Abstract

Successions in old fields were studied on the example of the Starobilski steppes within Luhansk Oblast (Ukraine), region located in the basin of the left tributaries of the Siversky Donets, in the southern spurs of the Central Russian Upland. Stationary surveys were conducted in the Striltsivsky Steppe affiliate of the Luhansk Nature Reserve, with 269 ha of old fields (26% of the area) in its territory. Geobotanical releves were performed in 26 plots of abandoned fields, constant monitoring surveys were carried out in 15–27 year-old abandoned fields in the territory of the Reserve and 5–15 year-old abandoned fields in the territory of its buffer zone. In total, the itinerary and detailed surveys were conducted for about 50 plots of abandoned fields. The restoration of the steppe communities was seen only in the plots where grazing and/or mowing took place, which prevented the formation of dense litter and distribution of woody species. The long domination of rhizome grasses (Elytrigia repens) were characteristic in conditions of moderate-level disturbance (in the reserve), transition to the domination of bunchgrasses (Festuca valesiaca) was seen at the age of around 25 years, during the transitional period (20–25 years) communities with unstable structure formed, comprising E. repens, F. valesiaca and forbs (Achillea pannonica and Fragaria viridis). Duration of the stage of segetal and ruderal species in the sites under low effect was 10 years, the communities of unstable structure formed at the age of 5–10 years. In the conditions of stable moderate and high effect of grazing (high disturbance), we observed formation of bunchgrass communities at the age of 15 years. In the unused plots, we saw formation of phytocoenoses of shrubs at different stages of succession, starting from 10 years. The most abundant group of such kind comprised thickets of Ulmus pumila (with E. repens and Poa angustifolia in the herbaceous layer) and Prunus stepposa. The peculiarity of contemporary processes in the abandoned fields related to exacerbation of the vegetation’s anthropogenic transformation is distribution of alien tree species from plantations, the most aggressive of which are Ulmus pumila, Fraxinus lanceolata, Acer negundo, Elaeagnus angustifolia. The peculiarity of the succession processes in the region of studies was the domination of species of broad ecological spectrum, characteristic for abandoned fields of northern forest-steppe regions (Bromopsis inermis, Calamagrostis epigeios, Poa angustifolia, Fragaria viridis) and southern steppe regions (Bromus sguarrosus, Anisantha tectorum, Achillea pannonica, Artemisia austriaca), certain communities form dependent on the climatic conditions and type of land use in the period of succession in particular plots.

Highlights

  • One of the key issues in studies of abandoned field in the steppe zone is whether restoration of rare steppe biocenoses is possible in general, and to what extent the rare communities and species are capable of recovering in former arable lands

  • The participation of some steppe species of broad amplitude regarding the factor of synantropization rapidly increases (10–15 years), such species were abundant on grazing sites, grew in different anthropogenic biotopes and were distinctive for steppe phytocenoses

  • The peculiarity of succession in abandoned fields in the Starobilski steppes is the formation of communities of a very broad ecological spectrum, typical for abandoned fields both in northern forest steppe regions

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Summary

Introduction

One of the key issues in studies of abandoned field in the steppe zone is whether restoration of rare steppe biocenoses is possible in general, and to what extent the rare communities and species are capable of recovering in former arable lands. Restoration of vegetation in abandoned fields starts from initial communities and develops towards the natural vegetation (Suyundukov et al., 2008; Sojnekova & Chytry, 2015; Olijnyk & Parpan, 2017). A large amount of studies have emerged concerning various methods of ecological restoration of natural communities, consisting of using the methods of enhancing the succession due to introduction of seeds (or vegetative parts) of species of late stage for inhibition of the weedy stage development and creation of secondary communities (Vander Putten et al, 2000; Török et al, 2010; Albert et al, 2019)

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