Myrmecochory
Myrmecochory (
Distribution and diversity
Myrmecochory is exhibited by more than 3,000 plant
Evolutionary history
Myrmecochory has evolved independently many times in a large number of plant families. A recent phylogenetic study identified more than 100 separate origins of myrmecochory in 55 families of flowering plants.[4][7] With many independent evolutionary origins, elaiosomes have evolved from a wide variety of parent tissues.[6] Strong selective pressure or the relative ease with which elaiosomes can develop from parent tissues may explain the multiple origins of myrmecochory.[7] These findings identify myrmecochory as a prime example of convergent evolution. In addition, phylogenetic comparison of myrmecochorous plant groups reveals that more than half of the lineages in which myrmecochory evolved are more species-rich than their nonmyrmecochorous sister groups. Not only is myrmecochory a convergent trait, but it also promotes diversification in multiple flowering plant lineages.[4]
Ecology
Myrmecochory is usually classified as a
Few studies have examined the costs and benefits to ants participating in myrmecochory. Much remains to be understood about the selective advantages conferred upon myrmecochorous ants.[9]
No single hypothesis explains the evolution and persistence of myrmecochory. Instead, a combination of beneficial effects working at different spatiotemporal scales likely contribute to the viability of this predominantly mutualistic interaction. Three commonly cited advantages to myrmecochorous plants are increased dispersal distance, directed dispersal, and seed predator avoidance.
Dispersal distance
Increasing dispersal distance from the parent plant is likely to reduce seed mortality resulting from density-dependent effects.[10] Ants can transport seeds as far as 180 m[11] but the average is less than 2 m, and values between 0.5 and 1.5 m are most common.[6] Perhaps due to the relatively limited distance that ants disperse seeds, many myrmecochores exhibit diplochory, a two-staged dispersal mechanism, often with ballistic projection as the initial mechanism, that can increase dispersal distance by as much as 50%.[2][6] In some cases, ballistic dispersal distance regularly exceeds that of transport by ants.[12] The dispersal distance achieved through myrmecochory is likely to provide an advantage proportionate to the spatial scale of density-dependent effects acting on individual plants. As such, the relatively modest distances ants transport seeds are likely to be more advantageous for myrmecochorous shrubs, forbs, and other plants of small stature.[9]
Directed dispersal
Myrmecochorous plants may benefit when ants disperse seeds to nutrient-rich or protected microsites that enhance germination and establishment of seedlings. Ants disperse seeds in fairly predictable ways, either by disposing of them in underground middens or by ejecting them from the nest.[2] These patterns of ant dispersal are predictable enough to permit plants to manipulate animal behaviour and influence seed fate,[13] effectively directing the dispersal of seeds to desirable sites. For example, myrmecochores can influence seed fate by producing rounder, smoother diaspores that inhibit ants from redispersing seeds after elaiosome removal. This increases the likelihood that seeds will remain underground instead of being ejected from the nest.[14]
Nest chemistry is ideally suited for seed germination given that ant colonies are typically enriched with plant nutrients such as phosphorus and
Seed predator avoidance
Myrmecochorous plants escape or avoid seed predation by granivores when ants remove and sequester diaspores.[2] This benefit is particularly pronounced in areas where myrmecochorous plants are subject to heavy seed predation, which may be common. In mesic forest habitats, seed predators remove around 60% of all dispersed seeds within a few days, and eventually remove all seeds not removed by ants.[12][16] In addition to attracting ants, elaiosomes also appeal to granivores, and their presence can increase seed predation rates.[9]
Nature of the interaction
Myrmecochory is traditionally thought to be a diffuse or facultative
Ants, however, do not appear to form obligate relationships with myrmecochorous plants. Since no known ant species relies entirely on elaiosomes for their nutritional needs, ants remain generalist foragers even when entering into relationships with a more specialized myrmecochore.[16]
As with many other facultative mutualisms, cheating is present on both sides of the interaction. Ants cheat by consuming elaiosomes without transporting seeds or through outright seed predation. Myrmecochorous plants can also cheat, either by producing diaspores with nonremovable elaiosomes or by simulating the presence of a nonexistent reward with chemical cues. Ants are sometimes capable of discriminating between cheaters and mutualists as shown by studies demonstrating preference for the diaspores of noncheating myrmecochores.[18] Cheating is also inhibited by ecological interactions external to the myrmecochorous interaction; simple models suggest that predation exerts a stabilizing influence on a mutualism such as myrmecochory.[16]
Myrmecochory and invasive species
Myrmecochores are threatened by invasive species in some ecosystems. For instance, the Argentine ant is an aggressive invader capable of displacing native ant populations. Since Argentine ants do not disperse seeds, invasions may lead to a breakdown in the myrmecochory mutualism, inhibiting the dispersal ability of myrmecochores and causing long-term alterations in plant community dynamics.[19][20] Invasive ant species can also maintain seed dispersal in their introduced range, as is the case with the red fire ant in the Southeastern United States.[21] Some invasive ants are also seed-disperses in their native range, such as the European fire ant, and can act as a high-quality disperser in their introduced range [22]
In South Africa, the Argentine ant has in some cases displaced native ants that disperse the seeds of
Myrmecochorous plants are also capable of invading ecosystems. These invaders may gain an advantage in areas where native ants disperse invasive seeds. Similarly, the spread of myrmecochorous invaders may be inhibited by limitations in the ranges of native ant populations.[24]
See also
References
- ISBN 9780520948433.
- ^ a b c d e f g h Beattie, A.J. (1985). The Evolutionary Ecology of Ant-Plant Mutualisms. Cambridge University Press, Cambridge U.K.
- ^ Beattie, A.J. and Hughes, L. (2002). “Ant–plant interactions” In Plant–Animal Interactions and Evolutionary Approach, (eds C. M. Herrera & O. Pellmyr), pp. 211–35. Blackwell Science, Oxford.
- ^ doi:10.1016/j.ppees.2009.08.001. Archived from the original(PDF) on 2011-07-21. Retrieved 2010-09-15.
- ^ Westoby, Mark, L. Hughes, and B.L. Rice (1991). “Seed dispersal by ants; comparing infertile with fertile soils.” In Ant-plant interactions, Camilla R. Huxley and David F. Cutler (eds.), pp. 434-447, Oxford University Press, New York.
- ^ a b c d Buckley, R.C. (1982). “Ant-plant interactions: a world review” In Ant-plant interactions in Australia, Buckley R.C. (ed.), pp. 111-141, Dr W. Junk Publishers, The Hague.
- ^ PMID 19436714.
- ^ Westoby, Mark., Barbara Rice, Julia M. Shelley, David Haig, and J.L. Kohen (1982). “Plants' use of ants for dispersal at West Head, New South Wales” In Ant-plant interactions in Australia, Buckley R.C. (ed.), pp. 75-87, Dr W. Junk Publishers, The Hague.
- ^ .
- S2CID 84490190.
- .
- ^ JSTOR 2259181.
- ^ Hanzawa, F.M., Beattie, A.J., and Culver, D.C. (1988). “Directed dispersal: demographic analysis of an ant-plant mutualism”. The American Naturalist, 131(1): 1-13.
- S2CID 7093586.
- PMID 21067420.
- ^ a b c d Heithaus, E.R., Culver, D.C., and Beattie, A.J.. (1980). “Models of some ant-plant mutualisms”. The American Naturalist 116(3): 347-361.
- ^ PMID 19967857.
- .
- S2CID 26506155.
- S2CID 1789520.
- S2CID 12979775.
- PMID 25540283.
- ISSN 0012-9658.
- S2CID 42782201.
External links
- Media related to Myrmecochory at Wikimedia Commons
- Hallam, Jacque. "Flowers and Ants". Illinois Department of Natural Resources. Retrieved 20 January 2022.