Bee and wasp responses to a fragmented landscape in southern Brazil

Abstract The available studies on Hymenoptera assemblages in fragmented landscapes have shown that these insects are sensitive to fragmentation, besides some different conclusions which are possibly linked to different landscape attributes and sampling designs. The present objective is to determine...
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Autor*in:	Gonçalves, Rodrigo B. [verfasserIn] Sydney, Nicolle V. [verfasserIn] Oliveira, Priscila S. [verfasserIn] Artmann, Nathiele O. [verfasserIn]

Format:	E-Artikel
Sprache:	Englisch

Erschienen:	2014

Schlagwörter:	Anthophila Apoidea Biodiversity loss Conservation

Übergeordnetes Werk:	Enthalten in: Journal of insect conservation - Dordrecht [u.a.] : Springer Science + Business Media B.V, 1997, 18(2014), 6 vom: 16. Nov., Seite 1193-1201
Übergeordnetes Werk:	volume:18 ; year:2014 ; number:6 ; day:16 ; month:11 ; pages:1193-1201

Links:	Volltext

DOI / URN:	10.1007/s10841-014-9730-9

Katalog-ID:	SPR013655345

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100	1		\|a Gonçalves, Rodrigo B. \|e verfasserin \|4 aut
245	1	0	\|a Bee and wasp responses to a fragmented landscape in southern Brazil
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520			\|a Abstract The available studies on Hymenoptera assemblages in fragmented landscapes have shown that these insects are sensitive to fragmentation, besides some different conclusions which are possibly linked to different landscape attributes and sampling designs. The present objective is to determine the correlation among the descriptors of bees and wasps assemblages with fragment predictors (size, connectivity and edge effect) within a fragmented landscape of Semidecidual Seasonal Forest (Paraná State, Brazil). For this purpose five forest fragments, from three to 484 hectares, were sampled during a year, summing up 480 samples of baited traps and 3,480 of bowl traps. We have found that abundance of Apinae and oligolectic bees increase and the richness of Augochlorini bees decreases with increasing fragment size. Connectivity has positively influenced bee richness and edge effect has positively influenced the abundance of oligoletic bees. Orchid bees also respond to the site predictors, especially for the Eufriesea violacea, which abundance was positively correlated with fragment size and connectivity, however negatively with edge effect, and Eufriesea nigrita which abundance was negatively correlated with fragment size, but positively with edge effect. Composition of bees, Crabronidae and Pompilidae wasps were influenced by fragment size. Plebeia droryana and Tetrapedia diversipes could be considered as indicators, according to their sensitiveness to habitat predictors. Our results are congruent with previous studies which found that bees are sensitive to landscape fragmentation, we suggest that the group be used in ecological indicator and monitoring studies.
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650		4	\|a Conservation \|7 (dpeaa)DE-He213
700	1		\|a Sydney, Nicolle V. \|e verfasserin \|4 aut
700	1		\|a Oliveira, Priscila S. \|e verfasserin \|4 aut
700	1		\|a Artmann, Nathiele O. \|e verfasserin \|4 aut
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matchkey_str	article:15729753:2014----::eadapepnetargetdadcpi
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publishDate	2014
allfields	10.1007/s10841-014-9730-9 doi (DE-627)SPR013655345 (SPR)s10841-014-9730-9-e DE-627 ger DE-627 rakwb eng 590 ASE 42.00 bkl Gonçalves, Rodrigo B. verfasserin aut Bee and wasp responses to a fragmented landscape in southern Brazil 2014 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract The available studies on Hymenoptera assemblages in fragmented landscapes have shown that these insects are sensitive to fragmentation, besides some different conclusions which are possibly linked to different landscape attributes and sampling designs. The present objective is to determine the correlation among the descriptors of bees and wasps assemblages with fragment predictors (size, connectivity and edge effect) within a fragmented landscape of Semidecidual Seasonal Forest (Paraná State, Brazil). For this purpose five forest fragments, from three to 484 hectares, were sampled during a year, summing up 480 samples of baited traps and 3,480 of bowl traps. We have found that abundance of Apinae and oligolectic bees increase and the richness of Augochlorini bees decreases with increasing fragment size. Connectivity has positively influenced bee richness and edge effect has positively influenced the abundance of oligoletic bees. Orchid bees also respond to the site predictors, especially for the Eufriesea violacea, which abundance was positively correlated with fragment size and connectivity, however negatively with edge effect, and Eufriesea nigrita which abundance was negatively correlated with fragment size, but positively with edge effect. Composition of bees, Crabronidae and Pompilidae wasps were influenced by fragment size. Plebeia droryana and Tetrapedia diversipes could be considered as indicators, according to their sensitiveness to habitat predictors. Our results are congruent with previous studies which found that bees are sensitive to landscape fragmentation, we suggest that the group be used in ecological indicator and monitoring studies. Anthophila (dpeaa)DE-He213 Apoidea (dpeaa)DE-He213 Biodiversity loss (dpeaa)DE-He213 Conservation (dpeaa)DE-He213 Sydney, Nicolle V. verfasserin aut Oliveira, Priscila S. verfasserin aut Artmann, Nathiele O. verfasserin aut Enthalten in Journal of insect conservation Dordrecht [u.a.] : Springer Science + Business Media B.V, 1997 18(2014), 6 vom: 16. Nov., Seite 1193-1201 (DE-627)320575330 (DE-600)2016976-0 1572-9753 nnns volume:18 year:2014 number:6 day:16 month:11 pages:1193-1201 https://dx.doi.org/10.1007/s10841-014-9730-9 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER 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_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_2008 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 42.00 ASE AR 18 2014 6 16 11 1193-1201
spelling	10.1007/s10841-014-9730-9 doi (DE-627)SPR013655345 (SPR)s10841-014-9730-9-e DE-627 ger DE-627 rakwb eng 590 ASE 42.00 bkl Gonçalves, Rodrigo B. verfasserin aut Bee and wasp responses to a fragmented landscape in southern Brazil 2014 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract The available studies on Hymenoptera assemblages in fragmented landscapes have shown that these insects are sensitive to fragmentation, besides some different conclusions which are possibly linked to different landscape attributes and sampling designs. The present objective is to determine the correlation among the descriptors of bees and wasps assemblages with fragment predictors (size, connectivity and edge effect) within a fragmented landscape of Semidecidual Seasonal Forest (Paraná State, Brazil). For this purpose five forest fragments, from three to 484 hectares, were sampled during a year, summing up 480 samples of baited traps and 3,480 of bowl traps. We have found that abundance of Apinae and oligolectic bees increase and the richness of Augochlorini bees decreases with increasing fragment size. Connectivity has positively influenced bee richness and edge effect has positively influenced the abundance of oligoletic bees. Orchid bees also respond to the site predictors, especially for the Eufriesea violacea, which abundance was positively correlated with fragment size and connectivity, however negatively with edge effect, and Eufriesea nigrita which abundance was negatively correlated with fragment size, but positively with edge effect. Composition of bees, Crabronidae and Pompilidae wasps were influenced by fragment size. Plebeia droryana and Tetrapedia diversipes could be considered as indicators, according to their sensitiveness to habitat predictors. Our results are congruent with previous studies which found that bees are sensitive to landscape fragmentation, we suggest that the group be used in ecological indicator and monitoring studies. Anthophila (dpeaa)DE-He213 Apoidea (dpeaa)DE-He213 Biodiversity loss (dpeaa)DE-He213 Conservation (dpeaa)DE-He213 Sydney, Nicolle V. verfasserin aut Oliveira, Priscila S. verfasserin aut Artmann, Nathiele O. verfasserin aut Enthalten in Journal of insect conservation Dordrecht [u.a.] : Springer Science + Business Media B.V, 1997 18(2014), 6 vom: 16. Nov., Seite 1193-1201 (DE-627)320575330 (DE-600)2016976-0 1572-9753 nnns volume:18 year:2014 number:6 day:16 month:11 pages:1193-1201 https://dx.doi.org/10.1007/s10841-014-9730-9 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER 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_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_2008 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 42.00 ASE AR 18 2014 6 16 11 1193-1201
allfields_unstemmed	10.1007/s10841-014-9730-9 doi (DE-627)SPR013655345 (SPR)s10841-014-9730-9-e DE-627 ger DE-627 rakwb eng 590 ASE 42.00 bkl Gonçalves, Rodrigo B. verfasserin aut Bee and wasp responses to a fragmented landscape in southern Brazil 2014 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract The available studies on Hymenoptera assemblages in fragmented landscapes have shown that these insects are sensitive to fragmentation, besides some different conclusions which are possibly linked to different landscape attributes and sampling designs. The present objective is to determine the correlation among the descriptors of bees and wasps assemblages with fragment predictors (size, connectivity and edge effect) within a fragmented landscape of Semidecidual Seasonal Forest (Paraná State, Brazil). For this purpose five forest fragments, from three to 484 hectares, were sampled during a year, summing up 480 samples of baited traps and 3,480 of bowl traps. We have found that abundance of Apinae and oligolectic bees increase and the richness of Augochlorini bees decreases with increasing fragment size. Connectivity has positively influenced bee richness and edge effect has positively influenced the abundance of oligoletic bees. Orchid bees also respond to the site predictors, especially for the Eufriesea violacea, which abundance was positively correlated with fragment size and connectivity, however negatively with edge effect, and Eufriesea nigrita which abundance was negatively correlated with fragment size, but positively with edge effect. Composition of bees, Crabronidae and Pompilidae wasps were influenced by fragment size. Plebeia droryana and Tetrapedia diversipes could be considered as indicators, according to their sensitiveness to habitat predictors. Our results are congruent with previous studies which found that bees are sensitive to landscape fragmentation, we suggest that the group be used in ecological indicator and monitoring studies. Anthophila (dpeaa)DE-He213 Apoidea (dpeaa)DE-He213 Biodiversity loss (dpeaa)DE-He213 Conservation (dpeaa)DE-He213 Sydney, Nicolle V. verfasserin aut Oliveira, Priscila S. verfasserin aut Artmann, Nathiele O. verfasserin aut Enthalten in Journal of insect conservation Dordrecht [u.a.] : Springer Science + Business Media B.V, 1997 18(2014), 6 vom: 16. Nov., Seite 1193-1201 (DE-627)320575330 (DE-600)2016976-0 1572-9753 nnns volume:18 year:2014 number:6 day:16 month:11 pages:1193-1201 https://dx.doi.org/10.1007/s10841-014-9730-9 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER 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_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_2008 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 42.00 ASE AR 18 2014 6 16 11 1193-1201
allfieldsGer	10.1007/s10841-014-9730-9 doi (DE-627)SPR013655345 (SPR)s10841-014-9730-9-e DE-627 ger DE-627 rakwb eng 590 ASE 42.00 bkl Gonçalves, Rodrigo B. verfasserin aut Bee and wasp responses to a fragmented landscape in southern Brazil 2014 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract The available studies on Hymenoptera assemblages in fragmented landscapes have shown that these insects are sensitive to fragmentation, besides some different conclusions which are possibly linked to different landscape attributes and sampling designs. The present objective is to determine the correlation among the descriptors of bees and wasps assemblages with fragment predictors (size, connectivity and edge effect) within a fragmented landscape of Semidecidual Seasonal Forest (Paraná State, Brazil). For this purpose five forest fragments, from three to 484 hectares, were sampled during a year, summing up 480 samples of baited traps and 3,480 of bowl traps. We have found that abundance of Apinae and oligolectic bees increase and the richness of Augochlorini bees decreases with increasing fragment size. Connectivity has positively influenced bee richness and edge effect has positively influenced the abundance of oligoletic bees. Orchid bees also respond to the site predictors, especially for the Eufriesea violacea, which abundance was positively correlated with fragment size and connectivity, however negatively with edge effect, and Eufriesea nigrita which abundance was negatively correlated with fragment size, but positively with edge effect. Composition of bees, Crabronidae and Pompilidae wasps were influenced by fragment size. Plebeia droryana and Tetrapedia diversipes could be considered as indicators, according to their sensitiveness to habitat predictors. Our results are congruent with previous studies which found that bees are sensitive to landscape fragmentation, we suggest that the group be used in ecological indicator and monitoring studies. Anthophila (dpeaa)DE-He213 Apoidea (dpeaa)DE-He213 Biodiversity loss (dpeaa)DE-He213 Conservation (dpeaa)DE-He213 Sydney, Nicolle V. verfasserin aut Oliveira, Priscila S. verfasserin aut Artmann, Nathiele O. verfasserin aut Enthalten in Journal of insect conservation Dordrecht [u.a.] : Springer Science + Business Media B.V, 1997 18(2014), 6 vom: 16. Nov., Seite 1193-1201 (DE-627)320575330 (DE-600)2016976-0 1572-9753 nnns volume:18 year:2014 number:6 day:16 month:11 pages:1193-1201 https://dx.doi.org/10.1007/s10841-014-9730-9 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER 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_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_2008 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 42.00 ASE AR 18 2014 6 16 11 1193-1201
allfieldsSound	10.1007/s10841-014-9730-9 doi (DE-627)SPR013655345 (SPR)s10841-014-9730-9-e DE-627 ger DE-627 rakwb eng 590 ASE 42.00 bkl Gonçalves, Rodrigo B. verfasserin aut Bee and wasp responses to a fragmented landscape in southern Brazil 2014 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract The available studies on Hymenoptera assemblages in fragmented landscapes have shown that these insects are sensitive to fragmentation, besides some different conclusions which are possibly linked to different landscape attributes and sampling designs. The present objective is to determine the correlation among the descriptors of bees and wasps assemblages with fragment predictors (size, connectivity and edge effect) within a fragmented landscape of Semidecidual Seasonal Forest (Paraná State, Brazil). For this purpose five forest fragments, from three to 484 hectares, were sampled during a year, summing up 480 samples of baited traps and 3,480 of bowl traps. We have found that abundance of Apinae and oligolectic bees increase and the richness of Augochlorini bees decreases with increasing fragment size. Connectivity has positively influenced bee richness and edge effect has positively influenced the abundance of oligoletic bees. Orchid bees also respond to the site predictors, especially for the Eufriesea violacea, which abundance was positively correlated with fragment size and connectivity, however negatively with edge effect, and Eufriesea nigrita which abundance was negatively correlated with fragment size, but positively with edge effect. Composition of bees, Crabronidae and Pompilidae wasps were influenced by fragment size. Plebeia droryana and Tetrapedia diversipes could be considered as indicators, according to their sensitiveness to habitat predictors. Our results are congruent with previous studies which found that bees are sensitive to landscape fragmentation, we suggest that the group be used in ecological indicator and monitoring studies. Anthophila (dpeaa)DE-He213 Apoidea (dpeaa)DE-He213 Biodiversity loss (dpeaa)DE-He213 Conservation (dpeaa)DE-He213 Sydney, Nicolle V. verfasserin aut Oliveira, Priscila S. verfasserin aut Artmann, Nathiele O. verfasserin aut Enthalten in Journal of insect conservation Dordrecht [u.a.] : Springer Science + Business Media B.V, 1997 18(2014), 6 vom: 16. Nov., Seite 1193-1201 (DE-627)320575330 (DE-600)2016976-0 1572-9753 nnns volume:18 year:2014 number:6 day:16 month:11 pages:1193-1201 https://dx.doi.org/10.1007/s10841-014-9730-9 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER 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_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_2008 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 42.00 ASE AR 18 2014 6 16 11 1193-1201
language	English
source	Enthalten in Journal of insect conservation 18(2014), 6 vom: 16. Nov., Seite 1193-1201 volume:18 year:2014 number:6 day:16 month:11 pages:1193-1201
sourceStr	Enthalten in Journal of insect conservation 18(2014), 6 vom: 16. Nov., Seite 1193-1201 volume:18 year:2014 number:6 day:16 month:11 pages:1193-1201
format_phy_str_mv	Article
institution	findex.gbv.de
topic_facet	Anthophila Apoidea Biodiversity loss Conservation
dewey-raw	590
isfreeaccess_bool	false
container_title	Journal of insect conservation
authorswithroles_txt_mv	Gonçalves, Rodrigo B. @@aut@@ Sydney, Nicolle V. @@aut@@ Oliveira, Priscila S. @@aut@@ Artmann, Nathiele O. @@aut@@
publishDateDaySort_date	2014-11-16T00:00:00Z
hierarchy_top_id	320575330
dewey-sort	3590
id	SPR013655345
language_de	englisch
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author	Gonçalves, Rodrigo B.
spellingShingle	Gonçalves, Rodrigo B. ddc 590 bkl 42.00 misc Anthophila misc Apoidea misc Biodiversity loss misc Conservation Bee and wasp responses to a fragmented landscape in southern Brazil
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topic_title	590 ASE 42.00 bkl Bee and wasp responses to a fragmented landscape in southern Brazil Anthophila (dpeaa)DE-He213 Apoidea (dpeaa)DE-He213 Biodiversity loss (dpeaa)DE-He213 Conservation (dpeaa)DE-He213
topic	ddc 590 bkl 42.00 misc Anthophila misc Apoidea misc Biodiversity loss misc Conservation
topic_unstemmed	ddc 590 bkl 42.00 misc Anthophila misc Apoidea misc Biodiversity loss misc Conservation
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title	Bee and wasp responses to a fragmented landscape in southern Brazil
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title_full	Bee and wasp responses to a fragmented landscape in southern Brazil
author_sort	Gonçalves, Rodrigo B.
journal	Journal of insect conservation
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author_browse	Gonçalves, Rodrigo B. Sydney, Nicolle V. Oliveira, Priscila S. Artmann, Nathiele O.
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title_sort	bee and wasp responses to a fragmented landscape in southern brazil
title_auth	Bee and wasp responses to a fragmented landscape in southern Brazil
abstract	Abstract The available studies on Hymenoptera assemblages in fragmented landscapes have shown that these insects are sensitive to fragmentation, besides some different conclusions which are possibly linked to different landscape attributes and sampling designs. The present objective is to determine the correlation among the descriptors of bees and wasps assemblages with fragment predictors (size, connectivity and edge effect) within a fragmented landscape of Semidecidual Seasonal Forest (Paraná State, Brazil). For this purpose five forest fragments, from three to 484 hectares, were sampled during a year, summing up 480 samples of baited traps and 3,480 of bowl traps. We have found that abundance of Apinae and oligolectic bees increase and the richness of Augochlorini bees decreases with increasing fragment size. Connectivity has positively influenced bee richness and edge effect has positively influenced the abundance of oligoletic bees. Orchid bees also respond to the site predictors, especially for the Eufriesea violacea, which abundance was positively correlated with fragment size and connectivity, however negatively with edge effect, and Eufriesea nigrita which abundance was negatively correlated with fragment size, but positively with edge effect. Composition of bees, Crabronidae and Pompilidae wasps were influenced by fragment size. Plebeia droryana and Tetrapedia diversipes could be considered as indicators, according to their sensitiveness to habitat predictors. Our results are congruent with previous studies which found that bees are sensitive to landscape fragmentation, we suggest that the group be used in ecological indicator and monitoring studies.
abstractGer	Abstract The available studies on Hymenoptera assemblages in fragmented landscapes have shown that these insects are sensitive to fragmentation, besides some different conclusions which are possibly linked to different landscape attributes and sampling designs. The present objective is to determine the correlation among the descriptors of bees and wasps assemblages with fragment predictors (size, connectivity and edge effect) within a fragmented landscape of Semidecidual Seasonal Forest (Paraná State, Brazil). For this purpose five forest fragments, from three to 484 hectares, were sampled during a year, summing up 480 samples of baited traps and 3,480 of bowl traps. We have found that abundance of Apinae and oligolectic bees increase and the richness of Augochlorini bees decreases with increasing fragment size. Connectivity has positively influenced bee richness and edge effect has positively influenced the abundance of oligoletic bees. Orchid bees also respond to the site predictors, especially for the Eufriesea violacea, which abundance was positively correlated with fragment size and connectivity, however negatively with edge effect, and Eufriesea nigrita which abundance was negatively correlated with fragment size, but positively with edge effect. Composition of bees, Crabronidae and Pompilidae wasps were influenced by fragment size. Plebeia droryana and Tetrapedia diversipes could be considered as indicators, according to their sensitiveness to habitat predictors. Our results are congruent with previous studies which found that bees are sensitive to landscape fragmentation, we suggest that the group be used in ecological indicator and monitoring studies.
abstract_unstemmed	Abstract The available studies on Hymenoptera assemblages in fragmented landscapes have shown that these insects are sensitive to fragmentation, besides some different conclusions which are possibly linked to different landscape attributes and sampling designs. The present objective is to determine the correlation among the descriptors of bees and wasps assemblages with fragment predictors (size, connectivity and edge effect) within a fragmented landscape of Semidecidual Seasonal Forest (Paraná State, Brazil). For this purpose five forest fragments, from three to 484 hectares, were sampled during a year, summing up 480 samples of baited traps and 3,480 of bowl traps. We have found that abundance of Apinae and oligolectic bees increase and the richness of Augochlorini bees decreases with increasing fragment size. Connectivity has positively influenced bee richness and edge effect has positively influenced the abundance of oligoletic bees. Orchid bees also respond to the site predictors, especially for the Eufriesea violacea, which abundance was positively correlated with fragment size and connectivity, however negatively with edge effect, and Eufriesea nigrita which abundance was negatively correlated with fragment size, but positively with edge effect. Composition of bees, Crabronidae and Pompilidae wasps were influenced by fragment size. Plebeia droryana and Tetrapedia diversipes could be considered as indicators, according to their sensitiveness to habitat predictors. Our results are congruent with previous studies which found that bees are sensitive to landscape fragmentation, we suggest that the group be used in ecological indicator and monitoring studies.
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title_short	Bee and wasp responses to a fragmented landscape in southern Brazil
url	https://dx.doi.org/10.1007/s10841-014-9730-9
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author2	Sydney, Nicolle V. Oliveira, Priscila S. Artmann, Nathiele O.
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up_date	2024-07-03T21:15:52.074Z
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The present objective is to determine the correlation among the descriptors of bees and wasps assemblages with fragment predictors (size, connectivity and edge effect) within a fragmented landscape of Semidecidual Seasonal Forest (Paraná State, Brazil). For this purpose five forest fragments, from three to 484 hectares, were sampled during a year, summing up 480 samples of baited traps and 3,480 of bowl traps. We have found that abundance of Apinae and oligolectic bees increase and the richness of Augochlorini bees decreases with increasing fragment size. Connectivity has positively influenced bee richness and edge effect has positively influenced the abundance of oligoletic bees. Orchid bees also respond to the site predictors, especially for the Eufriesea violacea, which abundance was positively correlated with fragment size and connectivity, however negatively with edge effect, and Eufriesea nigrita which abundance was negatively correlated with fragment size, but positively with edge effect. Composition of bees, Crabronidae and Pompilidae wasps were influenced by fragment size. Plebeia droryana and Tetrapedia diversipes could be considered as indicators, according to their sensitiveness to habitat predictors. 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