Biology:Temporal plasticity

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Temporal plasticity, also known as fine-grained environmental adaptation,[1] is a type of phenotypic plasticity that involves the phenotypic change of organisms in response to changes in the environment over time. Animals can respond to short-term environmental changes with physiological (reversible) and behavioral changes; plants, which are sedentary, respond to short-term environmental changes with both physiological and developmental (non-reversible) changes.[2] Temporal plasticity takes place over a time scale of minutes, days, or seasons, and in environments that are both variable and predictable within the lifespan of an individual. Temporal plasticity is considered adaptive if the phenotypic response results in increased fitness.[3]  Non-reversible phenotypic changes can be observed in metameric organisms such as plants that depend on the environmental condition(s) each metamer was developed under.[1] Under some circumstances early exposure to specific stressors can affect how an individual plant is capable of responding to future environmental changes (Metaplasticity).[4]

Reversible plasticity

A reversible change is defined as one that is expressed in response to an environmental stressor but returns to a normal state after the stress is no longer present.[5] Reversible changes are more likely to be adaptive for an organism when the stress driving the change is temporary and the organism is likely to be exposed to it again within its lifetime.[6] Reversible plasticity often involves changes in physiology or behavior. Perennial plants, which often experience recurring stresses in their environment due to lack of mobility, benefit greatly from reversible physiological plasticity such as changes in resource uptake and allocation.[7] When essential nutrients are low, root and leaf resorption rates can increase, persisting at a high rate until there are more nutrients available in the soil and resorption rates can return back to their normal state.[8]

Irreversible plasticity

Irreversible changes are described as changes that remain expressed in an organism after the environmental stress has ceased.[5] Environmental shifts that drive irreversible plasticity in an organism tend to be less rapidly changing, such as gradually increasing temperatures. This often leads to permanent changes in morphology or in the developmental process of an organism (developmental plasticity).[9] Plants are highly plastic and tend to express many irreversible developmental changes, such as shifts in timing of bud and flower development.[10] In animals, many organisms benefit from having multiple persisting morphs in a population that arise during development in response to environmental conditions. For example, freshwater snails will form more spherical shells when in the presence of a predator (bluegill sunfish) and conical shells when predators are absent.[11] These shell shapes are permanent and cannot be reverted, even if the predator status of the snail's environment changes.

Examples

Morphologically and developmentally plastic traits can be reversible in some cases, and there are some physiological responses which can be irreversible, which differs from the typical trend. One example of developmental plasticity that is reversible is the shift in mouth form of roundworm, Pristionchus pacificus, when exposed to a changes in food type and availability.[12] A second example of reversible developmental plasticity is the length of Galapagos marine iguanas, Amblyrhynchus cristatus, in response to El Niño weather conditions. During El Niño seasons, the algal food supply decreases, but increases during La Niña seasons. This change in food availability coincides with the changes in iguana size during the season.[13]

A unique and complex example of plasticity is camouflage, an adaption that allows animals to avoid predators by hiding in plain sight.[14] The mechanisms behind camouflage are not the same in all species - they can be morphological, physiological, behavioral, or even a combination of traits.[15] Camouflage can also be irreversible or reversible, depending on the species. Camouflage can be irreversible when color patterns or other morphological traits are set during development. However, camouflage can also be reversible, with color, texture, and behavioral changes occurring in response to immediate threats (e.g., Mimic octopus).

In some cases, the exact same change in phenotype can be reversible in one species and irreversible in another. For example, both pea and wheat plants express changes in root growth due to environmental cues, but the changes are permanent only for wheat.[16] Sometimes this can even occur within the same species, due to the largely unpredictable results of interactions between an individual's genetic make-up and their specific environmental experiences.[17]

Leaf development

Dicerandra linearifolia leaves grown at the beginning of its development, with lower ambient temperature, are thicker, wider, and possess less stomata than those grown later in the same year.[1]

Root density

In times of sporadic nutrient availability, fine root density increases in order to more efficiently absorb nutrients. In times of water inundation, plants will increase root mass in response to make use of the excess water in the environment.[4]

Nutrient resorption

Plants are capable of adjusting the degree nutrients are reabsorbed from their leaves. Resorption tends to be incomplete in nutrient-rich environments, and conversely nutrient poor environments often trigger complete resorption in plants.[8]

Leaf morphology

Leaves grown during the dry season differ than those grown in wetter seasons. The leaves differ in their shape (leaves grown during the dry season were longer and narrower in comparison to those grown during the wet season), possessed higher trichome density, and lower anthocyanin levels.[18]

References

  1. 1.0 1.1 1.2 "Adaptation to Fine-Grained Environmental Variation: An Analysis of Within-Individual Leaf Variation in an Annual Plant". Evolution; International Journal of Organic Evolution 50 (3): 1111–1118. June 1996. doi:10.2307/2410651. PMID 28565263. 
  2. "Shade-induced plasticity in invasive Impatiens glandulifera populations". Weed Research 60: 16–25. 23 May 2019. doi:10.1111/wre.12394. http://connection.ebscohost.com/c/articles/141335477. 
  3. "The relative advantages of plasticity and fixity in different environments: when is it good for a plant to adjust?". Evolutionary Ecology 16 (3): 285–297. 2002. doi:10.1023/A:1019684612767. ProQuest 750494735. Bibcode2002EvEco..16..285A. https://www.proquest.com/docview/750494735. 
  4. 4.0 4.1 "Experience of inundation or drought alters the responses of plants to subsequent water conditions" (in en). Journal of Ecology 105 (1): 176–187. Jan 2017. doi:10.1111/1365-2745.12649. Bibcode2017JEcol.105..176W. 
  5. 5.0 5.1 "Characterization, costs, cues and future perspectives of phenotypic plasticity". Annals of Botany 130 (2): 131–148. September 2022. doi:10.1093/aob/mcac087. PMID 35771883. 
  6. "How stress selects for reversible phenotypic plasticity". Journal of Evolutionary Biology 18 (4): 873–883. July 2005. doi:10.1111/j.1420-9101.2005.00959.x. PMID 16033559. 
  7. "Importance of plasticity and decision-making strategies for plant resource acquisition in spatio-temporally variable environments". The New Phytologist 174 (1): 182–193. January 2007. doi:10.1111/j.1469-8137.2007.01969.x. PMID 17335508. 
  8. 8.0 8.1 "Global temporal patterns in plant nutrient resorption plasticity" (in en). Global Ecology and Biogeography 28 (6): 728–743. February 2019. doi:10.1111/geb.12885. ISSN 1466-822X. Bibcode2019GloEB..28..728D. https://collected.jcu.edu/fac_bib_2019/64. 
  9. "The role of developmental plasticity in evolutionary innovation". Proceedings. Biological Sciences 278 (1719): 2705–2713. September 2011. doi:10.1098/rspb.2011.0971. PMID 21676977. 
  10. "Developmental plasticity in plants". Cold Spring Harbor Symposia on Quantitative Biology 77: 63–73. 2012-01-01. doi:10.1101/sqb.2012.77.014720. PMID 23250989. 
  11. "Freshwater snail responses to fish predation integrate phenotypic plasticity and local adaptation" (in en). Aquatic Ecology 54 (1): 309–322. 2020. doi:10.1007/s10452-019-09744-x. ISSN 1386-2588. Bibcode2020AqEco..54..309G. 
  12. "Environmental influence on Pristionchus pacificus mouth form through different culture methods". Scientific Reports 7 (1): 7207. August 2017. doi:10.1038/s41598-017-07455-7. PMID 28775277. Bibcode2017NatSR...7.7207W. 
  13. Wikelski, Martin; Thom, Corinna (January 2000). "Marine iguanas shrink to survive El Niño" (in en). Nature 403 (6765): 37–38. doi:10.1038/47396. ISSN 1476-4687. PMID 10638740. Bibcode2000Natur.403...37W. https://www.nature.com/articles/47396. 
  14. "Camouflage in predators". Biological Reviews of the Cambridge Philosophical Society 95 (5): 1325–1340. October 2020. doi:10.1111/brv.12612. PMID 32410297. 
  15. "Camouflage through colour change: mechanisms, adaptive value and ecological significance". Philosophical Transactions of the Royal Society of London. Series B, Biological Sciences 372 (1724): 20160342. July 2017. doi:10.1098/rstb.2016.0342. PMID 28533459. 
  16. "Reversible and irreversible root phenotypic plasticity under fluctuating soil physical conditions" (in en). Environmental and Experimental Botany 188: 104494. 2021-08-01. doi:10.1016/j.envexpbot.2021.104494. ISSN 0098-8472. 
  17. "Dissection of the molecular bases of genotype x environment interactions: a study of phenotypic plasticity of Saccharomyces cerevisiae in grape juices". BMC Genomics 19 (1): 772. November 2018. doi:10.1186/s12864-018-5145-4. PMID 30409183. 
  18. "Plastic responses to temporal variation in moisture availability: consequences for water use efficiency and plant performance". Oecologia 153 (4): 821–832. October 2007. doi:10.1007/s00442-007-0794-z. PMID 17636336. Bibcode2007Oecol.153..821P.