Changes in the Distribution of European Mistletoe (Viscum album) in Hungary During the Last Hundred Years
Abstract The hemiparasitic European mistletoe (Viscum album) from the family Viscaceae (Santalaceae s.l.) is able to infest more than 380 woody taxa in Europe. At the beginning of the $ 20^{th} $ century, less than 10 % of Hungary was infested. The distribution area was centralized in the Transdanub...
Ausführliche Beschreibung
Gespeichert in:
| Autor*in: |
Varga, Ildikó [verfasserIn] |
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| Format: |
E-Artikel |
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| Sprache: |
Englisch |
| Erschienen: |
2014 |
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| Schlagwörter: |
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| Anmerkung: |
© Institute of Botany, Academy of Sciences of the Czech Republic 2014 |
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| Übergeordnetes Werk: |
Enthalten in: Folia geobotanica - Dordrecht [u.a.] : Springer, 1966, 49(2014), 4 vom: 12. Aug., Seite 559-577 |
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| Übergeordnetes Werk: |
volume:49 ; year:2014 ; number:4 ; day:12 ; month:08 ; pages:559-577 |
| Links: |
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| DOI / URN: |
10.1007/s12224-014-9193-5 |
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| Katalog-ID: |
SPR025468715 |
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| 520 | |a Abstract The hemiparasitic European mistletoe (Viscum album) from the family Viscaceae (Santalaceae s.l.) is able to infest more than 380 woody taxa in Europe. At the beginning of the $ 20^{th} $ century, less than 10 % of Hungary was infested. The distribution area was centralized in the Transdanubian Mountains, and no mass occurrence was noticed elsewhere. Since then, the infested area has almost tripled, and heavily infested forests can be observed in numerous parts of Hungary, especially in the northeast area of the Hungarian Great Plain. However, the central region of the Hungarian Great Plain is still uninfested. In the North Hungarian Mountains, where the presence of potential hosts is very frequent, mistletoe is still quite rare. The most infested macroregion of Hungary is Western Transdanubia, the only region where all three different subspecies can be found. No significant changes have been observed in the proportions of the most common hosts in the last 90 years, with poplars (Populus spp.) and black locust (Robinia pseudoacacia) still being the most frequently infested species. Silver maple (Acer saccharinum) is now a heavily infested host in city parks, while the abundance of infested apple (Malus spp.) and pear (Pyrus spp.) trees has decreased with the transformation of cultivation techniques. In infested areas, nine to twelve of the most common 18 host species can be found, while only five to eight species can be observed in uninfested areas. The increased mistletoe occurrence can be attributed to several factors, including human impact, larger forest area and a growing number of breeding pairs of the mistle thrush (Turdus viscivorus). | ||
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| 650 | 4 | |a Hungarian macroregions |7 (dpeaa)DE-He213 | |
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| 700 | 1 | |a Pejchal, Miloš |4 aut | |
| 700 | 1 | |a Hyvönen, Jaakko |4 aut | |
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10.1007/s12224-014-9193-5 doi (DE-627)SPR025468715 (SPR)s12224-014-9193-5-e DE-627 ger DE-627 rakwb eng Varga, Ildikó verfasserin aut Changes in the Distribution of European Mistletoe (Viscum album) in Hungary During the Last Hundred Years 2014 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Institute of Botany, Academy of Sciences of the Czech Republic 2014 Abstract The hemiparasitic European mistletoe (Viscum album) from the family Viscaceae (Santalaceae s.l.) is able to infest more than 380 woody taxa in Europe. At the beginning of the $ 20^{th} $ century, less than 10 % of Hungary was infested. The distribution area was centralized in the Transdanubian Mountains, and no mass occurrence was noticed elsewhere. Since then, the infested area has almost tripled, and heavily infested forests can be observed in numerous parts of Hungary, especially in the northeast area of the Hungarian Great Plain. However, the central region of the Hungarian Great Plain is still uninfested. In the North Hungarian Mountains, where the presence of potential hosts is very frequent, mistletoe is still quite rare. The most infested macroregion of Hungary is Western Transdanubia, the only region where all three different subspecies can be found. No significant changes have been observed in the proportions of the most common hosts in the last 90 years, with poplars (Populus spp.) and black locust (Robinia pseudoacacia) still being the most frequently infested species. Silver maple (Acer saccharinum) is now a heavily infested host in city parks, while the abundance of infested apple (Malus spp.) and pear (Pyrus spp.) trees has decreased with the transformation of cultivation techniques. In infested areas, nine to twelve of the most common 18 host species can be found, while only five to eight species can be observed in uninfested areas. The increased mistletoe occurrence can be attributed to several factors, including human impact, larger forest area and a growing number of breeding pairs of the mistle thrush (Turdus viscivorus). distribution map (dpeaa)DE-He213 habitats (dpeaa)DE-He213 hemiparasite (dpeaa)DE-He213 Hungarian macroregions (dpeaa)DE-He213 Poczai, Péter aut Tiborcz, Viktor aut Aranyi, Nikolett Réka aut Baltazár, Tivadar aut Bartha, Dénes aut Pejchal, Miloš aut Hyvönen, Jaakko aut Enthalten in Folia geobotanica Dordrecht [u.a.] : Springer, 1966 49(2014), 4 vom: 12. Aug., Seite 559-577 (DE-627)329555952 (DE-600)2047713-2 1874-9348 nnns volume:49 year:2014 number:4 day:12 month:08 pages:559-577 https://dx.doi.org/10.1007/s12224-014-9193-5 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_206 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_374 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2018 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_2939 GBV_ILN_2946 GBV_ILN_2949 GBV_ILN_2951 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4346 GBV_ILN_4393 GBV_ILN_4700 AR 49 2014 4 12 08 559-577 |
| spelling |
10.1007/s12224-014-9193-5 doi (DE-627)SPR025468715 (SPR)s12224-014-9193-5-e DE-627 ger DE-627 rakwb eng Varga, Ildikó verfasserin aut Changes in the Distribution of European Mistletoe (Viscum album) in Hungary During the Last Hundred Years 2014 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Institute of Botany, Academy of Sciences of the Czech Republic 2014 Abstract The hemiparasitic European mistletoe (Viscum album) from the family Viscaceae (Santalaceae s.l.) is able to infest more than 380 woody taxa in Europe. At the beginning of the $ 20^{th} $ century, less than 10 % of Hungary was infested. The distribution area was centralized in the Transdanubian Mountains, and no mass occurrence was noticed elsewhere. Since then, the infested area has almost tripled, and heavily infested forests can be observed in numerous parts of Hungary, especially in the northeast area of the Hungarian Great Plain. However, the central region of the Hungarian Great Plain is still uninfested. In the North Hungarian Mountains, where the presence of potential hosts is very frequent, mistletoe is still quite rare. The most infested macroregion of Hungary is Western Transdanubia, the only region where all three different subspecies can be found. No significant changes have been observed in the proportions of the most common hosts in the last 90 years, with poplars (Populus spp.) and black locust (Robinia pseudoacacia) still being the most frequently infested species. Silver maple (Acer saccharinum) is now a heavily infested host in city parks, while the abundance of infested apple (Malus spp.) and pear (Pyrus spp.) trees has decreased with the transformation of cultivation techniques. In infested areas, nine to twelve of the most common 18 host species can be found, while only five to eight species can be observed in uninfested areas. The increased mistletoe occurrence can be attributed to several factors, including human impact, larger forest area and a growing number of breeding pairs of the mistle thrush (Turdus viscivorus). distribution map (dpeaa)DE-He213 habitats (dpeaa)DE-He213 hemiparasite (dpeaa)DE-He213 Hungarian macroregions (dpeaa)DE-He213 Poczai, Péter aut Tiborcz, Viktor aut Aranyi, Nikolett Réka aut Baltazár, Tivadar aut Bartha, Dénes aut Pejchal, Miloš aut Hyvönen, Jaakko aut Enthalten in Folia geobotanica Dordrecht [u.a.] : Springer, 1966 49(2014), 4 vom: 12. Aug., Seite 559-577 (DE-627)329555952 (DE-600)2047713-2 1874-9348 nnns volume:49 year:2014 number:4 day:12 month:08 pages:559-577 https://dx.doi.org/10.1007/s12224-014-9193-5 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_206 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_374 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2018 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_2939 GBV_ILN_2946 GBV_ILN_2949 GBV_ILN_2951 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4346 GBV_ILN_4393 GBV_ILN_4700 AR 49 2014 4 12 08 559-577 |
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10.1007/s12224-014-9193-5 doi (DE-627)SPR025468715 (SPR)s12224-014-9193-5-e DE-627 ger DE-627 rakwb eng Varga, Ildikó verfasserin aut Changes in the Distribution of European Mistletoe (Viscum album) in Hungary During the Last Hundred Years 2014 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Institute of Botany, Academy of Sciences of the Czech Republic 2014 Abstract The hemiparasitic European mistletoe (Viscum album) from the family Viscaceae (Santalaceae s.l.) is able to infest more than 380 woody taxa in Europe. At the beginning of the $ 20^{th} $ century, less than 10 % of Hungary was infested. The distribution area was centralized in the Transdanubian Mountains, and no mass occurrence was noticed elsewhere. Since then, the infested area has almost tripled, and heavily infested forests can be observed in numerous parts of Hungary, especially in the northeast area of the Hungarian Great Plain. However, the central region of the Hungarian Great Plain is still uninfested. In the North Hungarian Mountains, where the presence of potential hosts is very frequent, mistletoe is still quite rare. The most infested macroregion of Hungary is Western Transdanubia, the only region where all three different subspecies can be found. No significant changes have been observed in the proportions of the most common hosts in the last 90 years, with poplars (Populus spp.) and black locust (Robinia pseudoacacia) still being the most frequently infested species. Silver maple (Acer saccharinum) is now a heavily infested host in city parks, while the abundance of infested apple (Malus spp.) and pear (Pyrus spp.) trees has decreased with the transformation of cultivation techniques. In infested areas, nine to twelve of the most common 18 host species can be found, while only five to eight species can be observed in uninfested areas. The increased mistletoe occurrence can be attributed to several factors, including human impact, larger forest area and a growing number of breeding pairs of the mistle thrush (Turdus viscivorus). distribution map (dpeaa)DE-He213 habitats (dpeaa)DE-He213 hemiparasite (dpeaa)DE-He213 Hungarian macroregions (dpeaa)DE-He213 Poczai, Péter aut Tiborcz, Viktor aut Aranyi, Nikolett Réka aut Baltazár, Tivadar aut Bartha, Dénes aut Pejchal, Miloš aut Hyvönen, Jaakko aut Enthalten in Folia geobotanica Dordrecht [u.a.] : Springer, 1966 49(2014), 4 vom: 12. Aug., Seite 559-577 (DE-627)329555952 (DE-600)2047713-2 1874-9348 nnns volume:49 year:2014 number:4 day:12 month:08 pages:559-577 https://dx.doi.org/10.1007/s12224-014-9193-5 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_206 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_374 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2018 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_2939 GBV_ILN_2946 GBV_ILN_2949 GBV_ILN_2951 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4346 GBV_ILN_4393 GBV_ILN_4700 AR 49 2014 4 12 08 559-577 |
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10.1007/s12224-014-9193-5 doi (DE-627)SPR025468715 (SPR)s12224-014-9193-5-e DE-627 ger DE-627 rakwb eng Varga, Ildikó verfasserin aut Changes in the Distribution of European Mistletoe (Viscum album) in Hungary During the Last Hundred Years 2014 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Institute of Botany, Academy of Sciences of the Czech Republic 2014 Abstract The hemiparasitic European mistletoe (Viscum album) from the family Viscaceae (Santalaceae s.l.) is able to infest more than 380 woody taxa in Europe. At the beginning of the $ 20^{th} $ century, less than 10 % of Hungary was infested. The distribution area was centralized in the Transdanubian Mountains, and no mass occurrence was noticed elsewhere. Since then, the infested area has almost tripled, and heavily infested forests can be observed in numerous parts of Hungary, especially in the northeast area of the Hungarian Great Plain. However, the central region of the Hungarian Great Plain is still uninfested. In the North Hungarian Mountains, where the presence of potential hosts is very frequent, mistletoe is still quite rare. The most infested macroregion of Hungary is Western Transdanubia, the only region where all three different subspecies can be found. No significant changes have been observed in the proportions of the most common hosts in the last 90 years, with poplars (Populus spp.) and black locust (Robinia pseudoacacia) still being the most frequently infested species. Silver maple (Acer saccharinum) is now a heavily infested host in city parks, while the abundance of infested apple (Malus spp.) and pear (Pyrus spp.) trees has decreased with the transformation of cultivation techniques. In infested areas, nine to twelve of the most common 18 host species can be found, while only five to eight species can be observed in uninfested areas. The increased mistletoe occurrence can be attributed to several factors, including human impact, larger forest area and a growing number of breeding pairs of the mistle thrush (Turdus viscivorus). distribution map (dpeaa)DE-He213 habitats (dpeaa)DE-He213 hemiparasite (dpeaa)DE-He213 Hungarian macroregions (dpeaa)DE-He213 Poczai, Péter aut Tiborcz, Viktor aut Aranyi, Nikolett Réka aut Baltazár, Tivadar aut Bartha, Dénes aut Pejchal, Miloš aut Hyvönen, Jaakko aut Enthalten in Folia geobotanica Dordrecht [u.a.] : Springer, 1966 49(2014), 4 vom: 12. Aug., Seite 559-577 (DE-627)329555952 (DE-600)2047713-2 1874-9348 nnns volume:49 year:2014 number:4 day:12 month:08 pages:559-577 https://dx.doi.org/10.1007/s12224-014-9193-5 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_206 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_374 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2018 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_2939 GBV_ILN_2946 GBV_ILN_2949 GBV_ILN_2951 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4346 GBV_ILN_4393 GBV_ILN_4700 AR 49 2014 4 12 08 559-577 |
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10.1007/s12224-014-9193-5 doi (DE-627)SPR025468715 (SPR)s12224-014-9193-5-e DE-627 ger DE-627 rakwb eng Varga, Ildikó verfasserin aut Changes in the Distribution of European Mistletoe (Viscum album) in Hungary During the Last Hundred Years 2014 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Institute of Botany, Academy of Sciences of the Czech Republic 2014 Abstract The hemiparasitic European mistletoe (Viscum album) from the family Viscaceae (Santalaceae s.l.) is able to infest more than 380 woody taxa in Europe. At the beginning of the $ 20^{th} $ century, less than 10 % of Hungary was infested. The distribution area was centralized in the Transdanubian Mountains, and no mass occurrence was noticed elsewhere. Since then, the infested area has almost tripled, and heavily infested forests can be observed in numerous parts of Hungary, especially in the northeast area of the Hungarian Great Plain. However, the central region of the Hungarian Great Plain is still uninfested. In the North Hungarian Mountains, where the presence of potential hosts is very frequent, mistletoe is still quite rare. The most infested macroregion of Hungary is Western Transdanubia, the only region where all three different subspecies can be found. No significant changes have been observed in the proportions of the most common hosts in the last 90 years, with poplars (Populus spp.) and black locust (Robinia pseudoacacia) still being the most frequently infested species. Silver maple (Acer saccharinum) is now a heavily infested host in city parks, while the abundance of infested apple (Malus spp.) and pear (Pyrus spp.) trees has decreased with the transformation of cultivation techniques. In infested areas, nine to twelve of the most common 18 host species can be found, while only five to eight species can be observed in uninfested areas. The increased mistletoe occurrence can be attributed to several factors, including human impact, larger forest area and a growing number of breeding pairs of the mistle thrush (Turdus viscivorus). distribution map (dpeaa)DE-He213 habitats (dpeaa)DE-He213 hemiparasite (dpeaa)DE-He213 Hungarian macroregions (dpeaa)DE-He213 Poczai, Péter aut Tiborcz, Viktor aut Aranyi, Nikolett Réka aut Baltazár, Tivadar aut Bartha, Dénes aut Pejchal, Miloš aut Hyvönen, Jaakko aut Enthalten in Folia geobotanica Dordrecht [u.a.] : Springer, 1966 49(2014), 4 vom: 12. Aug., Seite 559-577 (DE-627)329555952 (DE-600)2047713-2 1874-9348 nnns volume:49 year:2014 number:4 day:12 month:08 pages:559-577 https://dx.doi.org/10.1007/s12224-014-9193-5 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_206 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_374 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2018 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_2939 GBV_ILN_2946 GBV_ILN_2949 GBV_ILN_2951 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4346 GBV_ILN_4393 GBV_ILN_4700 AR 49 2014 4 12 08 559-577 |
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At the beginning of the $ 20^{th} $ century, less than 10 % of Hungary was infested. The distribution area was centralized in the Transdanubian Mountains, and no mass occurrence was noticed elsewhere. Since then, the infested area has almost tripled, and heavily infested forests can be observed in numerous parts of Hungary, especially in the northeast area of the Hungarian Great Plain. However, the central region of the Hungarian Great Plain is still uninfested. In the North Hungarian Mountains, where the presence of potential hosts is very frequent, mistletoe is still quite rare. The most infested macroregion of Hungary is Western Transdanubia, the only region where all three different subspecies can be found. No significant changes have been observed in the proportions of the most common hosts in the last 90 years, with poplars (Populus spp.) and black locust (Robinia pseudoacacia) still being the most frequently infested species. Silver maple (Acer saccharinum) is now a heavily infested host in city parks, while the abundance of infested apple (Malus spp.) and pear (Pyrus spp.) trees has decreased with the transformation of cultivation techniques. In infested areas, nine to twelve of the most common 18 host species can be found, while only five to eight species can be observed in uninfested areas. 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Varga, Ildikó Poczai, Péter Tiborcz, Viktor Aranyi, Nikolett Réka Baltazár, Tivadar Bartha, Dénes Pejchal, Miloš Hyvönen, Jaakko |
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Elektronische Aufsätze |
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Varga, Ildikó |
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10.1007/s12224-014-9193-5 |
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changes in the distribution of european mistletoe (viscum album) in hungary during the last hundred years |
| title_auth |
Changes in the Distribution of European Mistletoe (Viscum album) in Hungary During the Last Hundred Years |
| abstract |
Abstract The hemiparasitic European mistletoe (Viscum album) from the family Viscaceae (Santalaceae s.l.) is able to infest more than 380 woody taxa in Europe. At the beginning of the $ 20^{th} $ century, less than 10 % of Hungary was infested. The distribution area was centralized in the Transdanubian Mountains, and no mass occurrence was noticed elsewhere. Since then, the infested area has almost tripled, and heavily infested forests can be observed in numerous parts of Hungary, especially in the northeast area of the Hungarian Great Plain. However, the central region of the Hungarian Great Plain is still uninfested. In the North Hungarian Mountains, where the presence of potential hosts is very frequent, mistletoe is still quite rare. The most infested macroregion of Hungary is Western Transdanubia, the only region where all three different subspecies can be found. No significant changes have been observed in the proportions of the most common hosts in the last 90 years, with poplars (Populus spp.) and black locust (Robinia pseudoacacia) still being the most frequently infested species. Silver maple (Acer saccharinum) is now a heavily infested host in city parks, while the abundance of infested apple (Malus spp.) and pear (Pyrus spp.) trees has decreased with the transformation of cultivation techniques. In infested areas, nine to twelve of the most common 18 host species can be found, while only five to eight species can be observed in uninfested areas. The increased mistletoe occurrence can be attributed to several factors, including human impact, larger forest area and a growing number of breeding pairs of the mistle thrush (Turdus viscivorus). © Institute of Botany, Academy of Sciences of the Czech Republic 2014 |
| abstractGer |
Abstract The hemiparasitic European mistletoe (Viscum album) from the family Viscaceae (Santalaceae s.l.) is able to infest more than 380 woody taxa in Europe. At the beginning of the $ 20^{th} $ century, less than 10 % of Hungary was infested. The distribution area was centralized in the Transdanubian Mountains, and no mass occurrence was noticed elsewhere. Since then, the infested area has almost tripled, and heavily infested forests can be observed in numerous parts of Hungary, especially in the northeast area of the Hungarian Great Plain. However, the central region of the Hungarian Great Plain is still uninfested. In the North Hungarian Mountains, where the presence of potential hosts is very frequent, mistletoe is still quite rare. The most infested macroregion of Hungary is Western Transdanubia, the only region where all three different subspecies can be found. No significant changes have been observed in the proportions of the most common hosts in the last 90 years, with poplars (Populus spp.) and black locust (Robinia pseudoacacia) still being the most frequently infested species. Silver maple (Acer saccharinum) is now a heavily infested host in city parks, while the abundance of infested apple (Malus spp.) and pear (Pyrus spp.) trees has decreased with the transformation of cultivation techniques. In infested areas, nine to twelve of the most common 18 host species can be found, while only five to eight species can be observed in uninfested areas. The increased mistletoe occurrence can be attributed to several factors, including human impact, larger forest area and a growing number of breeding pairs of the mistle thrush (Turdus viscivorus). © Institute of Botany, Academy of Sciences of the Czech Republic 2014 |
| abstract_unstemmed |
Abstract The hemiparasitic European mistletoe (Viscum album) from the family Viscaceae (Santalaceae s.l.) is able to infest more than 380 woody taxa in Europe. At the beginning of the $ 20^{th} $ century, less than 10 % of Hungary was infested. The distribution area was centralized in the Transdanubian Mountains, and no mass occurrence was noticed elsewhere. Since then, the infested area has almost tripled, and heavily infested forests can be observed in numerous parts of Hungary, especially in the northeast area of the Hungarian Great Plain. However, the central region of the Hungarian Great Plain is still uninfested. In the North Hungarian Mountains, where the presence of potential hosts is very frequent, mistletoe is still quite rare. The most infested macroregion of Hungary is Western Transdanubia, the only region where all three different subspecies can be found. No significant changes have been observed in the proportions of the most common hosts in the last 90 years, with poplars (Populus spp.) and black locust (Robinia pseudoacacia) still being the most frequently infested species. Silver maple (Acer saccharinum) is now a heavily infested host in city parks, while the abundance of infested apple (Malus spp.) and pear (Pyrus spp.) trees has decreased with the transformation of cultivation techniques. In infested areas, nine to twelve of the most common 18 host species can be found, while only five to eight species can be observed in uninfested areas. The increased mistletoe occurrence can be attributed to several factors, including human impact, larger forest area and a growing number of breeding pairs of the mistle thrush (Turdus viscivorus). © Institute of Botany, Academy of Sciences of the Czech Republic 2014 |
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Changes in the Distribution of European Mistletoe (Viscum album) in Hungary During the Last Hundred Years |
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| score |
7.399864 |