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Ocena stopnia inwazji Impatiens glandulifera w różnych typach siedlisk w rejonie Pogórza Śląskiego i Beskidu Małego

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Warianty tytułu
EN
Assessment of the invasion degree of Impatiens glandulifera in different types of habitats in the Silesian Foothills and Little Beskids
Języki publikacji
PL
Abstrakty
EN
Himalayan balsam Impatiens glandulifera Royle, native to Central Asia and the Himalayan region, is one of the most invasive alien species in Europe. It is listed as a species considered a threat to the European Union and is also classified as a highly invasive species in Poland. Cultivation is prohibited without a permit from the General Director for Environmental Protection. Impatiens glandulifera is more common in southern Poland, especially in river valleys, but can also be found in other habitat types. This study examined the occurrence of this species in several selected localities: Cieszyn, Szczyrk, Rzyki, Rychwałd, Ustroń, Wisła, and Żywiec, belonging to the Silesian Foothills, Silesian Beskids, Żywiec Beskids, and Little Beskids mesoregions. In total 313 sites of this species were identified, with the largest number localities in Żywiec, with 120 populations. Considering habitat preferences of the species, approximately 16% of the populations were located in forests under canopy of trees. Over 36% were sites located directly in riparian habitats (banks of streams, rivers, ponds). More than 42% were populations were in ruderal habitats connected to communication routes: roads, roadsides, and railway embankments. Only ca. 5% sites were located on meadows and grasslands. Contrary to our expectations, slightly almost 3% of the sites were large-scale populations exceeding 500 m2, while the most common population size was between 10-50 individuals (27%). The most common size of occupied area was between 10-20 m2 (30%). More than 52% of all sites were populations with individuals varied 1 and 1.5 m in height. The fewest, i.e. 6.2%, were sites where I. glandulifera reached a height of shoots exceeding 1.5 m. The height of individuals of I. glandulifera was positively correlated with abundance and size of area occupied by populations. The study results show differences between localities in both the total number of sites, their area, population size, and their share among various habitat types. Thus, it can be concluded that the degree of invasion of the studied species varies depending on the location and an increase in the number of sites can be expected in the future.
Rocznik
Strony
50--58
Opis fizyczny
Bibliogr. 19 poz., rys., tab., wykr.
Twórcy
  • University of Bielsko-Biala, Institute of Engineering Sciences, Willowa 2, 43-309 Bielsko-Biała, Poland
  • University of Bielsko-Biala
  • University of Bielsko-Biala
  • University of Bielsko-Biala
  • University of Bielsko-Biala
  • University of Bielsko-Biala
  • University of Bielsko-Biala
  • University of Bielsko-Biala
  • University of Silesia, Institute of Earth Sciences, Będzińska 60, 41-200 Sosnowiec, Poland
Bibliografia
  • 1. Adamowski W., Krzysztofiak A., Dajdok Z. 2018. Impatiens glandulifera Royle – Karta informacyjna gatunku. Generalna Dyrekcja Ochrony Środowiska: http://www.gov.pl/gdos/inwazyjne-gatunki-obce-ias, dostęp: 2025-11-25.
  • 2. Beerling D.J., Perrins J.M. 1993. Impatiens glandulifera royle (impatiens Roylei Walp.). Journal of Ecology, 81(2), 367–382.
  • 3. Child L., de Waal L. 1997. The use of GIS in the management of Fallopia japonica in the urban environ-ment. [W:]: Plant invasions: studies from North America and Europe (red. J.H. Brock, M. Wade, P. Pyšek, D.F. Greene). Backhuys Publishers, Leiden, The Netherlands, 207–220.
  • 4. Clements D.R., Feenstra K.R., Jones K., Staniforth R. 2008. The biology of invasive alien plants in Canada. 9. Impatiens glandulifera Royle. Canadian Journal of Plant Science, 88(2), 403–417.
  • 5. Coakley S., Petti C. 2021. Impacts of the invasive Impatiens glandulifera: Lessons learned from one of Europe’s top invasive species. Biology, 10(7), 619.
  • 6. Čuda J., Rumlerová Z., Brůna J., Skálová H., Pyšek P. 2017a. Floods affect the abundance of invasive Impatiens glandulifera and its spread from river corridors. Diversity and Distributions, 23(4), 342–354.
  • 7. Čuda J., Vitkova M., Albrechtova M., Guo W.Y., Barney J.N., Pyšek P. 2017b. Invasive herb Impatiens glandulifera has minimal impact on multiple components of temperate forest ecosystem function. Biological Invasions, 19(10), 3051–3066.
  • 8. Dajdok Z., Anioł-Kwiatkowska J. 1998. Wstępne wyniki nad ekspansją niecierpka gruczołowatego Impatiens glandulifera Royle w Dolinie Odry. Badania Fizjograficzne nad Polską Zachodnią, Ser. B. 47, 195–204.
  • 9. Helsen K., Diekmann M., Decocq G., De Pauw K., Govaert S., Graae B.J., Hagenblad J., Liira J., Orczewska A., Sanczuk P., Van Meerbeek K., De Frenne P. 2021. Biological flora of Central Europe: Impatiens glandulifera Royle. Perspectives in Plant Ecology, Evolution and Systematics, 50, 125609.
  • 10. Hejda M., Pyšek P. 2006. What is the impact of Impatiens glandulifera on species diversity of invaded riparian vegetation? Biological conservation, 132(2), 143–152.
  • 11. Kostrakiewicz-Gierałt K. 2015. The effect of habitat conditions on the abundance of populations and selected individual and floral traits of Impatiens glandulifera Royle. Biodiversity: Research and Con-servation, 37, 51–58.
  • 12. Kostrakiewicz-Gierałt K., Zając M. 2014. The influence of habitat conditions on the performance of two invasive, annuals — Impatiens glandulifera and Bidens frondosa. Biologia, 69(4), 449–462.
  • 13. Najberek K., Olejniczak P., Berent K., Gąsienica-Staszeczek M., Solarz W. 2020. The ability of seeds to float with water currents contributes to the invasion success of Impatiens balfourii and I. glandu-lifera. Journal of Plant Research, 133(5), 649–664.
  • 14. Pyšek P., Prach K. 1993. Plant invasions and the role of riparian habitats: a comparison of four species alien to central Europe. Journal of Biogeography, 20, 413–420.
  • 15. Sheppard A.W., Shaw R.H., Sforza R. 2006. Top 20 environmental weeds for classical biological control in Europe: a review of opportunities, regulations and other barriers to adoption. Weed Research, 46, 93–117.
  • 16. Staniszewski R. 2022. Invasive Alien Species Impatiens glandulifera Royle-Spread Dynamics, Environmental Impacts and Youth Perception of the Problem. Polish Journal of Environmental Studies, 31(2), 1337–1343.
  • 17. Tokarska-Guzik B. 2005. The establishment and spread of alien plant species (kenophytes) in the flora of Poland. Uniwersytet Śląski, Katowice.
  • 18. Uziębło A.K. 2008. Invasion of Impatiens glandulifera in the surroundings of the Babia Góra National Park (Western Carpathians, Poland). [W:] Plant Invasions: Human perception, ecological impacts and management (red. B. Tokarska-Guzik, J.H. Brock, G. Brundu, L. Child, C.C. Daehler, P. Pyšek). Backhuys Publishers, Leiden, The Netherlands, 161–167.
  • 19. Wyatt A.L., Pardoe H.S., Cleal C.J., Sánchez Vilas J. 2024. Rapid morphological change in UK populations of Impatiens glandulifera. Scientific Reports, 14(1), 19275.
Typ dokumentu
Bibliografia
Identyfikator YADDA
bwmeta1.element.baztech-08a971a0-203a-44e2-8c65-6fb7fa5ae04e
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