, where the continues to demand photosynthates without providing proportional uptake or stress alleviation. Experimental from arbuscular mycorrhizal fungi (AMF) interactions demonstrates negative growth responses, with mycorrhizal plants exhibiting smaller production under these conditions. In specific plant-fungus pairings, such as Joshua trees (Yucca brevifolia) inoculated with diverse ectomycorrhizal communities, certain fungal consortia induce parasitic effects by impairing seedling establishment and survival, particularly in resource-limited settings where inefficient nutrient transfer predominates. High fungal densities can exacerbate this, as mycorrhizae compete with host plants for carbon resources, leading to diminished induced defenses and overall fitness. Such parasitism aligns with a broader mutualism-parasitism continuum, where developmental or environmental factors tip the balance toward net costs for the plant. Neutral outcomes occur when mycorrhizal colonization neither significantly enhances nor impairs plant performance, often in scenarios of balanced resource exchange or ineffective nutrient pathways. These interactions are documented in controlled studies where plant biomass and nutrient status show no differential response to fungal presence, suggesting minimal symbiotic functionality. Factors like incompatible host-fungus specificity or suboptimal soil conditions can contribute to this neutrality, preventing the establishment of exploitative dynamics while failing to yield mutualistic gains. Empirical data indicate that such neutral states are less common than mutualism but highlight the variability inherent in mycorrhizal symbioses across ecological contexts.

Inhibitory Factors and Failed Symbioses

High levels of soil , often from excessive fertilization (e.g., 240 kg/ha), inhibit arbuscular mycorrhizal (AM) colonization by reducing the plant's dependence on fungal uptake, thereby suppressing initiation and hyphal development. Similarly, high inputs via fertilizers decrease root infection rates and production in crops like . Acidic conditions (pH 4.5) impair AM functionality primarily by limiting arbuscule formation within , disrupting exchange interfaces essential for maintenance. Optimal pH varies by fungal ; for instance, Glomus mosseae performs well in alkaline soils (pH 6–9), while G. intraradices exhibits reduced extraradical at pH 5. Temperature extremes outside 20–30°C hinder mycelial growth and spore germination, with colonization dropping below 10°C temperatures; conversely, excessive moisture or stresses hyphal networks, as mycorrhizae require balanced and water availability for establishment. High salinity (Na > 3181 ppm) further reduces , though tolerant strains like G. mosseae show partial resilience. Biotic interactions often lead to failed symbioses through antagonism; soil bacteria such as produce antibiotics (e.g., phenazine-1-carboxylic acid), volatile organic compounds, and chitinases that degrade fungal cell walls, inhibiting ectomycorrhizal (ECM) hyphal integrity and colonization. These microbes also compete for carbon and , modulate via organic acids to unfavorable levels (e.g., below 6.5 for pH-sensitive ECM like Amanita rubescens), or release toxins like . Pathogenic fungi (e.g., ) vie for root access and induce plant defenses, including and phytoalexins, which collateralize against mycorrhizal ingress. Saprotrophic fungi and competing AM fungi exacerbate resource scarcity, preventing stable associations. Genetic mismatches between host and fungi contribute to symbiosis failure; certain lack key symbiosis genes (e.g., deletions in signaling pathways), rendering them non-responsive to fungal signals and incapable of forming arbuscules or mantles, as seen in independent evolutionary losses of AM capability. Host modulates compatibility, with trade-offs where high mycorrhizal dependence correlates with lower benefits under compatible conditions, leading to neutral or aborted interactions. In , prior nodulation suppresses subsequent AM colonization via conflicts. Agricultural practices amplify failures; physically severs extraradical hyphae, while rotating with non-mycorrhizal hosts (e.g., brassicas) starves fungal propagules, reducing inoculum viability and recolonization potential. Endemic mycorrhizae outcompete introduced strains, further hindering deliberate inoculations in managed systems. These factors collectively result in incomplete or transient symbioses, where initial contact occurs but degenerates due to incompatible signaling or environmental overrides, yielding no net mutualism.

Debates on Universal Mutualism

The concept of mycorrhizal symbiosis as universally mutualistic, wherein both plant and fungus invariably benefit through reciprocal nutrient exchange, has faced scrutiny from empirical studies revealing context-dependent outcomes along a mutualism-parasitism continuum. This perspective posits that the net benefit to the plant diminishes when the carbon cost allocated to the fungus exceeds gains in mineral nutrient uptake, particularly under conditions of high soil fertility or excessive fungal colonization. For instance, in phosphorus-enriched soils, arbuscular mycorrhizal fungi (AMF) may impose a net carbon drain on hosts without commensurate phosphorus delivery, shifting the interaction toward parasitism or neutrality. Experimental evidence underscores this variability; in greenhouse trials with Datura stramonium, plant biomass peaked at low AMF inoculum levels (1/24th pot volume) but declined at higher densities due to intensified resource competition and reduced herbivory tolerance (linear decrease, = 0.40, p = 0.022). Similarly, for the grass Corynephorus canescens, AMF colonization consistently reduced growth (mycorrhizal growth depression of -59%) under high and shaded conditions, exacerbating competitive disadvantages against neighbors, whereas Hieracium pilosella exhibited persistent mutualism (+78% growth). These findings challenge universalist views by highlighting species-specific responses and environmental modulators like availability and , where emerges not as aberration but as a predictable outcome when benefits are marginal. Field and inoculation studies further illustrate temporal and spatial dynamics; in Yucca brevifolia (Joshua trees) along a 1200-m elevation gradient in Joshua Tree National Park, low-elevation AMF communities initially induced parasitism (mycorrhizal growth response of -0.28 at 1 month) but transitioned to mutualism (+0.10 at 9 months), driven by shifts in fungal taxa (e.g., Gigasporaceae dominance at warmer, drier sites) and improved nutrient status over development. Reviews of AMF parasitism evidence, while noting methodological challenges in isolating fungal effects, affirm the continuum's validity through aggregated data on reduced plant fitness in fertile or high-colonization scenarios, countering claims of inherent reciprocity. Proponents of conditional mutualism argue that regulatory mechanisms, such as plant-sanctioned carbon allocation, stabilize benefits, yet critics emphasize empirical inconsistencies, including neutral or negative growth in over 20% of tested plant-fungus pairings under optimized lab conditions. This debate informs ecological modeling, as assuming universal mutualism overlooks potential costs in predicting community dynamics or restoration outcomes, particularly in anthropogenically altered soils where high nutrient inputs may favor parasitic shifts. Ongoing prioritizes fungal identity and abiotic gradients to quantify thresholds, revealing that while mutualism predominates in -poor habitats, parasitism's prevalence undermines blanket characterizations of the .

Global Occurrence and Specificity

Distribution Patterns

Mycorrhizal symbioses occur in approximately 90% of species worldwide, spanning diverse terrestrial ecosystems from to tropical rainforests. This near-ubiquity reflects the ancient evolutionary origins of these associations, with evidence dating back over million years, and their persistence across biomes underscores their role in to varying availability. Non-mycorrhizal , such as those in the and families, represent exceptions, often thriving in disturbed or nutrient-rich habitats where fungal dependency is reduced. Arbuscular mycorrhizae (AM), formed by fungi in the Glomeromycota phylum, exhibit the broadest distribution, associating with 72% of vascular and predominating in grasslands, croplands, and tropical forests where herbaceous and annual species abound. These associations thrive in warm, well-aerated soils with moderate levels, covering over 60% of global vegetated land area in AM-dominant plant communities. In contrast, ectomycorrhizae (ECM), primarily involving and , are restricted to about 2% of plant species—mainly woody perennials like pines (), oaks (), and birches ()—and cluster in temperate and boreal forests, where they facilitate uptake in cooler, organic-rich soils. ECM coverage aligns with biomes, comprising up to 20% of global tree-dominated landscapes but showing sharp declines toward the . Ericoid mycorrhizae, linked to Ericaceae shrubs such as heaths and blueberries, favor acidic, nutrient-impoverished soils in boreal, Mediterranean, and high-altitude regions, often co-occurring with ECM in mixed woodlands. Orchid mycorrhizae, involving basidiomycete fungi, display highly specialized patterns tied to orchid lifecycles, prevalent in tropical and temperate epiphytic or terrestrial habitats but absent from most non-orchid hosts. Latitudinal gradients influence type-specific richness: AM fungal diversity peaks in tropics and decreases poleward, while ECM diversity increases toward higher latitudes, driven by host plant distributions and climatic factors like temperature and precipitation. These patterns correlate with global carbon stocks, with ECM-dominated ecosystems storing more soil carbon due to slower decomposition rates.

Host-Fungus Specificity and Diversity

Host-fungus specificity in mycorrhizal symbioses differs markedly by fungal type, influencing partner compatibility and ecological roles. Arbuscular mycorrhizal (AM) fungi generally display low specificity as generalists, associating with over 90% of species across broad phylogenetic and functional groups, such as grasses, forbs, and trees. This broad host range enables AM fungi to colonize diverse habitats, with community composition shaped more by environmental factors than strict host barriers, though some phylogenetic clustering occurs. Ectomycorrhizal (ECM) fungi, by contrast, exhibit higher specificity, often restricted to host families or genera like or , with host phylogeny as the dominant determinant of compatibility. ECM specificity forms a gradient from generalists to specialists, with about 54% of ECM fungi linking to two or fewer host genera and 40% of epigeous basidiomycete genera exclusive to one host genus. Mechanistic filters sustain this pattern, including spatial-temporal host availability, root signaling for recognition via heterorhizic systems, fungal competition mediated by priority effects and secondary metabolites, and sanctions enforcing mutualistic carbon-nutrient exchange. Ericoid and orchid mycorrhizae show even stricter host fidelity, typically confined to or Orchidaceae, respectively, underscoring clade-specific evolutionary adaptations. Fungal diversity reflects these specificity patterns, with ECM associations supporting an estimated 25,000 compared to 300–1,000 for AM fungi, driven by specialized host interactions and in heterorhizic roots. Host diversity enhances fungal richness; for instance, co-occurring tree in forests maintain distinct ECM communities, including specialists, thereby bolstering overall ectomycorrhizal diversity across sites. In AM systems, low prevails, with 93% of taxa spanning multiple continents and 34% all six surveyed continents, facilitating global dispersal and adaptable host partnering under varying local conditions. Such dynamics highlight how host-fungus specificity modulates , with specialist-heavy ECM networks promoting niche partitioning and AM generalism enabling widespread resilience.

Human Applications and Impacts

Agricultural and Crop Enhancement

Arbuscular mycorrhizal fungi (AMF) enhance agricultural productivity by forming symbiotic associations with crop roots, primarily improving , , and uptake, which supports greater shoot and overall plant vigor. In field trials, AMF has increased crop yields, particularly in rainfed conditions, through mechanisms including elevated rates and stress mitigation. For instance, yields showed significant positive responses to AMF application, with benefits most pronounced in nutrient-poor or degraded soils where native fungal communities are limited. These fungi enable reductions in chemical inputs by extending the system's absorptive capacity via extraradical hyphae, promoting efficient cycling and minimizing leaching losses. Studies combining AMF with lowered rates in crops like and demonstrate maintained or enhanced yields alongside improved indicators, such as increased microbial diversity. AMF also bolster crop resilience to abiotic stresses, including and , by facilitating water transport and osmotic adjustment, which is critical for sustainable farming in variable climates. Commercial mycorrhizal inoculants, often containing species like Rhizophagus or Claroideoglomus, are applied to or to accelerate establishment, potentially lowering the environmental footprint of intensive . However, efficacy varies; while some products enhance colonization and growth in horticultural and field crops, others exhibit low viability, label inaccuracies, or contamination risks, underscoring the need for site-specific testing and quality controls. Meta-analyses indicate that globally sourced inoculants can outperform local strains in certain contexts but may not consistently alter plant status without complementary practices like reduced .

Forestry Restoration and Revegetation

Mycorrhizal inoculation of seedlings has been integrated into forestry restoration practices to improve and growth on degraded lands, including post-mining sites and eroded slopes. Inoculation with ectomycorrhizal fungi, such as Pisolithus tinctorius, enhances uptake and in pine species, leading to field rates exceeding 80% in some trials compared to non-inoculated controls. Custom nursery production of bareroot and container-grown trees, paired with selected mycorrhizal associates, facilitates scalable revegetation, as demonstrated in U.S. Forest Service programs targeting arid and nutrient-poor environments. Arbuscular mycorrhizal fungi (AMF) supports revegetation by accelerating establishment and accumulation in severely disturbed ecosystems. A 2016 review highlighted AMF's role in restoring degraded grasslands and forests, where inoculated plants exhibited up to 50% greater root colonization and improved in symbiotic partners. In mine wasteland reclamation, mycorrhizal applications reduce heavy metal uptake while promoting ; meta-analyses of field studies report 20-40% increases in plant cover and metrics within 2-5 years post-inoculation. Restoration thinning in ponderosa pine forests influences mycorrhizal propagule densities, with moderate preserving fungal inoculum for understory recovery and long-term tree vigor. Combined strategies, such as AMF with soil amendments like , have succeeded in semi-arid areas, yielding 30% higher survival in herbaceous and woody species under water-limited conditions. These approaches underscore mycorrhizae's utility in resilient ecosystems, though efficacy varies with site-specific chemistry and fungal-host compatibility.

Threats from Agricultural Practices

Intensive practices, such as conventional plowing, physically disrupt the extraradical hyphal networks of arbuscular mycorrhizal fungi (AMF), reducing their density and connectivity by severing mycelia and exposing them to environmental stresses. This disturbance diminishes viability and root colonization rates, with studies showing that repeated can decrease AMF and infectivity in agricultural s. In contrast, conservation preserves these networks, highlighting as one of the most damaging factors to beneficial fungi. Excessive application of chemical fertilizers suppresses AMF activity by altering plant-fungus signaling and reducing the plant's dependence on fungal acquisition, as high availability diminishes the mutualistic benefits. Long-term intensive fertilization has been linked to lower AMF abundance and diversity, with meta-analyses indicating that phosphorus-rich amendments particularly inhibit . This effect stems from disrupted carbon-for- exchanges, where fertilized plants allocate fewer resources to fungal partners. Pesticides and fungicides, commonly used in conventional , directly harm AMF propagules and hyphae, leading to reduced fungal and impaired formation. Research demonstrates that certain herbicides and fungicides decrease and root infection rates, exacerbating in managed soils. Combined with and fertilization, these chemicals compound threats, often resulting in simplified AMF communities less resilient to stressors. Monoculture cropping systems further threaten mycorrhizal diversity by limiting host variety, which restricts AMF species composition and abundance compared to diversified rotations or polycultures. Continuous has been shown to lower AMF richness, as specialized fungi adapted to specific hosts decline without varied inputs. Intensive agriculture's reliance on such practices thus perpetuates a cycle of reduced symbiotic efficiency and degradation.

Climate Change and Environmental Interactions

Responses to Global Change Drivers

Mycorrhizal associations demonstrate dynamic responses to drivers, including elevated atmospheric CO2, rising temperatures, altered patterns, and increased deposition, which collectively influence fungal community composition, establishment, and host resilience. These responses often involve shifts in fungal abundance, diversity, and functional traits, mediated by interactions between abiotic stressors and plant-fungus specificity. For instance, arbuscular mycorrhizal (AM) fungi typically exhibit increased colonization under elevated CO2, enhancing nutrient uptake and growth, though effects vary by host species and conditions. Ectomycorrhizal (ECM) fungi, in contrast, may show altered organic acquisition capabilities, potentially extending CO2 fertilization effects in nitrogen-limited ecosystems. Elevated temperatures, often ranging from 2–3°C in experimental settings, generally promote greater root biomass allocation in mycorrhizal plants, with meta-analyses indicating an average 8.1% increase in root-to-shoot ratios, facilitating enhanced fungal exploration of soil resources. However, warming can induce shifts toward drought-tolerant fungal taxa, particularly in AM associations, where increased diversity correlates with improved plant tolerance to water stress through better water and nutrient transport. ECM-dominated forests may experience community restructuring, with some taxa declining under prolonged heat, potentially reducing overall symbiosis efficacy in warming scenarios. Drought conditions, exacerbated by , elicit adaptive responses in mycorrhizae, such as hyphal proliferation and spore trait modifications in AM fungi to maintain connectivity and resource flow to hosts, thereby mitigating stress and sustaining . In ECM systems, fungal shifts toward more resilient species can enhance rates but may also amplify losses in early-successional stages. Nitrogen deposition, typically at rates of 10–50 kg N ha⁻¹ year⁻¹ in impacted regions, disrupts mycorrhizal structures by favoring non-mycorrhizal competitors and reducing fungal reliance in hosts, leading to legacy effects on community feedbacks. These alterations underscore mycorrhizae's role in modulating vulnerability, though empirical data reveal context-dependent outcomes influenced by baseline and host diversity.

Feedback Effects on Carbon and Nutrient Cycles

Mycorrhizal associations exert significant feedback effects on carbon and cycles through the bidirectional exchange between and fungi, where allocate photosynthates to fungal partners in return for enhanced nutrient acquisition, thereby influencing dynamics and . Globally, transfer substantial carbon to mycorrhizal fungi, estimated at 3.93 gigatons of CO₂ equivalent annually to arbuscular mycorrhizal (AM) fungi and 9.07 gigatons to ectomycorrhizal (ECM) fungi, representing a major flux in terrestrial carbon cycling. This carbon supports extensive extraradical mycelial networks that contribute to pools, with fungal biomass acting as a sink by stabilizing against . However, the net effect on varies by mycorrhizal type: ECM-dominated systems often slow litter and promote carbon storage due to enzymatic inhibition of microbes, while AM systems may accelerate turnover through greater reliance on saprotrophic activity. In cycles, mycorrhizae enhance and uptake efficiency, reducing leaching losses and fostering tighter loops in phosphorus-limited soils. AM fungi, in particular, alleviate soil loss during by immobilizing particles and boosting demand, thereby maintaining retention under disturbance. These interactions create positive feedbacks where improved availability supports greater and carbon allocation to fungi, amplifying mycelial proliferation and soil aggregation, which in turn stabilizes carbon and reduces export. ECM fungi further modulate cycling by accessing organic sources via oxidative enzymes, potentially decoupling carbon and dynamics in boreal forests. from field experiments confirms that mycorrhizal presence can suppress leaching by up to 50% in agroecosystems, underscoring their role in sustaining . Under drivers like elevated CO₂ and warming, mycorrhizal feedbacks introduce variability: increased atmospheric CO₂ may elevate plant carbon transfer to fungi without proportionally enhancing nutrient return, potentially priming for decomposition in AM systems. In contrast, ECM dominance in northern latitudes correlates with decelerated carbon cycling, buffering against warming-induced losses, though shifts toward AM-associated shrubs could accelerate nutrient turnover and carbon release. These type-specific responses highlight causal pathways where mycorrhizal community composition mediates climate-carbon feedbacks, with ECM systems exhibiting stronger stabilization of against enzymatic breakdown. Long-term observations indicate that such feedbacks could amplify nutrient limitations in warming scenarios, constraining and altering cycle .

Conservation and Future Research

Protection Strategies and Mapping

Protection strategies for mycorrhizal fungi emphasize habitat preservation, minimal soil disturbance, and integration into broader to maintain symbiotic networks essential for and stability. Reduced tillage practices, such as , preserve mycorrhizal hyphal networks by limiting disruption to extraradical , which can extend connectivity by orders of magnitude beyond systems. Cover cropping and diverse rotations further support arbuscular mycorrhizal fungi (AMF) diversity, enhancing resilience against pathogens through competitive exclusion and improved nutrient cycling. with native mycorrhizal propagules during restoration projects has shown efficacy in re-establishing associations, particularly for ectomycorrhizal (ECM) fungi in , where banks or ectomycorrhizal seedlings improve survival rates by 20-50% in degraded sites. Avoiding broad-spectrum fungicides and excessive fertilization is critical, as these suppress AMF colonization; for instance, copper-based fungicides, used in organic agriculture, reduce AMF viability by up to 70%. Holistic approaches advocate incorporating "" into conservation frameworks alongside flora and fauna, prioritizing fungal-inclusive protected areas to counter vulnerabilities from land-use intensification. Mapping efforts leverage high-resolution geospatial models to delineate mycorrhizal biodiversity hotspots, revealing systematic under-protection. Predictive maps from global datasets indicate that over 90% of high-richness areas for AMF and ECM fungi fall outside designated protected zones, with less than 10% overlap with existing reserves as of 2025. These models integrate properties, host distributions, and climatic variables to forecast richness at 1 km² resolution, identifying priorities in tropical forests and temperate grasslands where ECM hotspots align poorly with diversity peaks. The Underground Atlas v1.0 provides open-access visualizations of AM and ECM distributions, highlighting endemic clusters vulnerable to . Such mapping informs targeted interventions, including zoning for low-impact agriculture and restoration corridors, while continuous monitoring via molecular surveys addresses data gaps in underrepresented regions. Emerging tools like machine learning-enhanced extrapolations underscore biases in current protections, urging policy shifts to safeguard underground potentials estimated at billions of tons globally.

Emerging Research Frontiers

Recent genomic studies have identified key genes involved in uptake and symbiotic establishment in mycorrhizal fungi, providing targets for enhancing plant productivity in . For instance, analyses of arbuscular mycorrhizal (AM) fungal genomes reveal mechanisms for acquisition, challenging traditional market exchange models by showing higher supply in phosphorus-rich soils. Small RNA-mediated has emerged as a critical layer in AM symbiosis, with 2024 research demonstrating its role in modulating host-fungal interactions for improved stress tolerance. Ecological research frontiers extend to macro-scale processes, including fungal community assembly in dynamic environments like forelands, where rapid colonization by ectomycorrhizal fungi occurs within decades of ice retreat. Mycorrhizal networks are increasingly linked to sequestration, with frameworks proposed in 2024 connecting AM fungi to stabilization and feedback loops in diversity. Nano-scale techniques, such as nanoSIMS, track carbon allocation from plants to fungi, revealing precise flux dynamics under varying conditions. In agricultural applications, advances in commercial AM fungal inoculants focus on species like Rhizophagus irregularis and Funneliformis mosseae, produced via root organ cultures or to improve propagule viability and field efficacy. The global market for these products reached approximately $995 million USD in 2024, driven by demand for inputs that reduce use and enhance resilience to and . Emerging mycorrhization protocols enable controlled , boosting production and resistance in nursery plants. Future directions emphasize integrating molecular signaling with modeling to predict mycorrhizal responses to , including optimized inoculant formulations to minimize displacement of native fungi and tailored applications for diverse crops. Research also targets regulators of evolution and trait-based approaches for consistent AM fungal performance across soils.

References

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