Quantifying the synergistic effects of impervious surface and drought on radial tree growth

Abstract The global trend of increasing urbanization is generating isolated patches of vegetation that could be strongly influenced by the surrounding landscape. Simultaneously, many of these urban forests will be exposed to the increasing temperatures and higher risk of drought conditions brought u...
Ausführliche Beschreibung

Gespeichert in:

Autor*in:	McClung, Teegan [verfasserIn] Ibáñez, Inés [verfasserIn]

Format:	E-Artikel
Sprache:	Englisch

Erschienen:	2017

Schlagwörter:	Basal area increment Northern red oak PDSI Shagbark hickory Sugar maple

Übergeordnetes Werk:	Enthalten in: Urban ecosystems - Dordrecht [u.a.] : Springer Science + Business Media B.V, 1997, 21(2017), 1 vom: 11. Sept., Seite 147-155
Übergeordnetes Werk:	volume:21 ; year:2017 ; number:1 ; day:11 ; month:09 ; pages:147-155

Links:	Volltext

DOI / URN:	10.1007/s11252-017-0699-5

Katalog-ID:	SPR018209750

Internformat


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245	1	0	\|a Quantifying the synergistic effects of impervious surface and drought on radial tree growth
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520			\|a Abstract The global trend of increasing urbanization is generating isolated patches of vegetation that could be strongly influenced by the surrounding landscape. Simultaneously, many of these urban forests will be exposed to the increasing temperatures and higher risk of drought conditions brought up by climate change. The heat island effect associated with an increase in impervious surface cover and its influence on urban vegetation has been document mostly for large urban centers. However, how the effects of urbanization may interact with tree resilience to drought have been much less studied, especially in middle size cities like the majority of those populating eastern North America. In this study, we analyzed 30 years of tree radial growth data collected from individuals of three common native species in remnant forest patches distributed along a gradient of urbanization in the Midwestern USA. Acer saccharum and Quercus rubra show reduced growth rates in years with lower water availability. Our results also indicate that the detrimental effects of impervious surface cover eliminated any of the beneficial effects of growing in a wet year for A. saccharum and Q. rubra, and these effects of increase impervious surface cover on growth were more detrimental than those of droughty years. Carya ovata, the third species, did not show differential growth along the urbanization gradient or among years with varying water availability. This study illustrates how the combination of drought events and increasing impervious surface cover could have a differential impact on coexisting species in urban forests, which could further alter the species composition and functioning of these ecosystems.
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650		4	\|a Sugar maple \|7 (dpeaa)DE-He213
700	1		\|a Ibáñez, Inés \|e verfasserin \|4 aut
773	0	8	\|i Enthalten in \|t Urban ecosystems \|d Dordrecht [u.a.] : Springer Science + Business Media B.V, 1997 \|g 21(2017), 1 vom: 11. Sept., Seite 147-155 \|w (DE-627)320593622 \|w (DE-600)2019257-5 \|x 1573-1642 \|7 nnns
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912			\|a GBV_ILN_23
912			\|a GBV_ILN_24
912			\|a GBV_ILN_31
912			\|a GBV_ILN_32
912			\|a GBV_ILN_39
912			\|a GBV_ILN_40
912			\|a GBV_ILN_60
912			\|a GBV_ILN_62
912			\|a GBV_ILN_63
912			\|a GBV_ILN_69
912			\|a GBV_ILN_70
912			\|a GBV_ILN_73
912			\|a GBV_ILN_74
912			\|a GBV_ILN_90
912			\|a GBV_ILN_95
912			\|a GBV_ILN_100
912			\|a GBV_ILN_101
912			\|a GBV_ILN_105
912			\|a GBV_ILN_110
912			\|a GBV_ILN_120
912			\|a GBV_ILN_138
912			\|a GBV_ILN_150
912			\|a GBV_ILN_151
912			\|a GBV_ILN_152
912			\|a GBV_ILN_161
912			\|a GBV_ILN_170
912			\|a GBV_ILN_171
912			\|a GBV_ILN_187
912			\|a GBV_ILN_213
912			\|a GBV_ILN_224
912			\|a GBV_ILN_230
912			\|a GBV_ILN_250
912			\|a GBV_ILN_281
912			\|a GBV_ILN_285
912			\|a GBV_ILN_293
912			\|a GBV_ILN_370
912			\|a GBV_ILN_602
912			\|a GBV_ILN_636
912			\|a GBV_ILN_702
912			\|a GBV_ILN_2001
912			\|a GBV_ILN_2003
912			\|a GBV_ILN_2004
912			\|a GBV_ILN_2005
912			\|a GBV_ILN_2006
912			\|a GBV_ILN_2007
912			\|a GBV_ILN_2009
912			\|a GBV_ILN_2010
912			\|a GBV_ILN_2011
912			\|a GBV_ILN_2014
912			\|a GBV_ILN_2015
912			\|a GBV_ILN_2020
912			\|a GBV_ILN_2021
912			\|a GBV_ILN_2025
912			\|a GBV_ILN_2026
912			\|a GBV_ILN_2027
912			\|a GBV_ILN_2031
912			\|a GBV_ILN_2034
912			\|a GBV_ILN_2037
912			\|a GBV_ILN_2038
912			\|a GBV_ILN_2039
912			\|a GBV_ILN_2044
912			\|a GBV_ILN_2048
912			\|a GBV_ILN_2049
912			\|a GBV_ILN_2050
912			\|a GBV_ILN_2055
912			\|a GBV_ILN_2057
912			\|a GBV_ILN_2059
912			\|a GBV_ILN_2061
912			\|a GBV_ILN_2064
912			\|a GBV_ILN_2065
912			\|a GBV_ILN_2068
912			\|a GBV_ILN_2070
912			\|a GBV_ILN_2086
912			\|a GBV_ILN_2088
912			\|a GBV_ILN_2093
912			\|a GBV_ILN_2106
912			\|a GBV_ILN_2107
912			\|a GBV_ILN_2108
912			\|a GBV_ILN_2110
912			\|a GBV_ILN_2111
912			\|a GBV_ILN_2112
912			\|a GBV_ILN_2113
912			\|a GBV_ILN_2116
912			\|a GBV_ILN_2118
912			\|a GBV_ILN_2119
912			\|a GBV_ILN_2122
912			\|a GBV_ILN_2129
912			\|a GBV_ILN_2143
912			\|a GBV_ILN_2144
912			\|a GBV_ILN_2147
912			\|a GBV_ILN_2148
912			\|a GBV_ILN_2152
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912			\|a GBV_ILN_2188
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912			\|a GBV_ILN_2232
912			\|a GBV_ILN_2336
912			\|a GBV_ILN_2446
912			\|a GBV_ILN_2470
912			\|a GBV_ILN_2472
912			\|a GBV_ILN_2507
912			\|a GBV_ILN_2522
912			\|a GBV_ILN_2548
912			\|a GBV_ILN_4012
912			\|a GBV_ILN_4035
912			\|a GBV_ILN_4037
912			\|a GBV_ILN_4046
912			\|a GBV_ILN_4112
912			\|a GBV_ILN_4125
912			\|a GBV_ILN_4126
912			\|a GBV_ILN_4242
912			\|a GBV_ILN_4246
912			\|a GBV_ILN_4249
912			\|a GBV_ILN_4251
912			\|a GBV_ILN_4305
912			\|a GBV_ILN_4306
912			\|a GBV_ILN_4307
912			\|a GBV_ILN_4313
912			\|a GBV_ILN_4322
912			\|a GBV_ILN_4323
912			\|a GBV_ILN_4324
912			\|a GBV_ILN_4325
912			\|a GBV_ILN_4326
912			\|a GBV_ILN_4333
912			\|a GBV_ILN_4334
912			\|a GBV_ILN_4335
912			\|a GBV_ILN_4336
912			\|a GBV_ILN_4338
912			\|a GBV_ILN_4393
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Indexfelder

author_variant	t m tm i i ii
matchkey_str	article:15731642:2017----::uniynteyegsiefcsfmevosufcadr
hierarchy_sort_str	2017
bklnumber	42.90 43.31 74.12
publishDate	2017
allfields	10.1007/s11252-017-0699-5 doi (DE-627)SPR018209750 (SPR)s11252-017-0699-5-e DE-627 ger DE-627 rakwb eng 570 ASE 42.90 bkl 43.31 bkl 74.12 bkl McClung, Teegan verfasserin aut Quantifying the synergistic effects of impervious surface and drought on radial tree growth 2017 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract The global trend of increasing urbanization is generating isolated patches of vegetation that could be strongly influenced by the surrounding landscape. Simultaneously, many of these urban forests will be exposed to the increasing temperatures and higher risk of drought conditions brought up by climate change. The heat island effect associated with an increase in impervious surface cover and its influence on urban vegetation has been document mostly for large urban centers. However, how the effects of urbanization may interact with tree resilience to drought have been much less studied, especially in middle size cities like the majority of those populating eastern North America. In this study, we analyzed 30 years of tree radial growth data collected from individuals of three common native species in remnant forest patches distributed along a gradient of urbanization in the Midwestern USA. Acer saccharum and Quercus rubra show reduced growth rates in years with lower water availability. Our results also indicate that the detrimental effects of impervious surface cover eliminated any of the beneficial effects of growing in a wet year for A. saccharum and Q. rubra, and these effects of increase impervious surface cover on growth were more detrimental than those of droughty years. Carya ovata, the third species, did not show differential growth along the urbanization gradient or among years with varying water availability. This study illustrates how the combination of drought events and increasing impervious surface cover could have a differential impact on coexisting species in urban forests, which could further alter the species composition and functioning of these ecosystems. Basal area increment (dpeaa)DE-He213 Northern red oak (dpeaa)DE-He213 PDSI (dpeaa)DE-He213 Shagbark hickory (dpeaa)DE-He213 Sugar maple (dpeaa)DE-He213 Ibáñez, Inés verfasserin aut Enthalten in Urban ecosystems Dordrecht [u.a.] : Springer Science + Business Media B.V, 1997 21(2017), 1 vom: 11. Sept., Seite 147-155 (DE-627)320593622 (DE-600)2019257-5 1573-1642 nnns volume:21 year:2017 number:1 day:11 month:09 pages:147-155 https://dx.doi.org/10.1007/s11252-017-0699-5 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA SSG-OPC-GGO SSG-OPC-ASE 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_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_101 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_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 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_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 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_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_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_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 42.90 ASE 43.31 ASE 74.12 ASE AR 21 2017 1 11 09 147-155
spelling	10.1007/s11252-017-0699-5 doi (DE-627)SPR018209750 (SPR)s11252-017-0699-5-e DE-627 ger DE-627 rakwb eng 570 ASE 42.90 bkl 43.31 bkl 74.12 bkl McClung, Teegan verfasserin aut Quantifying the synergistic effects of impervious surface and drought on radial tree growth 2017 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract The global trend of increasing urbanization is generating isolated patches of vegetation that could be strongly influenced by the surrounding landscape. Simultaneously, many of these urban forests will be exposed to the increasing temperatures and higher risk of drought conditions brought up by climate change. The heat island effect associated with an increase in impervious surface cover and its influence on urban vegetation has been document mostly for large urban centers. However, how the effects of urbanization may interact with tree resilience to drought have been much less studied, especially in middle size cities like the majority of those populating eastern North America. In this study, we analyzed 30 years of tree radial growth data collected from individuals of three common native species in remnant forest patches distributed along a gradient of urbanization in the Midwestern USA. Acer saccharum and Quercus rubra show reduced growth rates in years with lower water availability. Our results also indicate that the detrimental effects of impervious surface cover eliminated any of the beneficial effects of growing in a wet year for A. saccharum and Q. rubra, and these effects of increase impervious surface cover on growth were more detrimental than those of droughty years. Carya ovata, the third species, did not show differential growth along the urbanization gradient or among years with varying water availability. This study illustrates how the combination of drought events and increasing impervious surface cover could have a differential impact on coexisting species in urban forests, which could further alter the species composition and functioning of these ecosystems. Basal area increment (dpeaa)DE-He213 Northern red oak (dpeaa)DE-He213 PDSI (dpeaa)DE-He213 Shagbark hickory (dpeaa)DE-He213 Sugar maple (dpeaa)DE-He213 Ibáñez, Inés verfasserin aut Enthalten in Urban ecosystems Dordrecht [u.a.] : Springer Science + Business Media B.V, 1997 21(2017), 1 vom: 11. Sept., Seite 147-155 (DE-627)320593622 (DE-600)2019257-5 1573-1642 nnns volume:21 year:2017 number:1 day:11 month:09 pages:147-155 https://dx.doi.org/10.1007/s11252-017-0699-5 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA SSG-OPC-GGO SSG-OPC-ASE 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_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_101 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_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 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_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 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_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_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_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 42.90 ASE 43.31 ASE 74.12 ASE AR 21 2017 1 11 09 147-155
allfields_unstemmed	10.1007/s11252-017-0699-5 doi (DE-627)SPR018209750 (SPR)s11252-017-0699-5-e DE-627 ger DE-627 rakwb eng 570 ASE 42.90 bkl 43.31 bkl 74.12 bkl McClung, Teegan verfasserin aut Quantifying the synergistic effects of impervious surface and drought on radial tree growth 2017 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract The global trend of increasing urbanization is generating isolated patches of vegetation that could be strongly influenced by the surrounding landscape. Simultaneously, many of these urban forests will be exposed to the increasing temperatures and higher risk of drought conditions brought up by climate change. The heat island effect associated with an increase in impervious surface cover and its influence on urban vegetation has been document mostly for large urban centers. However, how the effects of urbanization may interact with tree resilience to drought have been much less studied, especially in middle size cities like the majority of those populating eastern North America. In this study, we analyzed 30 years of tree radial growth data collected from individuals of three common native species in remnant forest patches distributed along a gradient of urbanization in the Midwestern USA. Acer saccharum and Quercus rubra show reduced growth rates in years with lower water availability. Our results also indicate that the detrimental effects of impervious surface cover eliminated any of the beneficial effects of growing in a wet year for A. saccharum and Q. rubra, and these effects of increase impervious surface cover on growth were more detrimental than those of droughty years. Carya ovata, the third species, did not show differential growth along the urbanization gradient or among years with varying water availability. This study illustrates how the combination of drought events and increasing impervious surface cover could have a differential impact on coexisting species in urban forests, which could further alter the species composition and functioning of these ecosystems. Basal area increment (dpeaa)DE-He213 Northern red oak (dpeaa)DE-He213 PDSI (dpeaa)DE-He213 Shagbark hickory (dpeaa)DE-He213 Sugar maple (dpeaa)DE-He213 Ibáñez, Inés verfasserin aut Enthalten in Urban ecosystems Dordrecht [u.a.] : Springer Science + Business Media B.V, 1997 21(2017), 1 vom: 11. Sept., Seite 147-155 (DE-627)320593622 (DE-600)2019257-5 1573-1642 nnns volume:21 year:2017 number:1 day:11 month:09 pages:147-155 https://dx.doi.org/10.1007/s11252-017-0699-5 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA SSG-OPC-GGO SSG-OPC-ASE 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_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_101 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_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 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_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 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_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_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_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 42.90 ASE 43.31 ASE 74.12 ASE AR 21 2017 1 11 09 147-155
allfieldsGer	10.1007/s11252-017-0699-5 doi (DE-627)SPR018209750 (SPR)s11252-017-0699-5-e DE-627 ger DE-627 rakwb eng 570 ASE 42.90 bkl 43.31 bkl 74.12 bkl McClung, Teegan verfasserin aut Quantifying the synergistic effects of impervious surface and drought on radial tree growth 2017 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract The global trend of increasing urbanization is generating isolated patches of vegetation that could be strongly influenced by the surrounding landscape. Simultaneously, many of these urban forests will be exposed to the increasing temperatures and higher risk of drought conditions brought up by climate change. The heat island effect associated with an increase in impervious surface cover and its influence on urban vegetation has been document mostly for large urban centers. However, how the effects of urbanization may interact with tree resilience to drought have been much less studied, especially in middle size cities like the majority of those populating eastern North America. In this study, we analyzed 30 years of tree radial growth data collected from individuals of three common native species in remnant forest patches distributed along a gradient of urbanization in the Midwestern USA. Acer saccharum and Quercus rubra show reduced growth rates in years with lower water availability. Our results also indicate that the detrimental effects of impervious surface cover eliminated any of the beneficial effects of growing in a wet year for A. saccharum and Q. rubra, and these effects of increase impervious surface cover on growth were more detrimental than those of droughty years. Carya ovata, the third species, did not show differential growth along the urbanization gradient or among years with varying water availability. This study illustrates how the combination of drought events and increasing impervious surface cover could have a differential impact on coexisting species in urban forests, which could further alter the species composition and functioning of these ecosystems. Basal area increment (dpeaa)DE-He213 Northern red oak (dpeaa)DE-He213 PDSI (dpeaa)DE-He213 Shagbark hickory (dpeaa)DE-He213 Sugar maple (dpeaa)DE-He213 Ibáñez, Inés verfasserin aut Enthalten in Urban ecosystems Dordrecht [u.a.] : Springer Science + Business Media B.V, 1997 21(2017), 1 vom: 11. Sept., Seite 147-155 (DE-627)320593622 (DE-600)2019257-5 1573-1642 nnns volume:21 year:2017 number:1 day:11 month:09 pages:147-155 https://dx.doi.org/10.1007/s11252-017-0699-5 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA SSG-OPC-GGO SSG-OPC-ASE 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_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_101 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_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 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_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 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_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_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_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 42.90 ASE 43.31 ASE 74.12 ASE AR 21 2017 1 11 09 147-155
allfieldsSound	10.1007/s11252-017-0699-5 doi (DE-627)SPR018209750 (SPR)s11252-017-0699-5-e DE-627 ger DE-627 rakwb eng 570 ASE 42.90 bkl 43.31 bkl 74.12 bkl McClung, Teegan verfasserin aut Quantifying the synergistic effects of impervious surface and drought on radial tree growth 2017 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract The global trend of increasing urbanization is generating isolated patches of vegetation that could be strongly influenced by the surrounding landscape. Simultaneously, many of these urban forests will be exposed to the increasing temperatures and higher risk of drought conditions brought up by climate change. The heat island effect associated with an increase in impervious surface cover and its influence on urban vegetation has been document mostly for large urban centers. However, how the effects of urbanization may interact with tree resilience to drought have been much less studied, especially in middle size cities like the majority of those populating eastern North America. In this study, we analyzed 30 years of tree radial growth data collected from individuals of three common native species in remnant forest patches distributed along a gradient of urbanization in the Midwestern USA. Acer saccharum and Quercus rubra show reduced growth rates in years with lower water availability. Our results also indicate that the detrimental effects of impervious surface cover eliminated any of the beneficial effects of growing in a wet year for A. saccharum and Q. rubra, and these effects of increase impervious surface cover on growth were more detrimental than those of droughty years. Carya ovata, the third species, did not show differential growth along the urbanization gradient or among years with varying water availability. This study illustrates how the combination of drought events and increasing impervious surface cover could have a differential impact on coexisting species in urban forests, which could further alter the species composition and functioning of these ecosystems. Basal area increment (dpeaa)DE-He213 Northern red oak (dpeaa)DE-He213 PDSI (dpeaa)DE-He213 Shagbark hickory (dpeaa)DE-He213 Sugar maple (dpeaa)DE-He213 Ibáñez, Inés verfasserin aut Enthalten in Urban ecosystems Dordrecht [u.a.] : Springer Science + Business Media B.V, 1997 21(2017), 1 vom: 11. Sept., Seite 147-155 (DE-627)320593622 (DE-600)2019257-5 1573-1642 nnns volume:21 year:2017 number:1 day:11 month:09 pages:147-155 https://dx.doi.org/10.1007/s11252-017-0699-5 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA SSG-OPC-GGO SSG-OPC-ASE 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_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_101 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_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 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_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 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_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_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_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 42.90 ASE 43.31 ASE 74.12 ASE AR 21 2017 1 11 09 147-155
language	English
source	Enthalten in Urban ecosystems 21(2017), 1 vom: 11. Sept., Seite 147-155 volume:21 year:2017 number:1 day:11 month:09 pages:147-155
sourceStr	Enthalten in Urban ecosystems 21(2017), 1 vom: 11. Sept., Seite 147-155 volume:21 year:2017 number:1 day:11 month:09 pages:147-155
format_phy_str_mv	Article
institution	findex.gbv.de
topic_facet	Basal area increment Northern red oak PDSI Shagbark hickory Sugar maple
dewey-raw	570
isfreeaccess_bool	false
container_title	Urban ecosystems
authorswithroles_txt_mv	McClung, Teegan @@aut@@ Ibáñez, Inés @@aut@@
publishDateDaySort_date	2017-09-11T00:00:00Z
hierarchy_top_id	320593622
dewey-sort	3570
id	SPR018209750
language_de	englisch
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author	McClung, Teegan
spellingShingle	McClung, Teegan ddc 570 bkl 42.90 bkl 43.31 bkl 74.12 misc Basal area increment misc Northern red oak misc PDSI misc Shagbark hickory misc Sugar maple Quantifying the synergistic effects of impervious surface and drought on radial tree growth
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topic_title	570 ASE 42.90 bkl 43.31 bkl 74.12 bkl Quantifying the synergistic effects of impervious surface and drought on radial tree growth Basal area increment (dpeaa)DE-He213 Northern red oak (dpeaa)DE-He213 PDSI (dpeaa)DE-He213 Shagbark hickory (dpeaa)DE-He213 Sugar maple (dpeaa)DE-He213
topic	ddc 570 bkl 42.90 bkl 43.31 bkl 74.12 misc Basal area increment misc Northern red oak misc PDSI misc Shagbark hickory misc Sugar maple
topic_unstemmed	ddc 570 bkl 42.90 bkl 43.31 bkl 74.12 misc Basal area increment misc Northern red oak misc PDSI misc Shagbark hickory misc Sugar maple
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title	Quantifying the synergistic effects of impervious surface and drought on radial tree growth
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title_full	Quantifying the synergistic effects of impervious surface and drought on radial tree growth
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title_sort	quantifying the synergistic effects of impervious surface and drought on radial tree growth
title_auth	Quantifying the synergistic effects of impervious surface and drought on radial tree growth
abstract	Abstract The global trend of increasing urbanization is generating isolated patches of vegetation that could be strongly influenced by the surrounding landscape. Simultaneously, many of these urban forests will be exposed to the increasing temperatures and higher risk of drought conditions brought up by climate change. The heat island effect associated with an increase in impervious surface cover and its influence on urban vegetation has been document mostly for large urban centers. However, how the effects of urbanization may interact with tree resilience to drought have been much less studied, especially in middle size cities like the majority of those populating eastern North America. In this study, we analyzed 30 years of tree radial growth data collected from individuals of three common native species in remnant forest patches distributed along a gradient of urbanization in the Midwestern USA. Acer saccharum and Quercus rubra show reduced growth rates in years with lower water availability. Our results also indicate that the detrimental effects of impervious surface cover eliminated any of the beneficial effects of growing in a wet year for A. saccharum and Q. rubra, and these effects of increase impervious surface cover on growth were more detrimental than those of droughty years. Carya ovata, the third species, did not show differential growth along the urbanization gradient or among years with varying water availability. This study illustrates how the combination of drought events and increasing impervious surface cover could have a differential impact on coexisting species in urban forests, which could further alter the species composition and functioning of these ecosystems.
abstractGer	Abstract The global trend of increasing urbanization is generating isolated patches of vegetation that could be strongly influenced by the surrounding landscape. Simultaneously, many of these urban forests will be exposed to the increasing temperatures and higher risk of drought conditions brought up by climate change. The heat island effect associated with an increase in impervious surface cover and its influence on urban vegetation has been document mostly for large urban centers. However, how the effects of urbanization may interact with tree resilience to drought have been much less studied, especially in middle size cities like the majority of those populating eastern North America. In this study, we analyzed 30 years of tree radial growth data collected from individuals of three common native species in remnant forest patches distributed along a gradient of urbanization in the Midwestern USA. Acer saccharum and Quercus rubra show reduced growth rates in years with lower water availability. Our results also indicate that the detrimental effects of impervious surface cover eliminated any of the beneficial effects of growing in a wet year for A. saccharum and Q. rubra, and these effects of increase impervious surface cover on growth were more detrimental than those of droughty years. Carya ovata, the third species, did not show differential growth along the urbanization gradient or among years with varying water availability. This study illustrates how the combination of drought events and increasing impervious surface cover could have a differential impact on coexisting species in urban forests, which could further alter the species composition and functioning of these ecosystems.
abstract_unstemmed	Abstract The global trend of increasing urbanization is generating isolated patches of vegetation that could be strongly influenced by the surrounding landscape. Simultaneously, many of these urban forests will be exposed to the increasing temperatures and higher risk of drought conditions brought up by climate change. The heat island effect associated with an increase in impervious surface cover and its influence on urban vegetation has been document mostly for large urban centers. However, how the effects of urbanization may interact with tree resilience to drought have been much less studied, especially in middle size cities like the majority of those populating eastern North America. In this study, we analyzed 30 years of tree radial growth data collected from individuals of three common native species in remnant forest patches distributed along a gradient of urbanization in the Midwestern USA. Acer saccharum and Quercus rubra show reduced growth rates in years with lower water availability. Our results also indicate that the detrimental effects of impervious surface cover eliminated any of the beneficial effects of growing in a wet year for A. saccharum and Q. rubra, and these effects of increase impervious surface cover on growth were more detrimental than those of droughty years. Carya ovata, the third species, did not show differential growth along the urbanization gradient or among years with varying water availability. This study illustrates how the combination of drought events and increasing impervious surface cover could have a differential impact on coexisting species in urban forests, which could further alter the species composition and functioning of these ecosystems.
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title_short	Quantifying the synergistic effects of impervious surface and drought on radial tree growth
url	https://dx.doi.org/10.1007/s11252-017-0699-5
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doi_str	10.1007/s11252-017-0699-5
up_date	2024-07-03T18:10:17.526Z
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Simultaneously, many of these urban forests will be exposed to the increasing temperatures and higher risk of drought conditions brought up by climate change. The heat island effect associated with an increase in impervious surface cover and its influence on urban vegetation has been document mostly for large urban centers. However, how the effects of urbanization may interact with tree resilience to drought have been much less studied, especially in middle size cities like the majority of those populating eastern North America. In this study, we analyzed 30 years of tree radial growth data collected from individuals of three common native species in remnant forest patches distributed along a gradient of urbanization in the Midwestern USA. Acer saccharum and Quercus rubra show reduced growth rates in years with lower water availability. Our results also indicate that the detrimental effects of impervious surface cover eliminated any of the beneficial effects of growing in a wet year for A. saccharum and Q. rubra, and these effects of increase impervious surface cover on growth were more detrimental than those of droughty years. Carya ovata, the third species, did not show differential growth along the urbanization gradient or among years with varying water availability. 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Quantifying the synergistic effects of impervious surface and drought on radial tree growth

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