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Auf der alten sowjetischen Deponie in der Lieberoser Heide wurde im Juni 2009 ein Dachskadaver ausgelegt. Nach der vollständigen Skelettierung im August desselben Jahres erfolgte eine erste Erfassung ausgewählter Bodenparameter. Die Zweitbeprobung fand im Juni 2010 statt, wobei hier außerdem eine Aufnahme von Collembolen, Milben und der Vegetation erfolgte. Das Probenahmedesign bestand aus einem Probenpunkt im Zentrum sowie 4 nach Norden, Osten, Süden bzw. Westen ausgerichteten Teiltransekten mit jeweils 14 aufeinanderfolgenden Probenpunkten und einer in 1 m Abstand folgenden Außenprobe. Bei den Bodenparametern wurden pH-Wert, Wassergehalt, organische Substanz, Nitratstickstoff, Ammoniumstickstoff, Diphosphorpentoxid und Leitfähigkeit analysiert. Die Extraktion der Fauna orientierte sich an dem Prinzip von Macfayden. Die Proben enthielten 7.606 Collembolen aus 14 Arten. Es handelte sich überwiegend um Exemplare von Hypogastrura vernalis. Die Milben, 7.197 Tiere, wurden nur quantitativ erfasst. Anhand verschiedener statistischer Tests (SPSS, Canoco) wurde ermittelt, welche Bodenparameter signifikante Unterschiede zur Umgebung aufweisen. Sowohl pH-Wert als auch Humusgehalt zeigten weder bei der 1. noch bei der 2. Beprobung Abweichungen an. Bei Leitfähigkeit und Wassergehalt waren die Werte 2009 in der Nähe des Zentrums erhöht, 1 Jahr später jedoch nicht mehr. Erhöhte Ammoniumstickstoffwerte waren nur 2009 nachweisbar. Beim Nitratstickstoff konnten 2009 höhere Gehalte auf der ehemaligen Liegefläche des Kadavers gemessen werden, die jedoch 2010 deutlich geringer ausfielen. Diphosphorpentoxid zeigte eine ähnliche Entwicklung, wobei die Differenzen zwischen beiden Jahren merklich geringer waren.
30 sampling sites at 5 mining areas and reference sites in Lower Lusatia were studied for succession of Collembola. The study took place from 2001 to 2004. Two chronosequences were chosen, one for afforestation sites and one for sites with free succession. Additional data about some soil parameters (pH, organic matter content, water content, water capacity, conductivity, phosphate, ammonium and nitrate) are also given. Most soil parameters increase with age and/or vegetation development. Only pH decreases after melioration whereas no correlations were found for phosphate. At all study sites, 13.733 specimens, distributed across 84 species were identified with Mesaphorura macrochaeta and Parisotoma notabilis as most abundant species. Succession was studied on different levels. On the level of species and ecological groups, succession is from meadow species to forest species, but on the level of specimens and ecological groups, succession is from meadow species over eurotopic species to forest species. A model for species succession is offered on the level of specimens, presented separately for the epigaeic and the endogaeic community. Both successional developments could be divided into five parts: For the epigaeic community, the 1st stage is defined as sites without vegetation. Species found here are Pseudoanurophorus alticolus, Schoetella ununguiculata, Bourletiella pruinosa and Brachystomella parvula. At the 2nd stage, already some sparse vegetation can be found. Some sites are also covered densely by moss. Here, Cryptopygus thermophilus, Isotoma anglicana and Lepidocyrtus cyaneus are found fort he first time. The 3rd stage is defined as sites with dense vegetation, generally Calamagrostis epigejos dominated sites. Oldest sites have already some shrubs made of young pines or are clearings in young woodland. Several species are found here for the first time in notable dominances: Entomobrya lanuginosa, Entomobrya multifasciata, Lepidocyrtus lignorum, Isotoma viridis, Lepidocyrtus lanuginosus, Sminthurinus aureus, Sphaeridia pumilis and Tomocerus flavescens. The fourth stage is made up by afforestations up to 43 years on reclamation sites. 5 more species are found here: Entomobrya nivalis, Neanura muscorum, Orchesella flavescens, Paratullbergia macdougalli and Tomocerus vulgaris. The 5th stage would be the climax stage, an old oak forest. It is probably not comparable to a true primeval forest, but the type of forest typical for today’s mining sites. Only 2 species were found here: Micraphorura absoloni and Entomobrya corticalis. For the endogaeic community, data is even more based on statistical evidence. Succession of the endogaeic community is more dependent on soil parameters and succession of microflora. Generally, succession is from Mesaphorura atlantica on acidic sites and Proisotoma minuta on sites with higher pH to a Mesaphorura macrochaeta community, followed by a Parisotoma notabilis dominated community. Older afforested sites are dominated by Isotomiella minor and old oak forest on undisturbed sites by Folsomia penicula. Duration of the single successional stages depends on parameters like pH, moisture, vegetational structure and availability of certain fungi as basic food resource.