Abstract

The selection and comparative study of new forms of the Red Book species checker tree mountain ash (Torminalis glaberrima (Gand.) Sennikov & Kurtto) were conducted on the basis of generalizing the literary data and expeditionary research on the natural and local gene pool of the above-mentioned plant. Information was presented about the peculiarities of the selection and valuable forms of the checker tree concerning the indices of vitality and morphology in the Central, South-Western, and Western Forest-Steppe of Ukraine. These forms appeared to be characterized by high vigour (over 30–40 cm), large size and mass of the fruits (1.7–2.4 g), their increased nutritional value, high ecological plasticity and ornamentality (crown shape, leaf colouration and shades during the growing season). Taking into consideration the ornamental characteristics, the selected forms are rather promising in landscape construction and phytodesign as complementary elements of oak-beech, oak-hornbeam and other species associations, as well as green corridors of the ecological network. This will contribute to the restoration and preservation of this rare species, thus facilitating restoration, spreading and conservation of this rare species, thereby increasing the stability of ecosystem components, squares, alleys, nature-conservation territories and enhancing the aesthetic qualities of the gardens when establishing harmonious landscape compositions. The fruits of T. glaberrima are characterized as raw material for processing and manufacturing of medicinal preparations and food products. The biochemical analysis of the checker tree mountain ash berries has shown that they are characterized by high content of a number of biologically active substances: polyphenolic compounds, flavonoids, vitamin С. The wide use of the checker tree will enable the food and pharmaceutical markets to be supplied with medicinal and fruit raw material by its introduction into new cultivation conditions, namely: into industrial and ornamental horticulture, forestry. The new genotypes of T. glaberrima were selected and are planned to be transferred to the National Centre for the Plant Genetic Resources of Ukraine. That will make it possible to replenish the genetic bank of Ukraine with representatives of the species, which are promising in fruit growing and ornamental horticulture, forestry and nature conservation.

Highlights

  • In 1992 the UN conference took place in Rio de Janeiro dedicated to environmental problems

  • According to the results of the research in 2017–2020, the beginning of vegetation of the T. glaberrima model plants in the conditions of the Northern ForestSteppe falls in the third decade of March

  • This position is enshrined in many international documents, primarily in the Global Strategy for Plant Conservation and the European Strategy for Plant Conservation 2011–2020 (Hoebee et al, 2006). They clearly define the tasks of plant conservation ex situ 2020 in research institutions, protected areas, in ecosystem restoration programs (Paul et al, 2000; Zwierzyński & Bednorz, 2012). Both in Ukraine and abroad the main reason for population decline of T. glaberrima is the thoughtless exploitation of its natural specimens (Thomas, 2017), which led by the end of the XIX century and in the early XX century to the catastrophic reduction of its population to barely1% of the total area of mixed forests (Demesure-Musch & Oddou-Muratorio, 2004; Grynyk et al, 2019; Lefèvre et al, 2020)

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Summary

Introduction

In 1992 the UN conference took place in Rio de Janeiro dedicated to environmental problems. Change in the natural conditions and anthropogenic activity have caused a decrease in range, and alterations in the functional organization of many plant species (de Rigo et al, 2016; Bednorz & Nowinska, 2018). Most threatened plants are rare, endemic or edge of range (Krynytskyi et al, 2017). They are represented mostly by isolated populations, which differ in genetic and ecological structure, tied to certain habitat types that are separated from each other by geographic or biological barriers (de Rigo, et al, 2016; Hallmann et al, 2017)

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