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Migration of herb layer species into the poorest post-agricultural pine woods adjacent to ancient pine forests

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Warianty tytułu
Języki publikacji
EN
Abstrakty
EN
The recovery of species composition typical for ancient forests in recent woods is a very slow process and may last for decades or even centuries. It is enhanced only when postagricultural woods are adjacent to ancient ones. However, even in such a situation of the spatial contact of both forest types, colonization of recent woods by true forest species is a gradual process. According to studies focusing on the behaviour of individual species and their colonization rates into recent woods, it can be concluded that in more fertile habitats the migration process proceeds faster than on poorer sites. Thus, studies were conducted on light, acidic soils both in ancient and in adjoining post-agricultural pine woods (the Dicrano-Pinion Libb. 1933 alliance) and were focused on the process of the colonization of the herbaceous layer by woodland flora in recent woods. In eight transects 80 m in length perpendicular to the ancient/recent ecotone and consisting of 10 sample plots of 16 m2 laid out at intervals of 4 m, the percentage cover of herb layer species was recorded. The migration rates (based on the occurrence of the farthest individual and on the occurrence of the maximum cover of a species) for 12 forest species were calculated. The mean migration rate for all species reached 0.54 m yr[^-1] when based on maximum cover and 0.67 m yr[^-1] when based on the farthest individual and appeared to be lower than those reported in investigations in more fertile and moister habitats. The migration rates for individual species ranged from 0 to 1.21 m yr[^-1] and were also lower than in more fertile, black alder woodlands. The migration pattern of Vaccinium myrtillus L., the most abundant species in pine woods, fits the model based on the establishment of isolated individuals. The cover of most woodland species increased with the increasing age of a recent wood. Herb layer recovery on such sites is slower than in the more productive, fertile habitats of broadleaved forests. The ancient and recent pine woods investigated here differed in herb layer species composition despite the secondary succession having lasted for over 50-60 years.
Rocznik
Strony
75--85
Opis fizyczny
Bibliogr. 31 poz.,Rys., tab.,
Twórcy
autor
autor
  • University of Silesia, Faculty of Biology and Environmental Protection, Department of Ecology, Bankowa 9, 40-007 Katowice, anna.orczewska@us.edu.pl
Bibliografia
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  • 5. De Frenne P., Baeten L., Graae B. J., Brunet J., Wulf M., Orczewska A., Kolb A., Jansen I., Jamoneau A., Jacquemyn H., Hermy M., Diekmann M., De Schrijver A., De Sanctis M., Decocq G., Cousins S. A. O., Verheyen K. 2011 – Interregional variation in the floristic recovery of post-agricultural forests – J. Ecol. 99: 600–609.
  • 6. Dzwonko Z. 1993 – Relations between the floristic composition of isolated young woods and their proximity to ancient woodland – J. Veg. Sci. 4: 693–698.
  • 7. Dzwonko Z. 2001a – Effect of proximity of ancient deciduous woodland on restoration of the field layer vegetation in a pine plantation - Ecography, 24: 198–204.
  • 8. Dzwonko Z. 2001b – Migration of vascular plant species to a recent wood adjoining ancient woodland – Acta Soc. Bot. Pol. 70: 71–77.
  • 9. Dzwonko Z., Gawroński S. 1994 – The role of woodland fragments, soil types and dominantspecies in secondary succession on the western Carpathian foothills – Vegetatio, 111: 149–160.
  • 10. Dzwonko Z., Loster S. 1992 – Species richness and seed dispersal to secondary woods in southern Poland – J. Biogeogr. 19: 195–204.
  • 11. Dzwonko Z., Loster S. 2001 – Wskaźnikowe gatunki roślin starych lasów i ich znaczenie dla ochrony przyrody i kartografii roślinności [Ancient woodland plant species indicators and their importance for nature conservation and vegetation mapping] – Prace Geograficzne, 178: 119–132. (in Polish).
  • 12. Faliński J.B. 1986 – Vegetation dynamics in temperate lowland primeval forests – Geobotany, 8: 1–537.
  • 13. F l i n n , K . M . , Ve l l e n d M . 2005 – Recovery of forest plant communities in post-agricultural landscapes – Front. Ecol. Environ. 3: 243–250.
  • 14. Hermy M., Honnay O., Firbank L., Grashof-Bokdam C., Lawesson J. 1999 - An ecological comparison between ancient and other forest plant species of Europe, and the implications for forest conservation – Biol. Conserv. 91: 9–22.
  • 15. Hermy M., Verheyen K. 2007 – Legacies of the past in the present-day forest biodiversity: a review of past land-use effects on forest plant species composition and diversity – Ecol. Res. 22: 361–371
  • 16. Honnay, O., Bossuyt, B. 2005 – Prolonged clonal growth: escape route or route to extinction? – Oikos, 108: 427–432.
  • 17. Honnay, O., Degroote, B., and Hermy, M. 1998 – Ancient-forest plant species in western Belgium: a species list and possible ecological mechanisms – Belg. J. Bot. 130: 139–154.
  • 18. Honnay O., Hérault B., Bossuyt B. 2009 - Opportunities and constraints of using understorey plants to set forest restoration and conservation priorities. (In: Setting conservation targets for managed forest landscapes, Eds: M.A. Villard, B.G. Jonsson) – Cambridge University Press, pp. 227–243.
  • 19. Honnay O., Jacquemyn H., Roldán-RuizI., Hermy M. 2006 – Consequences of prolonged clonal growth on local and regional genetic structure and fruiting success of the forest perennial Maianthemum bifolium – Oikos, 112: 21–30.
  • 20. Matlack G.R. 1994 – Plant species migration in a mixed-history forest landscape in eastern North America – Ecology, 75: 1491–1502.
  • 21. Orczewska A. 2009 – Migration of herbaceous woodland flora into post-agricultural black alder woods planted on wet and fertile habitats in south western Poland – Plant Ecol. 204: 83–96.
  • 22. Orczewska A. 2010 – Colonization capacity of herb woodland species in fertile, recent alder woods adjacent to ancient forest sites – Pol. J. Ecol. 58: 297–310.
  • 23. Peterken G.F. 1977 – Habitat conservation priorities in British and European woodlands – Biol. Conserv. 11: 223–236.
  • 24. Peterken G.F., Game M. 1984 – Historical factors affecting the number and distribution of vascular plant species in the woodlands of Central Lincolnshire – J. Ecol. 72: 155–182.
  • 25. Singleton R., Gardescu S., Marks P. L., Geber M. 2001 – Forest herb colonization of postagricultural forests in central New York State, USA – J. Ecol. 89: 325–338.
  • 26. Sobczak R. 1996 – O powracaniu lasów na grunty porolne w Polsce [On restoration of the forest on former agricultural waste land in Poland] – Sylwan, 5: 35–39. (in Polish).
  • 27. Tuszyński M. 1990 – Właściwości gleb porolnych a gospodarka leśna [Properties of postagricultural soils and forest economy] – Sylwan, 3: 41–51. (in Polish).
  • 28. Van der Pijl L. 1982 – Principles of dispersal in higher plants – Springer, Berlin.
  • 29. Verheyen K., Honnay O., Motzkin G., Hermy M., Foster D. R. 2003 – Response of forest plant species to land-use change: a life-history trait-based approach – J. Ecol. 91: 563–577.
  • 30. World Reference Base for Soil Resources 1998 – FAO, ISSS, ISRIC, Rome.
  • 31. Wulf, M., Heinken T. 2008 – Colonization of recent coniferous versus deciduous forest stands by vascular plants at the local scale – App. Veg. Sci. 11: 307–316.
Typ dokumentu
Bibliografia
Identyfikator YADDA
bwmeta1.element.baztech-article-BGPK-3205-2400
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