Tento díl je zaměřen především na obnovu ekosystémů na výsypkách po těžbě uhlí, v lomech, vytěžených štěrkopískovnách a rašeliništích. Pokud není zničena nějaká cenná lokalita, maloplošná těžba může často být obohacením krajiny. I v případě větších těžeben a navazujících výsypek a odvalů nemusí být za určitých okolností jejich existence negativní. Mohou se stát útočišti pro mnoho druhů rostlin i živočichů, které z běžné, intenzivně využívané krajiny mizejí. Podmínkou ovšem je, že těžbou narušená místa nejsou technicky rekultivována, nýbrž jsou ponechána spontánní, případně mírně řízené (usměrňované) nebo uměle blokované sukcesi. and The article deals mainly with the restoration of ecosystems situated in spoil heaps from coal mining, in quarries, disused gravel-sand pits and extracted peatland. A small-scale excavation can enrich the landscape if it does not cause damage to a rare locality. Even greater excavations and dumps do not necessarily have a negative effect on the environment. Such localities can be used for conservation of numerous plant and animal species disappearing from the surrounding intensively utilized landscape. Nevertheless, such localities need to be left to spontaneous succession or managed only to a small degree, without technical reclamation.
This study was conducted at 17 peatlands in the Czech Republic mined either by the traditional block-cut method or industrially. Phytosociological reléves of 5 × 5 m were carried out in representative parts of successional stages in disturbed peatlands. Age and environmental characteristics were assessed for each relevé (position of water table, water pH, substratum chemistry, geographical area) or each locality (altitude, average annual temperature and precipitation). Phytosociological reléves recorded in natural vegetation, representing the respective target stages, were included into some analyses. Altogether, 210 relevés were analysed by the DCA ordination. Separately, relevés from milled and block-cut sites were elaborated by CCA with marginal and partial effects calculated. Despite the great variability in vegetation, especially among industrially harvested sites, there is a general tendency for peatland vegetation to recover spontaneously, especially at traditionally harvested sites, which all were, however, older than 50 years. The vegetation at the younger industrially harvested sites exhibited only a tendency to recover. All environmental variables investigated had at least some significant effect on the vegetation pattern, among them, soil pH, water table, nitrates, successional age and geographical location were most important. Abiotic site factors together and geographical location appeared to be more important in determining species composition than successional age.