Astragalus nitidiflorus

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Astragalus nitidiflorus
Astragalus nitidiflorus.jpg
Scientific classification OOjs UI icon edit-ltr.svg
Kingdom: Plantae
Clade: Tracheophytes
Clade: Angiosperms
Clade: Eudicots
Clade: Rosids
Order: Fabales
Family: Fabaceae
Subfamily: Faboideae
Genus: Astragalus
Species:
A. nitidiflorus
Binomial name
Astragalus nitidiflorus
Jiménez & Pau

Astragalus nitidiflorus is a species of legume in the family Fabaceae. It is endemic to Cartagena, southeast of Spain. It was refound after about 100 years of extinction and "the reappearance of this species has awakened the interest of environmental managers because the reasons for its critical situation are unknown". [2] In 2004, a group of 46 specimens were discovered in a protected area between Cartagena and Mazarrón and plans for the conservation of this species have been implemented.[ citation needed ] ISSR markers helped to find that Astragalus nitidiflorus has a low genetic diversity. [3] "This species grows in shallow soil from metamorphic and volcanic rocks in between mountain and cultivated areas". [3]

Contents

Astragalus nitidiflorus is arranged in five spatially separated populations with about two thousand specimens. To increase this plants population size a natural regeneration has to occur. Early in 2005 demographic studies about Astragalus nitidiflores identified roughly 69 adult plants". [3]

Its natural habitat is Mediterranean-type shrubby vegetation. This plant was first described in 1909, and was believed to be extinct.

Most of the individuals are preserved in a protected area called "Cabezos del Pericón", a Site of Community Importance included in the Natura 2000 ecological network.[ citation needed ]

Description

Astragalus nitidiflorus is endemic to the province of Murcia (southern Spain), where it forms the only known metapopulation worldwide. It is classified as Extinct in accordance with IUCN (2006) criteria. [4]

Etymology

Nitidiflorus: Latin epithet meaning "bright with flowers".

Biology

The life cycle of A. nitidiflorus begins with seeds, which germinate in autumn and winter. In summer, leaves and stems die and only a few buds remain at the base of the stem at ground level. After the autumn rains, the dormant buds of the P1 plants that have survived the summer sprout and begin a second stage of growth. [5]

A. nitidiflorus is a short-lived legume that colonizes old fields on volcanic soils. Most seeds and fruits were distributed in the soil surface layer (Table S1), and, except for 2011, most seeds were found inside fruits. This is explained by the type of fruit of A. nitidiflorus, an indehiscent and hard legume that prevents rapid release of seeds, which remain some years inside the fruit. Moreover, the considerable size of these fruits (ca. 1.9 cm 0.8 cm) hampers their burial, and nearly 100% them were on the soil surface. [4]

"The life cycle of this species is very weak due to its low germination and limited adult species Extreme climate conditions can lead to a decrease in population.". [6]

Habitat and cultivation

The seed bank is poor and very sensitive to changes in population size. The indehiscent fruit determines seed distribution in the soil around its mother plants. "A. nitidiflorus is able to form a short-term persistent soil seed bank". [4] The seeding process happens in the summer months when there is a surplus water supply. [3]

Beneficial uses

Not only with the Astragalus nitidiflorus, but most of the Astragalus plants have a plethora uses. Ranging from medicinal purposes, like helping treat the common cold or allergies, to feeding plants because of its good animal nutrition or the roots being good for controlling erosion. [7]

Threats to species

"Natural regeneration is not expected for patches where the species disappeared few years ago". [4]

Conservation

After the reappearance of this plant, the regional government of Murcia has declared this species as endangered. The known populations are under the protection of LIC of losCabezos Pericón spaces and the natural park of Sierra de la Muela, Cabo Tiñoso and Roldan. Some specimens also appear nearby the Black Cabeza de Tallante, that is close to an extinct Quaternary volcano, Cabezos Pericón. The population in the south-facing slopes part of Cabezos Pericón has been proposed as botany micorreserva with the name " Perez scrub the Netherlands '. The populations is also already protected as a Site of Community Importance (SCI ). [6] One of the main goals in conserving this plant is preserving the genetic diversity of the endangered species Long-term survival and the evolution of species depends on the maintenance of genetic connectivity To maintain this plant’s population habitat destruction must be prevented. Attempts to save this plant along with many of the other Astragalus plants have been made through the use of Thidiazuron. This is because of the plant’s naturally slow seedling development and seed germination. A chemical which is a plant growth regulator which helps the plants be stronger and grow faster. This has been shown to help the plants grow even sterile seedlings but the sterile seedlings did not have healthy development. The regenerated shoots, however, had much more success and are even able to be transferred to another place. However, this chemical does have negative side-effects such as hyperhydricity and poor shoot development which can occur but do not always present itself. [7]

Comparison with A. gines-lopezii

Astragalus gines-lopezii, A.nitidiflorus and A. devesae were described as the same species which was A. nitidiflorus. A. gines-lopezii is one of the phylogenetically closest species to A. nitidiflorus. A. nitidiflorus has a very high reproductive capacity on the production of flowers and seeds than A. gineslopezii. On the contrary, the proportion of flowers setting ripe fruits in A. gines-lopezii is higher compare to than in A. nitidiflorus. [8]

Related Research Articles

This is an index of conservation topics. It is an alphabetical index of articles relating to conservation biology and conservation of the natural environment.

<span class="mw-page-title-main">Seed bank</span> Backup seed storage

A seed bank stores seeds to preserve genetic diversity; hence it is a type of gene bank. There are many reasons to store seeds. One is to preserve the genes that plant breeders need to increase yield, disease resistance, drought tolerance, nutritional quality, taste, etc. of crops. Another is to forestall loss of genetic diversity in rare or imperiled plant species in an effort to conserve biodiversity ex situ. Many plants that were used centuries ago by humans are used less frequently now; seed banks offer a way to preserve that historical and cultural value. Collections of seeds stored at constant low temperature and low moisture are guarded against loss of genetic resources that are otherwise maintained in situ or in field collections. These alternative "living" collections can be damaged by natural disasters, outbreaks of disease, or war. Seed banks are considered seed libraries, containing valuable information about evolved strategies to combat plant stress, and can be used to create genetically modified versions of existing seeds. The work of seed banks often span decades and even centuries. Most seed banks are publicly funded and seeds are usually available for research that benefits the public.

<i>Ex situ</i> conservation Preservation of plants or animals outside their natural habitats

Ex situ conservation literally means, "off-site conservation". It is the process of protecting an endangered species, variety or breed, of plant or animal outside its natural habitat; for example, by removing part of the population from a threatened habitat and placing it in a new location, an artificial environment which is similar to the natural habitat of the respective animal and within the care of humans, example are zoological parks and wildlife sanctuaries. The degree to which humans control or modify the natural dynamics of the managed population varies widely, and this may include alteration of living environments, reproductive patterns, access to resources, and protection from predation and mortality. Ex situ management can occur within or outside a species' natural geographic range. Individuals maintained ex situ exist outside an ecological niche. This means that they are not under the same selection pressures as wild populations, and they may undergo artificial selection if maintained ex situ for multiple generations.

<i>Banksia cuneata</i> Endangered species of flowering plant

Banksia cuneata, commonly known as matchstick banksia or Quairading banksia, is an endangered species of flowering plant in the family Proteaceae. Endemic to southwest Western Australia, it belongs to Banksia subg. Isostylis, a sub-genus of three closely related Banksia species with inflorescences or flower clusters that are dome-shaped heads rather than characteristic Banksia flower spikes. A shrub or small tree up to 5 m (16 ft) high, it has prickly foliage and pink and cream flowers. The common name Matchstick Banksia arises from the blooms in late bud, the individual buds of which resemble matchsticks. The species is pollinated by honeyeaters (Meliphagidae).

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<i>Cupressus abramsiana</i> Species of conifer

The Santa Cruz cypress is a species of North American tree within the Cypress family. The species is endemic to the Santa Cruz Mountains within the Santa Cruz and San Mateo counties of west-central California. The U.S. Fish and Wildlife Service listed the species on the Endangered Species Act in 1987 due to increasing threats from habitat loss and disruption of natural forest fire regimes. In 2016, the conservation status of the Santa Cruz cypress changed to Threatened. The cited reasoning was a decrease in threats against their habitat.

<i>Banksia brownii</i> Species of shrub in the family Proteaceae found in Australia

Banksia brownii, commonly known as feather-leaved banksia or Brown's banksia, is a species of shrub that grows in southwest Western Australia. A plant with fine feathery leaves and large red-brown flower spikes, it usually grows as an upright bush around two metres (6.6 ft) high, but can also occur as a small tree or a low spreading shrub. First collected in 1829 and published the following year, it is placed in Banksiasubgenus Banksia, section Oncostylis, series Spicigerae. There are two genetically distinct forms.

The soil seed bank is the natural storage of seeds, often dormant, within the soil of most ecosystems. The study of soil seed banks started in 1859 when Charles Darwin observed the emergence of seedlings using soil samples from the bottom of a lake. The first scientific paper on the subject was published in 1882 and reported on the occurrence of seeds at different soil depths. Weed seed banks have been studied intensely in agricultural science because of their important economic impacts; other fields interested in soil seed banks include forest regeneration and restoration ecology.

<i>Ravenea</i> Genus of palms

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<i>Astragalus bibullatus</i> Species of legume

Astragalus bibullatus, the limestone glade milkvetch or Pyne's ground plum, is an endangered species of flowering plant that is endemic to the cedar glades of the central basin of Tennessee in the United States. It is found in only eight populations located within a few kilometers of each other in Rutherford County, Tennessee.

The ecology of Banksia is the relationships and interactions among the plant genus Banksia and its environment. Banksia has a number of adaptations that have so far enabled the genus to survive despite dry, nutrient-poor soil, low rates of seed set, high rates of seed predation and low rates of seedling survival. These adaptations include proteoid roots and lignotubers; specialised floral structures that attract nectariferous animals and ensure effective pollen transfer; and the release of seed in response to bushfire.

Myristica andamanica is a species of plant in the family Myristicaceae. It is endemic to the Andaman and Nicobar Islands. Recent studies by Waman and Bohra (2020) suggested that the seeds can regenerate on their own if they remain undisturbed in soil and favourable microclimatic conditions are available. However, to ensure regular production of seedlings, assisted regeneration was recommended. Retention of seed hull and use of sinking seeds gives high germination percentage. Soaking of seeds in water for 24 h prior to sowing improved germination.

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References

  1. Sánchez Gómez, P.; Carrión Vilches, M.Á.; Galicia Herbada, D. (2006). "Astragalus nitidiflorus". IUCN Red List of Threatened Species . 2006: e.T61652A12533286. doi: 10.2305/IUCN.UK.2006.RLTS.T61652A12533286.en . Retrieved 14 November 2021.
  2. Martínez-Sánchez, Juan J.; Segura, Francisco; Aguado, Mayra; Franco, José A.; Vicente, María J. (2011). "Life history and demographic features of Astragalus nitidiflorus, a critically endangered species". Flora - Morphology, Distribution, Functional Ecology of Plants. 206 (5): 423–432. doi:10.1016/j.flora.2010.11.006.
  3. 1 2 3 4 Vicente, María J.; Segura, Francisco; Aguado, Mayra; Migliaro, Daniele; Franco, José A.; Martínez-Sánchez, Juan J. (2011). "Genetic diversity of Astragalus nitidiflorus, a critically endangered endemic of SE Spain, and implications for its conservation". Biochemical Systematics and Ecology. 39 (3): 175–182. doi:10.1016/j.bse.2011.03.005.
  4. 1 2 3 4 Segura, Francisco; Martínez-Sánchez, Juan J.; Aguado, Mayra; Franco, José A.; Vicente, María J. (2014). "Could recently locally extinct population patches of Astragalus nitidiflorus regenerate from the soil seed bank?". Journal of Arid Environments. 110: 75–78. Bibcode:2014JArEn.110...75S. doi:10.1016/j.jaridenv.2014.07.002. hdl: 10317/10860 .
  5. Martínez-Sánchez, Juan J.; Segura, Francisco; Aguado, Mayra; Franco, José A.; Vicente, María J. (2011). "Life history and demographic features of Astragalus nitidiflorus, a critically endangered species". Flora - Morphology, Distribution, Functional Ecology of Plants. 206 (5): 423–432. doi:10.1016/j.flora.2010.11.006.
  6. 1 2 Vicente, María J.; Segura, Francisco; Aguado, Mayra; Migliaro, Daniele; Franco, José A.; Martínez-Sánchez, Juan J. (2011). "Genetic diversity of Astragalus nitidiflorus, a critically endangered endemic of SE Spain, and implications for its conservation". Biochemical Systematics and Ecology. 39 (3): 175–182. doi:10.1016/j.bse.2011.03.005.
  7. 1 2 M. Yorgancilar; S. Erisen (2011). "THE EFFECT OF THIDIAZURON (TDZ) ON SHOOT REGENERATION OF ASTRAGALUS SCHIZOPTERUS" (PDF). The Journal of Animal and Plant Sciences. 21 (3): 519–524. ISSN   1018-7081 . Retrieved 16 March 2022.
  8. "Archived copy" (PDF). Archived from the original (PDF) on 22 October 2014. Retrieved 22 October 2014.{{cite web}}: CS1 maint: archived copy as title (link)

Sources