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en Effects of forest fragmentation on european birds: implications of regional differences in species richness. -
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del recurso Acceso al recurso a2026-06-25
(anteriormente2026-06-23
) en Effects of forest fragmentation on european birds: implications of regional differences in species richness.
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| 79 | "notes": "Aim: In this paper, we adopted a large-scale approach to | 93 | "notes": "Aim: In this paper, we adopted a large-scale approach to | ||
| 80 | evaluate the effect of regional richness of forest birds on the number | 94 | evaluate the effect of regional richness of forest birds on the number | ||
| 81 | of bird species retained by forest fragments in several localities | 95 | of bird species retained by forest fragments in several localities | ||
| 82 | across Europe. Location: We studied bird assemblages in fourteen | 96 | across Europe. Location: We studied bird assemblages in fourteen | ||
| 83 | forest archipelagos embedded in agricultural matrices from southern | 97 | forest archipelagos embedded in agricultural matrices from southern | ||
| 84 | Norway to central Spain. Tree composition varied from oak and beech | 98 | Norway to central Spain. Tree composition varied from oak and beech | ||
| 85 | forests of the northern localities to oak and pine xerophitic | 99 | forests of the northern localities to oak and pine xerophitic | ||
| 86 | woodlands of the southern ones. The number of fragments in each forest | 100 | woodlands of the southern ones. The number of fragments in each forest | ||
| 87 | archipelago ranged from eighteen to 211. Methods: We used the Gleason | 101 | archipelago ranged from eighteen to 211. Methods: We used the Gleason | ||
| 88 | equation (s=a+z log A; where s and A are, respectively, the species | 102 | equation (s=a+z log A; where s and A are, respectively, the species | ||
| 89 | richness and size of forest fragments and z the rate of species loss) | 103 | richness and size of forest fragments and z the rate of species loss) | ||
| 90 | to estimate the species richness for 1- and 15-ha fragments in each | 104 | to estimate the species richness for 1- and 15-ha fragments in each | ||
| 91 | archipelago. The regional richness of forest birds was estimated by | 105 | archipelago. The regional richness of forest birds was estimated by | ||
| 92 | modelling the geographical distribution of species richness in the | 106 | modelling the geographical distribution of species richness in the | ||
| 93 | European atlas of breeding birds. Results: The latitudinal | 107 | European atlas of breeding birds. Results: The latitudinal | ||
| 94 | distribution of regional richness displayed a convex form, with the | 108 | distribution of regional richness displayed a convex form, with the | ||
| 95 | highest values being in central Europe. Along this gradient, the | 109 | highest values being in central Europe. Along this gradient, the | ||
| 96 | number of species retained by fragments and the rate of species loss | 110 | number of species retained by fragments and the rate of species loss | ||
| 97 | was positively related to regional richness. In addition, the | 111 | was positively related to regional richness. In addition, the | ||
| 98 | percentage of the regional pool of species sampled by fragments | 112 | percentage of the regional pool of species sampled by fragments | ||
| 99 | decreased in the southern localities. Main conclusions: Relationships | 113 | decreased in the southern localities. Main conclusions: Relationships | ||
| 100 | between regional richness of forest birds and richness in fragments | 114 | between regional richness of forest birds and richness in fragments | ||
| 101 | seem to explain why fragments in central Europe shelter more species | 115 | seem to explain why fragments in central Europe shelter more species | ||
| 102 | than their southern counterparts. The decreased ability of southern | 116 | than their southern counterparts. The decreased ability of southern | ||
| 103 | forest fragments to sample the regional richness of forest birds, | 117 | forest fragments to sample the regional richness of forest birds, | ||
| 104 | could be explained as an effect of the low abundance of many species | 118 | could be explained as an effect of the low abundance of many species | ||
| 105 | in the Mediterranean, which could depress their ability to prevent | 119 | in the Mediterranean, which could depress their ability to prevent | ||
| 106 | extinction in fragments by a rescue effect. Alternatively, high beta | 120 | extinction in fragments by a rescue effect. Alternatively, high beta | ||
| 107 | diversity in the Mediterranean could produce undersampling by | 121 | diversity in the Mediterranean could produce undersampling by | ||
| 108 | fragments of the regional pool of species. These regional differences | 122 | fragments of the regional pool of species. These regional differences | ||
| 109 | in the response of bird assemblages to forest fragmentation are used | 123 | in the response of bird assemblages to forest fragmentation are used | ||
| 110 | to discuss the usefulness of large-scale, biogeographical approaches | 124 | to discuss the usefulness of large-scale, biogeographical approaches | ||
| 111 | in the design of conservation guidelines.\n Palabras clave: Arable | 125 | in the design of conservation guidelines.\n Palabras clave: Arable | ||
| 112 | land, Biodiversity, Bird, Forest, Fragmentation, Mosaic", | 126 | land, Biodiversity, Bird, Forest, Fragmentation, Mosaic", | ||
| 113 | "notes_translated": { | 127 | "notes_translated": { | ||
| 114 | "en": "Aim: In this paper, we adopted a large-scale approach to | 128 | "en": "Aim: In this paper, we adopted a large-scale approach to | ||
| 115 | evaluate the effect of regional richness of forest birds on the number | 129 | evaluate the effect of regional richness of forest birds on the number | ||
| 116 | of bird species retained by forest fragments in several localities | 130 | of bird species retained by forest fragments in several localities | ||
| 117 | across Europe. Location: We studied bird assemblages in fourteen | 131 | across Europe. Location: We studied bird assemblages in fourteen | ||
| 118 | forest archipelagos embedded in agricultural matrices from southern | 132 | forest archipelagos embedded in agricultural matrices from southern | ||
| 119 | Norway to central Spain. Tree composition varied from oak and beech | 133 | Norway to central Spain. Tree composition varied from oak and beech | ||
| 120 | forests of the northern localities to oak and pine xerophitic | 134 | forests of the northern localities to oak and pine xerophitic | ||
| 121 | woodlands of the southern ones. The number of fragments in each forest | 135 | woodlands of the southern ones. The number of fragments in each forest | ||
| 122 | archipelago ranged from eighteen to 211. Methods: We used the Gleason | 136 | archipelago ranged from eighteen to 211. Methods: We used the Gleason | ||
| 123 | equation (s=a+z log A; where s and A are, respectively, the species | 137 | equation (s=a+z log A; where s and A are, respectively, the species | ||
| 124 | richness and size of forest fragments and z the rate of species loss) | 138 | richness and size of forest fragments and z the rate of species loss) | ||
| 125 | to estimate the species richness for 1- and 15-ha fragments in each | 139 | to estimate the species richness for 1- and 15-ha fragments in each | ||
| 126 | archipelago. The regional richness of forest birds was estimated by | 140 | archipelago. The regional richness of forest birds was estimated by | ||
| 127 | modelling the geographical distribution of species richness in the | 141 | modelling the geographical distribution of species richness in the | ||
| 128 | European atlas of breeding birds. Results: The latitudinal | 142 | European atlas of breeding birds. Results: The latitudinal | ||
| 129 | distribution of regional richness displayed a convex form, with the | 143 | distribution of regional richness displayed a convex form, with the | ||
| 130 | highest values being in central Europe. Along this gradient, the | 144 | highest values being in central Europe. Along this gradient, the | ||
| 131 | number of species retained by fragments and the rate of species loss | 145 | number of species retained by fragments and the rate of species loss | ||
| 132 | was positively related to regional richness. In addition, the | 146 | was positively related to regional richness. In addition, the | ||
| 133 | percentage of the regional pool of species sampled by fragments | 147 | percentage of the regional pool of species sampled by fragments | ||
| 134 | decreased in the southern localities. Main conclusions: Relationships | 148 | decreased in the southern localities. Main conclusions: Relationships | ||
| 135 | between regional richness of forest birds and richness in fragments | 149 | between regional richness of forest birds and richness in fragments | ||
| 136 | seem to explain why fragments in central Europe shelter more species | 150 | seem to explain why fragments in central Europe shelter more species | ||
| 137 | than their southern counterparts. The decreased ability of southern | 151 | than their southern counterparts. The decreased ability of southern | ||
| 138 | forest fragments to sample the regional richness of forest birds, | 152 | forest fragments to sample the regional richness of forest birds, | ||
| 139 | could be explained as an effect of the low abundance of many species | 153 | could be explained as an effect of the low abundance of many species | ||
| 140 | in the Mediterranean, which could depress their ability to prevent | 154 | in the Mediterranean, which could depress their ability to prevent | ||
| 141 | extinction in fragments by a rescue effect. Alternatively, high beta | 155 | extinction in fragments by a rescue effect. Alternatively, high beta | ||
| 142 | diversity in the Mediterranean could produce undersampling by | 156 | diversity in the Mediterranean could produce undersampling by | ||
| 143 | fragments of the regional pool of species. These regional differences | 157 | fragments of the regional pool of species. These regional differences | ||
| 144 | in the response of bird assemblages to forest fragmentation are used | 158 | in the response of bird assemblages to forest fragmentation are used | ||
| 145 | to discuss the usefulness of large-scale, biogeographical approaches | 159 | to discuss the usefulness of large-scale, biogeographical approaches | ||
| 146 | in the design of conservation guidelines.", | 160 | in the design of conservation guidelines.", | ||
| 147 | "es": "Aim: In this paper, we adopted a large-scale approach to | 161 | "es": "Aim: In this paper, we adopted a large-scale approach to | ||
| 148 | evaluate the effect of regional richness of forest birds on the number | 162 | evaluate the effect of regional richness of forest birds on the number | ||
| 149 | of bird species retained by forest fragments in several localities | 163 | of bird species retained by forest fragments in several localities | ||
| 150 | across Europe. Location: We studied bird assemblages in fourteen | 164 | across Europe. Location: We studied bird assemblages in fourteen | ||
| 151 | forest archipelagos embedded in agricultural matrices from southern | 165 | forest archipelagos embedded in agricultural matrices from southern | ||
| 152 | Norway to central Spain. Tree composition varied from oak and beech | 166 | Norway to central Spain. Tree composition varied from oak and beech | ||
| 153 | forests of the northern localities to oak and pine xerophitic | 167 | forests of the northern localities to oak and pine xerophitic | ||
| 154 | woodlands of the southern ones. The number of fragments in each forest | 168 | woodlands of the southern ones. The number of fragments in each forest | ||
| 155 | archipelago ranged from eighteen to 211. Methods: We used the Gleason | 169 | archipelago ranged from eighteen to 211. Methods: We used the Gleason | ||
| 156 | equation (s=a+z log A; where s and A are, respectively, the species | 170 | equation (s=a+z log A; where s and A are, respectively, the species | ||
| 157 | richness and size of forest fragments and z the rate of species loss) | 171 | richness and size of forest fragments and z the rate of species loss) | ||
| 158 | to estimate the species richness for 1- and 15-ha fragments in each | 172 | to estimate the species richness for 1- and 15-ha fragments in each | ||
| 159 | archipelago. The regional richness of forest birds was estimated by | 173 | archipelago. The regional richness of forest birds was estimated by | ||
| 160 | modelling the geographical distribution of species richness in the | 174 | modelling the geographical distribution of species richness in the | ||
| 161 | European atlas of breeding birds. Results: The latitudinal | 175 | European atlas of breeding birds. Results: The latitudinal | ||
| 162 | distribution of regional richness displayed a convex form, with the | 176 | distribution of regional richness displayed a convex form, with the | ||
| 163 | highest values being in central Europe. Along this gradient, the | 177 | highest values being in central Europe. Along this gradient, the | ||
| 164 | number of species retained by fragments and the rate of species loss | 178 | number of species retained by fragments and the rate of species loss | ||
| 165 | was positively related to regional richness. In addition, the | 179 | was positively related to regional richness. In addition, the | ||
| 166 | percentage of the regional pool of species sampled by fragments | 180 | percentage of the regional pool of species sampled by fragments | ||
| 167 | decreased in the southern localities. Main conclusions: Relationships | 181 | decreased in the southern localities. Main conclusions: Relationships | ||
| 168 | between regional richness of forest birds and richness in fragments | 182 | between regional richness of forest birds and richness in fragments | ||
| 169 | seem to explain why fragments in central Europe shelter more species | 183 | seem to explain why fragments in central Europe shelter more species | ||
| 170 | than their southern counterparts. The decreased ability of southern | 184 | than their southern counterparts. The decreased ability of southern | ||
| 171 | forest fragments to sample the regional richness of forest birds, | 185 | forest fragments to sample the regional richness of forest birds, | ||
| 172 | could be explained as an effect of the low abundance of many species | 186 | could be explained as an effect of the low abundance of many species | ||
| 173 | in the Mediterranean, which could depress their ability to prevent | 187 | in the Mediterranean, which could depress their ability to prevent | ||
| 174 | extinction in fragments by a rescue effect. Alternatively, high beta | 188 | extinction in fragments by a rescue effect. Alternatively, high beta | ||
| 175 | diversity in the Mediterranean could produce undersampling by | 189 | diversity in the Mediterranean could produce undersampling by | ||
| 176 | fragments of the regional pool of species. These regional differences | 190 | fragments of the regional pool of species. These regional differences | ||
| 177 | in the response of bird assemblages to forest fragmentation are used | 191 | in the response of bird assemblages to forest fragmentation are used | ||
| 178 | to discuss the usefulness of large-scale, biogeographical approaches | 192 | to discuss the usefulness of large-scale, biogeographical approaches | ||
| 179 | in the design of conservation guidelines.\n Palabras clave: Arable | 193 | in the design of conservation guidelines.\n Palabras clave: Arable | ||
| 180 | land, Biodiversity, Bird, Forest, Fragmentation, Mosaic" | 194 | land, Biodiversity, Bird, Forest, Fragmentation, Mosaic" | ||
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