American Journal of Plant Sciences
Vol.06 No.19(2015), Article ID:61880,12 pages
10.4236/ajps.2015.619309

Conservation of Endangered Species: Androsace mathildae Levier (Primulaceae) in Central Italy

Paolo Fasciani1,2, Loretta Pace1,2*

1Department of Life, Health & Environmental Sciences, University of L’Aquila, L’Aquila, Italy

2Alpine Botanical Garden “V. Rivera”, University of L’Aquila, L’Aquila, Italy

Copyright © 2015 by authors and Scientific Research Publishing Inc.

This work is licensed under the Creative Commons Attribution International License (CC BY).

http://creativecommons.org/licenses/by/4.0/

Received 7 November 2015; accepted 11 December 2015; published 14 December 2015

ABSTRACT

Climate change influences the distribution of species, causing the displacement of distribution areas, both in altitude and latitude. The potentially most climate change-susceptible taxa are those of mountain peaks, with limited distribution areas, such as rare or endemic species. In this paper, we deepened the study of Androsace mathildae Levier, a plant that lives in Central Italy over 2500 m asl. This species, classified as a rare plant according to the Red List of Plants of Italy, is included in Appendix I of the Bern Convention, Annex II and IV Habitats Directive 92/43 CEE, and is protected under Regional Law n. 45/79 of the Abruzzo Italian Region. In order to preserve A. mathildae, morphological observations and ex situ preservation have been performed. Results indicate that the germination of seeds increases in the presence of extracts of humic acids obtained by the decomposition of the lower leaves of the plant. The presence of Pyrenophora bromi (Ascomyta) on the leaves as a decomposition agent, has never been reported either on A. mathildae or at these altitudes. A number of experiments to obtain callus induction and neomorphogenesis were conducted to identify suitable procedures for in vitro stabilization. The obtained shoots had a high number of lateral buds (6.3 per plant, on average) which were used to increase the number of clones present in the growth chamber within a few sub-culture passages. This in vitro material will be used in cryopreservation and to improve the restocking activity of A. mathildae.

Keywords:

Biodiversity, Alpine Botanical Garden, Morphology, In Vitro Preservation

1. Introduction

EU Habitats Directive 92/43 identified the species of European Community (EC) interest whose conservation requires strict protection (Annex II-IV). Preservation, protection and improvement of the quality of the environment, including the conservation of natural habitats and flora, represent a fundamental general interest objective of the EC.

Conservation of endemic species requires a thorough knowledge of their biological and morphological features in order to define an appropriate strategy. The case study presented herein highlights how conventional strategies of propagation, such as the germination of seeds, do not prove to be efficient without the use of germplasm ex-situ conservation techniques.

Androsace mathildae Levier is a glacial relict present on a few stations in the Gran Sasso and Majella Mountains, so it is classified as a rare plant according to the Red List of Plants of Italy, it is further included in Appendix I of the Bern Convention, in Annex II and IV of Habitats Directive 92/43 CEE and it is protected under Regional Law n. 45/79 of the Abruzzo Italian Region [1] - [3] .

Alpine plants respond to the harsh environment with a high degree of specialization [4] .

A noteworthy aspect in plant survival at high altitude relates to the snow cover, that determines the distribution of plant species in the alpine zone. The snow cover has protective effects for the plants, consisting in the prevention of exposure to low temperatures, winter desiccation, ice blast and solar radiation (potentially dangerous to dormant tissue). However, prolonged life under the snow requires resistance to physico-chemical stresses and snowbed pathogens. In particular, the snow cover affects the phenorhythm of the plants, which need to have sufficient carbon reserves to overcome the prolonged winter and for clonal or reproductive propagation [4] . Vegetative shoot apices and leaf meristems in most alpine plants are buried several centimeters below the ground and thus are not exposed to low and high temperature extremes.

The snow cover and the paucity of humus present in the cracks where Androsace mathildae lives cause water stress due to reduced water availability. Alpine plants acquire water and mineral resources from substrates which differ in many respects from those common at lower altitudes. The grain size distribution found in alpine soil depends strongly on parent material.

By avoiding nucleation, a process called supercooling allows leaf and stem tissues to cool below freezing point without freezing. This process is favored by compartmentalization of plant water into cells and vessels, by cell wall impregnation with lignin and by the absence of particles which could initiate the crystallization process [4] .

The high capacity of clonal propagation in these high altitude species is due to the adjustments that the plants have developed to protect themselves from frost. In fact, the late frosts at high altitudes endanger the blooms and thus the possibility of sexual reproduction [5] . The compression of live zone and the small scale patterns of life conditions in steep alpine terrain represent natural experiments which provide unbeaten opportunities to study the plant adaptation and the mechanisms for survival of physical stress conditions [6] [7] .

The potentially most climate change-susceptible taxa are those of mountain peaks, with limited distribution areas, such as rare or endemic species [8] . The alpine flora is at risk of extinction in the European mountains, especially where there is no possibility of moving to a higher altitude (low and hot mountains, as Prealps and the Northern Apennines). Species occurring in isolated populations at the highest peaks of the Apennines, such as A. mathildae, are also at risk [9] . For conservation purposes, the plant is currently maintained as a small number of individuals in the flower beds in the Alpine Botanical Garden of Campo Imperatore. This garden is located in the Gran Sasso massif, within the “Gran Sasso e Montidella Laga” National Park, at 2117 m asl; thus its peculiar location makes it ideal for in situ conservation of Central Appennine high altitude species. The living plant collections and, increasingly, seed banks and cryopreserved tissue cultures maintained by botanic gardens, form a significant ex situ reservoir of endangered plants [10] [11] .

Today several botanical gardens use in vitro techniques in germplasm conservation, and long-term storage of material in culture for potential applications of cryopreservation [12] .

Androsace mathildae can be found in the cracks of limestone at an altitude between 2500 and 2900 m asl [13] . Its discovery dates back to 1875 and it is ascribed to the Swiss naturalist E. Levier while he was hiking on the Gran Sasso Mountain. He dedicated the plant to his wife Mathilde, since she saw it first, and he performed the early studies on its iconography and botanical characteristics [14] .

The genus Androsace L., (Primulaceae) comprises about 150 species distributed in extra-tropical mountain ranges of the Northern hemisphere. They are particularly common in the temperate-cold regions of the Arctic and in Asia, North America and Europe (Alps and Pyrenees) [15] [16] .

A. mathildae, a European member of Aretia, is a nano-chamaephyte present in the higher peaks of the Central Appennines [17] [18] ; it is a perennial cushion plant, up to 3 cm high, with single rosettes or forming a cushion with a diameter no larger than 3 - 5 cm. The leaves are basal, lanceolate, shiny green and glabrous except for a few hairs at the leaf tips. The flowers are axillary, single, and the pedicel is often curved when fruiting. The calyx is green, with a stellate pubescence, and the corolla has white petals with a yellow eye. The fruit ripens in late summer and contains from three to seven seeds (generally five), which upon falling end up inside the leaves of the basal rosette or slightly away from it; the flowering time occurs in June-July [19] - [21] .

Until recently, it was believed that Androsace mathildae was also present in the mountains of the Balkan peninsula (M. Komovi, Montenegro) [22] . The molecular phylogeographical investigations on the European members of Aretia by amplified fragment length polymorphism (AFLP) markers revealed a strong genetic divergence between the Italian and the Montenegrin populations. The study led to the establishment of a new species called A. komovensis sp. nov., which morphologically resembles A. mathildae Levier from the Abruzzo mountains (Italy), but differs in the persistent, dense and regular indumentums of the leaf margin [23] . Furthermore, molecular phylogenetic data indicate that A. komovensis is not closely related to A. mathildae Levier, but instead it is a sister species to the Eastern Alpine endemic A. hausmanni Leyb. [23] .

We invested great effort in a comprehensive study about this Primulacea in order to describe its morphological and ecological characteristics. A number of experiments to obtain callus induction and neomorphogenesis were conducted to identify suitable procedures for in vitro preservation of A. mathildae. This in vitro material will be useful in cryopreservation and improvement of restocking activity.

2. Materials and Methods

2.1. Plant Material

The material used for the study of A. mathildae was collected in late summer from 2008 to 2014 from several stations on Gran Sasso Mountain. Existing stations of Androsace mathildae present on the chain of Gran Sasso are: Corno Piccolo (2585 m asl rocks, 7 individuals, 640 m2); Corno Grande (with two stations: at 2780 m asl, 70 individuals, 925 m2 and at 2632 m asl, 100 individuals, 432 m2), Monte Camicia (2490 m asl, 14 individuals, 5 m2) and Monte Prena (2553 m asl, 2 individuals, 5 m2) [24] (Figure 1). We harvested plant parts (leaves, flowers, lateral buds, roots and seeds) in very small quantities, in order to protect individuals and minimize structural damage. The material was identified using Pignatti’s dichotomous analytical keys based on macroscopic and microscopic morphology [21] .

Figure 1. Map showing the chain of Gran Sasso (Italy). The distribution of stations of Androsace mathildae is indicated with black stars.

2.2. Morphological and Cytological Analysis

The morphology of the various parts of A. mathildae has been studied by means of stereomicroscope equipped with a high definition Leica digital camera, optical microscope (OM), and scanning electron microscope (SEM). Plant material used for SEM microscopic examination was fixed in glutaraldehyde (3% in 0.05 M phosphate buffer), dehydrated in a graded acetone series, and dried in a Balzers Critical Point Drier 020. The samples were mounted on aluminum stubs and sputter-coated with gold for 3 min at 15 mA current. Observations were carried out with a Philips XL30/CP Scanning Electron Microscope at 20 kV.

2.3. Vitality Test

Seeds of A. mathildae were subjected to the Triphenyl Tetrazolium Chloride test (TTC test) in order to check their viability. The TTC test is based on the reduction of the tetrazolium salt 2,3,5-triphenyl-tetrazolium chloride (TTC), an organic dye that highlights the respiratory activity. In the presence of a dehydrogenase, TTC turns from colorless to red (formazan) [25] . Data analysis was performed with the software package Microsoft Excel, version 2010.

2.4. Sterilization of Plant Material and Composition of Media Tested

To obtain sterile seedlings for in vitro cultures, seeds were placed in 15 ml Falcon tubes filled with water and a few drops of Tween® 20, and then agitated by vortex(fixed speed 2500 rpm) for 10 minutes. A part of the seeds was subjected to cold-wet stratification treatment to simulate chilling conditions under snowpack typical of high altitude mountain areas, while another part of the seeds was pre-treated with a commercial stimulator of germination containing humic extracts (Germinator®, CIFO) [26] . For stratification treatment, some soil collected from natural stations of A. mathildae was placed in aluminum containers (drilled on the bottom for drainage) and 90 seeds of A. mathildae were dropped over that, then covered with a light dusting of further soil. Next, the containers were wetted with vaporized water, covered with aluminum foil and placed in a refrigerator at 4˚C for 90 days [27] . With regard to the pre-treatment with Germinator®, 60 seeds were left to soak for 24 hours in 15 ml Falcon tubes containing deionized water plus 5 drops of Germinator®. A group of 30 seeds was subjected to both cold-wet stratification (firstly) and pre-treatment e surface sterilized in 0.1% NaOCl for 18 minutes. After a thorough wash, they were placed on Phytatray II vessels (Sigma) containing Murashige and Skoog (MS) basal medium [28] , supplemented with 3% sucrose and 0.7% agar, pH 5.7, and placed in a growth chamber at 22˚C. The seeds were placed to germinate part in the light, with neon Osram L30/41 lamp lighting and a photoperiod of 14 hours, and part in the dark; moreover, several concentrations of 6-benzylaminopurine(BAP) and a- naphthalene acetic acid(NAA) were added in some culture media in order to induce cell differentiation, by germination (see Table 1). Data analysis was performed with the software package Microsoft Excel, version 2010.

2.5. Callus Induction

In order to protect individuals and minimize structural damage, we harvested plants from natural station in very small quantities (Figure 2(a)). The leaves of A. mathildae were both cut into 3 × 3 mm fragments and halved by cutting along the central rib. The gems used for the explants were both apical and lateral buds present in the rosettes of A. mathildae (Figure 2 (b)). The callus induction was evaluated on 150 leaf explants and 50 buds, both harvested from individuals collected in nature, and 200 cotyledons obtained from seeds germinated in vitro [29] (Figure 2(c)). The sterilization was carried out according to the protocol described above, except for using a lower residence time in 0.1% NaOCl because the tissue, both of the leaf and the bud, is much softer than the integument of the seed. The residence time was of some minutes, mostly 10 minutes, paying attention to prevent that the tissues would turn yellow. The explants, after a thorough wash, were transferred in Phytatray II vessels containing MS with different concentrations of 2,4-dichlorophenoxyacetic acid (2,4-D), BAP and NAA, either alone or in combination, as shown in Table 2, and placed in a growth chamber at 22˚C, with neon Osram L30/41 lamp lighting and a photoperiod of 14 hours. The percentage of callus formation, namely the number of callus-forming explants relative to the total number of explants, was calculated after 4 weeks. Data analysis was performed with the software package Microsoft Excel, version 2010. Results are expressed as mean ± standard error.

Figure 2. (a) Androsace mathildae L. plants in a natural station; (b) Androsace mathildae L. specimen harvested from a natural station (in particular, the lateral buds are visible); (c) Androsace mathildae L. seeds sprouted in vitro.

Table 1. Media tested for seed germination and relative results.

2.6. Neomorphogenesis

The samples that demonstrated a better growth condition (with respect to mass, hardness and color) were transferred to new growth medium consisting of MS, BAP, NAA. To improve measurements of callus growth, we performed a visual evaluation [30] . The growth aspects that we have considered consist in the mass, hardness and colour.

After 1 month the frequency of differentiation in sprouts was calculated, expressed as number of calli with buds on the total number of calli × 100. Subsequently, the calli with the shoots were transferred to a fresh culture medium similar to the previous one, and the frequency of differentiation to shoot was calculated, expressed as number of calli with shoot on the total number of calli × 100, calculated after other 30 days. Each treatment was repeated 5 times, and each Phytatray II vessels contained about 13 - 20 calli. Data analysis was performed with the software package Microsoft Excel, version 2010. Results are expressed as mean ± standard error.

3. Results

3.1. Morphology and Microscopic Characteristics

Sample observation at SEM allowed to highlight several interesting morphological traits of Androsace mathildae, such as the calyx tube with five stamens (Figure 3(a)), the magnification of one stamen accreted to the corolla tube (Figure 3(b)) and numerous pollen grains (Figure 3(c)). The pollen grain is oblate-spheroidal, very small (7 - 8 µm × 12 - 14 µm) and tricolpate, with long and narrow colpi, the exine is foveolated (Figure 3(d)). The slightly ovoidal seed capsule, once ripened, opens up in five valves (Figure 3(e)); generally the capsule contains five seeds (about 1.5 mm × 1 mm) with reticulated seed coat (Figure 3(f)). Scanty hairs (about 100 µm long) are

Figure 3. Morphological observations at scanning electron microscopy of Androsace mathildae L.: (a) Calyx tube with five stamens (scale bar = 1 mm); (b) Magnification of stamen accreted to the corolla tube (scale bar = 100 μm); (c) Pollen grains (scale bar = 10 μm); (d) Detail of pollen grain in equatorial view (scale bar = 5 μm); (e) Seed capsule (scale bar = 500 μm); (f) Seed coat detail (scale bar = 500 μm); (g) Leaf margin detail (scale bar = 100 μm); (h) Fungal hyphae on the leaves (scale bar = 100 μm); (i) Detail thereof (scale bar = 20 μm).

found on the leaf apex (Figure 3(g)); this noteworthy feature allows to distinguish A. mathildae from A. komovensis sp. nov., which, conversely, exhibits leaves with a clearly ciliated margin [23] . The leaf analysis at higher magnitude pointed out the presence of fungal hyphae not yet identified (Figure 3(h) and Figure 3(i)); previous studies on Androsace genus reported the presence of actinomycetes named Agromyces albus sp. nov. over the aerial part of the plant [31] .

The stereo and optical microscope analysis led to the identification of the ascomycete Pyrenophora bromi as an agent of leaf decomposition (Figure 4(a) and Figure 4(b)). This is a small genus with thick-walled pseudothecia and bearing dark brown bristles on their upper surface [32] [33] . This ascomycete has never been reported either on A. mathildae, or at these altitudes.

3.2. Seed Vitality and Germinability

TTC test showed that all the seeds, both those harvested in summer 2008 and those harvested years after, were vital. In fact, all of them exhibited a bright red staining, sign of mitochondrial respiration. Therefore, we showed that prolonged preservation does not cause vitality reduction. In vitro seed germinability was calculated 7 weeks after the implantation. The germinability of seeds placed on auxin- and cytokinin-free media was very low (ranging from 0% to 15%) as reported by other authors [34] , while the percentage of sprouted seeds on auxin- and cytokinin-containing media and pre-treated with Germinator® was 91% (Table 1).

3.3. Plant Material Achievement

The best results with regard to germination, assessed 7 weeks after seed implantation (Table 1), were given by auxin- and cytokinin-containing media, with the same percentage for both Germinator® pre-treated and not pre-treated seeds. The main difference lies in the germination time, which was shorter for stimulator-treated seeds. Seeds placed on media without plant growth regulators, or media with only 2,4-D, exhibited a very low germinability and, in addition, the shoots began to get brown just after the germination, becoming unusable after about 2 weeks. In the present study, seed germination and callus formation response was higher in MS supplemented with BAP and NAA. In line with the observation reported in development studies in other genera, both low and high concentrations of 2,4-D failed to stimulate seed germination and protocorm development [35] [36] . Cotyledons used in the following explants were harvested from seeds germinated on media reported in Table 1 with germination over 92%.

3.4. Callus Induction

None of the tested media, containing the various 2,4-D, 2,4-D + BAP and BAP + NAA concentrations specified above, provided positive results for callus induction from leaf explants and apical and lateral buds. On the contrary, positive results were obtained for explants derived from in vitro-generated cotyledons placed in culture media containing 2,4-D + BAP and BAP + NAA (Table 2). The percentage of calli formed in the presence of 2,4-D + BAP is not very high and they did not exhibit a good growth, showing a colour tending to dark brown and often an insubstantial mass. Clearly better results were obtained on medium containing BAP + NAA at var-

(a) (b)

Figure 4. (a) Stereomicroscope analysis showing. Pyrenophora bromi with thick-walled pseudothecia and bearing dark brown bristles on decaying leaves (scale bar = 200 μm); (b) Optical microscope analysis showing details of asci and ascospores (scale bar = 50 μm).

Table 2. Media for callus induction tested on cotyledons obtained from in vitro germinated seeds. The percentage of callus formation, namely the number of callus-forming explants over the total number of explants × 100, was calculated after 4 weeks.

ious concentrations (Table 2), on which the frequency of callus formation is very high, reaching about 93% (Figure 5).

The calli presented a colour in many cases pale or tending to green, solid mass, excellent growth and strong neomorphogenesis capacity. At the time of observation many of the calli were already differentiating, generating the first buds and shoots.

3.5. Neomorphogenesis, Development and Growth of Regenerated Shoots

Transferring on MS medium supplemented with 0.5 mg∙l−1 BAP and 0.25 mg∙l−1 NAA caused an extremely high frequency (100%) in bud and shoot formation (see Table 3).

In particular, the calli that were firm and bright green and had a dimension higher than 5 mm showed higher neomorphogenetic capacity (Figure 6(a)). The number of buds ranged from 1 to 20 per callus, with an average of 7.12, while their dimensions were quite small (about 1 cm) (Figure 6(b)). We observed that calli remaining in the same medium for prolonged periods (>25 days) were subjected to unwanted phenomena, such as tendency to scorch. It is to be noted that the scorching process, even if diffused on the entire culture, did not cause culture death nor the loss of the neomorphogenetic capacity. In fact, transferring the scorched calli on fresh medium allowed the appearance and proliferation of morphogenetic tissue, even several (8 - 12) weeks after the scorch. A. mathildae presented a high growth rate but also a high number of lateral buds, which were used to increase the number of clones present in the growth chamber within a few sub-culture passages (Figure 6(c)), thus limiting the use of plant growth factors. This part of the study was particularly successful, with 100% of growth of the shoots.

4. Discussion

More than half of the vascular plant flora may become endangered by the year 2080 as a result of climatic changes [37] . The Red List evaluations represent the first unfavourable trends in the threat status of plant species [38] , as it is in our study case. As specified in Secretariat of the CBD 2002 [39] , the success of conservation must be based on a solid knowledge to understand the value of plant diversity. Our study aimed at deepening the morphological analysis of the plant. SEM observation of Androsace, performed in our work for the first time, allows us to describe the structural characteristics of a high altitude plant species. The pollen grain is oblate-spheroidal, the exine is foveolated without echine suggesting that pollination might be ambophily by insects and wind. The androceo consists of five stamens, connate with the corolla tube, and as many carpels welded consisted the ovary, which is overcome and unilocular. The tests we carried out with the TTC on the collected seeds indicate that pollination is successful because the seeds are vital showing mitochondrial respiration. The

Figure 5. Percentage of callus induction from cotyledons in media containing BAP + NAA at various concentrations.

Figure 6. (a) Androsace mathildae L. callus with bud primordium; (b) Androsace mathildae L. callus with multiple buds; (c) Androsace mathildae L. specimen obtained in vitro.

Table 3. Media tested for neomorphogenesis induction and relative obtained percentage of buds and shoots formation.

small number of seeds (about 5) and the size of the seeds, relatively large compared to the plants, are in agreement with previous studies which indicated a trend from larger numbers of small seeds at lower altitude to smaller numbers of larger seeds at higher altitude [40] .

The large size of the seed of A. mathildae prevents its long-distance diaspore favoring the fall in the vicinity of the basal rosette. We observed that the germination of seeds in the laboratory was increased by the use of extracts of humic acids. This condition in nature is replicated from the decomposition of the lower leaves of A. mathildae which welcome the seeds fallen from the plant’s floral mature peduncolate capsule [19] . Androsace mathildae can be found in the cracks of limestone at an altitude above 2500 m, with a little substrate, therefore the success of germination is due to the presence of organic material consisting of the same basal rosette decomposition. On the aerial portion of the plant we identified Pyrenophora bromi, never reported at these altitudes, as an agent of leaf decomposition. The results obtained by in vitro treatments show that the highest percentage (91%) of sprouted seeds was obtained on media with NAA (0.25 mg∙l−1) and BAP (0.5 mg∙l−1) pre-treated with a solution containing humic extracts. Callus induction was obtained from cotyledons of in vitro germinated seeds on a medium containing 0.5 mg∙l−1 6-benzylaminopurine and0.25 mg∙l−1 a-naphthalene acetic acid. The frequency of calli formation is about 93%, they presented a colour tending to green, solid mass, excellent growth and strong neomorphogenesis response. Development and growth of shoots was readily achieved using the same medium at various concentrations. Positive results were obtained in culture media containing 0.5 mg∙l−1 BAP and 0.25 mg∙l−1 NAA; we obtained an extremely high frequency (>93%) in callus, buds and shoots formation.

5. Conclusions

The conservation of endemic species is a primary aim in the activities of a botanical garden. Ex situ conservation collections aim at preserving the genetic diversity of target species threatened by climate change and human pressure. Specific conservation action, in order to define an appropriate strategy, includes a thorough knowledge of biological and morphological features of plant species and protocols for in vitro preservation finalized to long term conservation of genetic diversity [41] - [43] . The case study presented herein highlights how conventional strategies of propagation, such as the germination of seeds, do not result efficient without the use of germplasm ex-situ conservation techniques.

In this regard in vitro technologies can be successfully exploited for biodiversity conservation of the Habitats Directive’s plants that show a very low seed germination. On the other hand, in high altitude, agamic reproduction represents a strategy widely used by plants [4] . The studies were conducted despite the scant material available due to the small number of individuals present in nature, namely less than 200 [24] .

We developed a method for in vitro conservation of A. mathildae, which proved to be essential to design further methodologies aimed at ex situ conservation, such as cryopreservation that allows the storage of plant tissues like shoots [44] . The results demonstrated that an effective ex situ preservation strategy of threatened plants is possible through the deepening of the knowledge relating to the single plant studied.

Acknowledgements

The authors wish to thank Dr Lorenzo Arrizza (Centro di Microscopia Elettronica, University of L’Aquila) for skilful help in SEM observations.

Clarification

The proceedings were approved and carried out according to Protocol 207, registered in the Ethics and Animal Use Committee of UENF.

Cite this paper

PaoloFasciani,11,LorettaPace,11, (2015) Conservation of Endangered Species: Androsace mathildae Levier (Primulaceae) in Central Italy. American Journal of Plant Sciences,06,3175-3186. doi: 10.4236/ajps.2015.619309

References

  1. 1. Conti, F., Abbate, G., Alessandrini, A. and Blasi, C. (2005) An Annotated Checklist of the Italian Vascular Flora. Palombi Editori, Rome.

  2. 2. Conti, F., Manzi, A. and Pedrotti, F. (1997) Libro Rosso delle piante d’Italia. Ministero dell’Ambiente WWF Italia Società Botanica Italiana, CIAS, Università Camerino.

  3. 3. Rossi, G., Montagnani, C., Gargano, D., Peruzzi, L., Abeli, T., Ravera, S., Cogoni, A., Fenu, G., Magrini, S., Gennai, M., Foggi, B., Wagensommer, R.P., Venturella, G., Blasi, C., Raimondo, F.M. and Orsenigo, S. (2013) Lista Rossa della Flora Italiana. 1. Policy Species e altre specie minacciate Comitato Italiano IUCN e Ministero dell’Ambiente e della Tutela del Territorio e del Mare. StamperiaRomana.
    http://www.minambiente.it/sites/default/files/archivio/biblioteca/protezione_natura/lista_rossa_flora_italiana_policy_species.pdf

  4. 4. Korner, C. (1999) Alpine Plant Life. Sprinter, Berlin.
    http://dx.doi.org/10.1007/978-3-642-98018-3

  5. 5. Diemer, M.W. (1996) Evidence of Microclimatic Convergence of High Elevation a Seasonal Tropical Paramo and Seasonal Temperate Zone Alpine Environments. Journal of Vegetation Science, 7, 821-830.
    http://dx.doi.org/10.2307/3236460

  6. 6. Larcher, W. (1995) Physiological Plant Ecology. Ecophysiology and Stress Physiology of Functional Groups. Springer, Berlin, Heidelberg, New York.

  7. 7. Billings, W.D. (1979) High Mountain Ecosystems Evolution, Structure, Operation and Maintenance. In: Werrer, P.J., Ed., High Altitude Geoecology, AAAS Select Symp, 12, 97-125.

  8. 8. Thuiller, W. (2007) Biodiversity: Climate Change and the Ecologist. Nature, 448, 550-552.
    http://dx.doi.org/10.1038/448550a

  9. 9. Parolo, G. and Rossi, G. (2007) Upward Migration of Vascular Plants Following a Climate Warming Trend in the Alps. Basic and Applied Ecology.
    http://dx.doi.org/10.1016/j.baae.2007.01.005

  10. 10. Schulman, L. and Lehvavirta, S. (2011) Botanic Gardens in the Age of Climate Change. Biodiversity and Conservation, 20, 217-220.
    http://dx.doi.org/10.1007/s10531-010-9979-6

  11. 11. Heywood Vernon, H. (2011) The Role of Botanic Gardens as Resource and Introduction Centres in the Face of Global Change. Biodiversity and Conservation, 20, 221-239.
    http://dx.doi.org/10.1007/s10531-010-9781-5

  12. 12. Piovan, A. and Cassina, G. (2011) Crambe tataria: Actions for ex Situ Conservation. Biodiversity and Conservation, 20, 359-371.
    http://dx.doi.org/10.1007/s10531-010-9949-z

  13. 13. Smith, G.F. and Lowe, D.P. (1977) Androsaces. J.A. Kelly, F.L.S. Hart-Talbot Printers Ltd.

  14. 14. Levier, E. (1877) Androsaces mathildae, Species Italica Nova ab E. Levier Descripta. Nuovo Giornale Botanico Italiano, 10, 43-45.

  15. 15. Mabberley, D.J. (2008) Mabberley’s Plant-Book: A Portable Dictionary of Plants, Their Classifications, and Uses. Cambridge University Press, Cambridge.

  16. 16. Wu, L., Yang, K., Tao, S., Yang, W. and Jiang, C. (2012) Establishment of Regeneration Clone from Hypocotyl of Androsace filiformia. Journal of Shanxi Agricultural Sciences, 11.

  17. 17. Schneeweiss, G.M., Schönswetter, P., Kelso, S. and Niklfeld, H. (2004) Complex Biogeographic Patterns in Androsace (Primulaceae) and Related Genera: Evidence from Phylogenetic Analyses of Nuclear ITS and Plastid trnL-F Sequences. Systematic Biology, 53, 856-876.
    http://dx.doi.org/10.1080/10635150490522566

  18. 18. Blasi, C., Di Pietro, R., Fortini, P. and Catonica, C. (2003) The Main Plant Community Types of the Alpine Belt of the Appennine Chain. Plant Biosystems, 137, 83-110.
    http://dx.doi.org/10.1080/11263500312331351361

  19. 19. Tammaro, F. (1998) Il paesaggio vegetale dell’Abruzzo. Cogecstre Edizioni, Penne, 397-400.

  20. 20. Anchisi, E., Bernini, A., Cartasegna, N. and Polani, F. (1991) Androsace d’Europa. La Tipotecnica, San Vittore Olona (Mi).

  21. 21. Pignatti, S. (1982) Flora d’Italia. Volume II, Edagricole, Bologna.

  22. 22. Wraber, T. (1983) Androsace mathildae neufür die Balkanhalbinsel. Contributions, Macedonian Academy of Sciences and Arts, Section of Biological and Medical Sciences, 4, 41.

  23. 23. Schönswetter, P. and Schneeweiss, G.M. (2009) Androsace komovensis sp. nov., a Long Mistaken Local Endemic from the Southern Balkan Peninsula with Biogeographic Links to the Eastern Alps. Taxon, 58, 544-549.
    http://www.uibk.ac.at/botany/staff/publikationen/schoenswetter_peter/28.pdf

  24. 24. Bartolucci, F., Stinca, A., Tinti, D. and Conti, F. (2014) I beni ambientali individui del Parco nazionale del Gran Sasso e Monti della Laga.
    http://www.gransassolagapark.it/Pdf/progetti/PNGSLprogetti95-1.pdf

  25. 25. Moore, R.P. (1976) Tetrazolium Seed Testing Developments in North America. Seed Technology Journal, 1, 17-30.

  26. 26. Ayuso, M., Hernandez, T. and Garcia, C. (1996) Effect of Humic Fractions from Urban Wastes and Other More Evolved Organic Materials on Seed Germination. Journal of the Science of Food and Agriculture, 72, 461-468.
    http://onlinelibrary.wiley.com/doi/10.1002/%28SICI%291097-0010%28199612%2972:4%3C461::AID-JSFA680%3E3.0.CO;2-%23/epdf

  27. 27. Giménez-Benavides, L. and Milla, R. (2013) Comparative Germination Ecology of Two Altitudinal Vicariant Saxifraga Species Endemic to the North of Spain. Plant Biology, 15, 593-600.
    http://dx.doi.org/10.1111/j.1438-8677.2012.00663.x

  28. 28. Murashige, T. and Skoog, F. (1962) A Revised Medium for Rapid Growth and Biassays with Tobacco Tissue Cultures. Physiologia Plantarum, 15, 473-497.

  29. 29. Hartmann, H.T. and Kester, D.E. (1990) Propagazione delle piante. Basi scientifiche e applicazioni tecniche. Edizioni Agricole, Bologna, 555-582.

  30. 30. Remotti, P.C. and Löffler, H.J.M. (1995) Callus Induction and Plant Regeneration from Gladiolus. Plant Cell, Tissue and Organ Culture, 42, 171-178.

  31. 31. Dorofeeva, L.V., Krausova, V.I., Evtushenko, L.I. and Tiedje, J.M. (2003) Agromyce salbus sp. nov., Isolated from a Plant. International Journal of Systematic & Evolutionary Microbiology, 53, 1435-1438.
    http://dx.doi.org/10.1099/ijs.0.02428-0

  32. 32. Hanlin, R.T. (1990) Illustrated Genera of Ascomycetes. APS Press, St Paul.

  33. 33. Dennis, R.W.G. (1998) British Ascomycetes. Cramer, Vaduz, 460-461.

  34. 34. Frattaroli, A.R., Di Martino, L., Di Cecco, V., Catoni, R., Varone, L., Di Santo, M. and Gratani, L. (2013) Seed Germination Capability of Four Endemic Species in the Central Apennines (Italy): Relationships with Seed Size. Lazaroa, 34, 43-53.
    http://dx.doi.org/10.5209/rev_LAZA.2013.v34.n1.42253

  35. 35. Sathiyadash, K., Muthukumar, T., Murugan, S.B., Sathishkumar, R., Uma, E., Jaison, S. and Priyadharsini, P. (2013) In Vitro Asymbiotic Seed Germination, Mycorrhization and Seedling Development of Acampae praemorsa (Roxb.) Blatt. & McCann, a Common South Indian Orchid. Asian Pacific Journal of Reproduction, 2, 114-118.
    http://dx.doi.org/10.1016/S2305-0500(13)60130-X

  36. 36. Hsueh, Y.L. and Lou, C.H. (1947) Effects of 2,4-D on Seed Germination and Respiration. Science, 105, 283-285.
    http://dx.doi.org/10.1126/science.105.2724.283

  37. 37. Thuiller, W., Lavorel, S., Arau′jo, M.B., et al. (2005) Climate Change Threats to Plant Diversity in Europe. Proceedings of the National Academy of Sciences of the United States of America, 102, 8245-8250.
    http://dx.doi.org/10.1073/pnas.0409902102

  38. 38. Rassi, P., Hyvärinen, E., Juslén, A. and Mannerkoski, I., Eds. (2010) The 2010 Red List of Finnish Species. Ympäristöministeriö & Suomenympäristökeskus, Helsinki.
    www.environment.fi/redlist

  39. 39. Secretariat of the CBD (2002) Global Strategy for Plant Conservation. Secretariat of the Convention on Biological Diversity, Montreal.
    https://www.cbd.int/doc/publications/plant-conservation-report-en.pdf

  40. 40. Sawada, S., Nakajima, Y., Tsukuda, M., Sasaki, K., Hazama, Y., Futatsuya, M. and Watanabe, A. (1994) Ecotypic Differentiation of Dry Matter Production Processes in Relation to Survivorship and Reproductive Potential in Plantago asiatica Populations along Climatic Gradients. Functional Ecology, 8, 400-409.
    http://dx.doi.org/10.2307/2389834

  41. 41. Fasciani, P., Pirone, G. and Pace, L. (2012) Plant Biodiversity at High Altitude: In Vitro Preservation. Acta Horticulturae, 961, 159-165.
    10.17660/ActaHortic.2012.961.18

  42. 42. Pace, L., Angelosante Bruno, A. and Spano, L. (2009) In Vitro Plant Regeneration and Clonal Micropropagation of Leontopodium nivale (Ten.) Heut ex Hand.-Mazz. (Asteraceae). Plant Biosystems, 143, S12-S16.
    http://dx.doi.org/10.1080/11263500903216214

  43. 43. Pace, L., Pacioni, G. and Spano, L. (2004) In Vitro Propagation of Artemisia petrosa Subsp. eriantha: Potential for the Preservation of an Endangered Species. Plant Biosystems, 138, 291-294.
    http://dx.doi.org/10.1080/11263500400008874

  44. 44. Wang, Q.C., Panis, B., Engelmann, F., Lambardi, M. and Valkonen, J.P.T. (2009) Cryotherapy of Shoot Tips: A Technique for Pathogen Eradication to Produce Healthy Planting Materials and Prepare Healthy Plant Genetic Resources for Cryopreservation. Annals of Applied Biology, 154, 351-363.
    http://dx.doi.org/10.1111/j.1744-7348.2008.00308.x

NOTES

*Corresponding author.