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Revegetation following experimental disturbance in a boreal old‐growth Picea abies forest
Author(s) -
Rydgren Knut,
Hestmark Geir,
Økland Rune H.
Publication year - 1998
Publication title -
journal of vegetation science
Language(s) - English
Resource type - Journals
SCImago Journal Rank - 1.1
H-Index - 115
eISSN - 1654-1103
pISSN - 1100-9233
DOI - 10.2307/3237042
Subject(s) - revegetation , propagule , microsite , picea abies , disturbance (geology) , biology , seed dispersal , vegetation (pathology) , ecological succession , plant community , ecology , botany , biological dispersal , seedling , medicine , paleontology , population , demography , pathology , sociology
Abstract. We studied revegetation patterns after experimental fine‐scale disturbance (e.g. uprooting) in an old‐growth Picea abies forest in southeastern Norway. An experimental severity gradient was established by manipulation of the depth of soil disturbance; two types of disturbed areas were used. Species recovery was recorded in the disturbed patches in three successive years after disturbance. The cover of vascular plants and, even more so the cover of bryophytes and lichens, recovered slowly after disturbance. The least severe treatments (removal of vegetation and removal of vegetation and the litter layer) was followed by the fastest recovery. The mean number of vascular plant species was usually higher three years after disturbance than before disturbance, while the opposite was true for bryophytes. Several vascular plant species that were abundant in intact forest floor vegetation ( Vaccinium myrtillus, V. vitis‐idaea and Deschampsia flexuosa ) recovered during a three‐year period primarily by resprouting from intact rhizomes and clonal in‐growth. Other important recovery mechanisms included germination from a soil‐buried propagule bank (e.g. Luzula pilosa, Plagiothecium laetum agg., Pohlia nutans and Polytrichum spp.) and dispersal of propagules into the disturbed patches (e.g. Betula pubescens and Picea abies ). Microsite limitation seemed to occur in several species that were abundant in the soil propagule bank (e.g. the ferns Athyrium filix‐femina, Gymnocarpium dryopteris and Phegopteris connectilis ) but which did not appear in disturbed patches. Disturbance severity influenced revegetation patterns, recorded both as trajectories of vegetation composition in a DCA ordination space and as change in floristic dissimilarity. The length of the successional path (compositional change measured in β‐diversity units) increased with increasing disturbance severity, and was also influenced by the area of the disturbed patch and the distance to intact vegetation. The rate of succession depended on the method by which it was measured; decreasing year by year in floristic space, while first decreasing and then increasing in ordination space. The reason for this difference is explained.