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En el instante 25 de junio de 2026, 12:36:16 UTC,
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Modificado el valor del campo
modified
a2026-06-25
en Bird conservation in fragmented mediterranean forests of Spain: effects of geographical location, habitat and landscape degradation. -
Modificado el valor del campo
modified
del recurso Acceso al recurso a2026-06-25
(anteriormente2026-06-23
) en Bird conservation in fragmented mediterranean forests of Spain: effects of geographical location, habitat and landscape degradation.
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| 79 | "notes": "The effects of habitat fragmentation on forest bird | 93 | "notes": "The effects of habitat fragmentation on forest bird | ||
| 80 | assemblages were analysed in 214 holm oak (Quercus ilex) remnants | 94 | assemblages were analysed in 214 holm oak (Quercus ilex) remnants | ||
| 81 | spread across the northern and southern plateaux of central Spain. | 95 | spread across the northern and southern plateaux of central Spain. | ||
| 82 | Bird richness was highly dependent on fragment area for all species | 96 | Bird richness was highly dependent on fragment area for all species | ||
| 83 | regardless of isolation, and barely affected by habitat traits. | 97 | regardless of isolation, and barely affected by habitat traits. | ||
| 84 | Geographical location was associated with high differences in richness | 98 | Geographical location was associated with high differences in richness | ||
| 85 | of bird assemblages, which included 17 species exclusive to northern | 99 | of bird assemblages, which included 17 species exclusive to northern | ||
| 86 | remnants and one exclusive to southern remnants. This supports the | 100 | remnants and one exclusive to southern remnants. This supports the | ||
| 87 | hypothesis that habitat suitability deteriorates sharply from north to | 101 | hypothesis that habitat suitability deteriorates sharply from north to | ||
| 88 | south for forest birds in Spain. The species-area relationships of | 102 | south for forest birds in Spain. The species-area relationships of | ||
| 89 | bird assemblages sampled in fragmented forests along a broad | 103 | bird assemblages sampled in fragmented forests along a broad | ||
| 90 | continental gradient (from Norway to southern Spain) showed that true | 104 | continental gradient (from Norway to southern Spain) showed that true | ||
| 91 | forest birds only nest in woodlands >100 ha in southern Spain, whereas | 105 | forest birds only nest in woodlands >100 ha in southern Spain, whereas | ||
| 92 | the full complement of forest species occurs in much smaller fragments | 106 | the full complement of forest species occurs in much smaller fragments | ||
| 93 | in central-western Europe. Loss of species that are particularly | 107 | in central-western Europe. Loss of species that are particularly | ||
| 94 | sensitive to habitat fragmentation accounts for these differences | 108 | sensitive to habitat fragmentation accounts for these differences | ||
| 95 | between dry Spanish and mesic European woodlands. These results are | 109 | between dry Spanish and mesic European woodlands. These results are | ||
| 96 | explained by the low habitat suitability of Spanish woodlands, | 110 | explained by the low habitat suitability of Spanish woodlands, | ||
| 97 | associated with the restrictive conditions for plant regeneration in | 111 | associated with the restrictive conditions for plant regeneration in | ||
| 98 | the Mediterranean climate and long-standing human usage. There is, | 112 | the Mediterranean climate and long-standing human usage. There is, | ||
| 99 | therefore, a particular need to develop management strategies that | 113 | therefore, a particular need to develop management strategies that | ||
| 100 | conserve birds, and probably other forest organisms, in Mediterranean | 114 | conserve birds, and probably other forest organisms, in Mediterranean | ||
| 101 | regions by preventing habitat deterioration and decreases in fragment | 115 | regions by preventing habitat deterioration and decreases in fragment | ||
| 102 | size, and by conserving all woods >100 ha.\n Palabras clave: Bird, | 116 | size, and by conserving all woods >100 ha.\n Palabras clave: Bird, | ||
| 103 | Forest, Habitat fragmentation", | 117 | Forest, Habitat fragmentation", | ||
| 104 | "notes_translated": { | 118 | "notes_translated": { | ||
| 105 | "en": "The effects of habitat fragmentation on forest bird | 119 | "en": "The effects of habitat fragmentation on forest bird | ||
| 106 | assemblages were analysed in 214 holm oak (Quercus ilex) remnants | 120 | assemblages were analysed in 214 holm oak (Quercus ilex) remnants | ||
| 107 | spread across the northern and southern plateaux of central Spain. | 121 | spread across the northern and southern plateaux of central Spain. | ||
| 108 | Bird richness was highly dependent on fragment area for all species | 122 | Bird richness was highly dependent on fragment area for all species | ||
| 109 | regardless of isolation, and barely affected by habitat traits. | 123 | regardless of isolation, and barely affected by habitat traits. | ||
| 110 | Geographical location was associated with high differences in richness | 124 | Geographical location was associated with high differences in richness | ||
| 111 | of bird assemblages, which included 17 species exclusive to northern | 125 | of bird assemblages, which included 17 species exclusive to northern | ||
| 112 | remnants and one exclusive to southern remnants. This supports the | 126 | remnants and one exclusive to southern remnants. This supports the | ||
| 113 | hypothesis that habitat suitability deteriorates sharply from north to | 127 | hypothesis that habitat suitability deteriorates sharply from north to | ||
| 114 | south for forest birds in Spain. The species-area relationships of | 128 | south for forest birds in Spain. The species-area relationships of | ||
| 115 | bird assemblages sampled in fragmented forests along a broad | 129 | bird assemblages sampled in fragmented forests along a broad | ||
| 116 | continental gradient (from Norway to southern Spain) showed that true | 130 | continental gradient (from Norway to southern Spain) showed that true | ||
| 117 | forest birds only nest in woodlands >100 ha in southern Spain, whereas | 131 | forest birds only nest in woodlands >100 ha in southern Spain, whereas | ||
| 118 | the full complement of forest species occurs in much smaller fragments | 132 | the full complement of forest species occurs in much smaller fragments | ||
| 119 | in central-western Europe. Loss of species that are particularly | 133 | in central-western Europe. Loss of species that are particularly | ||
| 120 | sensitive to habitat fragmentation accounts for these differences | 134 | sensitive to habitat fragmentation accounts for these differences | ||
| 121 | between dry Spanish and mesic European woodlands. These results are | 135 | between dry Spanish and mesic European woodlands. These results are | ||
| 122 | explained by the low habitat suitability of Spanish woodlands, | 136 | explained by the low habitat suitability of Spanish woodlands, | ||
| 123 | associated with the restrictive conditions for plant regeneration in | 137 | associated with the restrictive conditions for plant regeneration in | ||
| 124 | the Mediterranean climate and long-standing human usage. There is, | 138 | the Mediterranean climate and long-standing human usage. There is, | ||
| 125 | therefore, a particular need to develop management strategies that | 139 | therefore, a particular need to develop management strategies that | ||
| 126 | conserve birds, and probably other forest organisms, in Mediterranean | 140 | conserve birds, and probably other forest organisms, in Mediterranean | ||
| 127 | regions by preventing habitat deterioration and decreases in fragment | 141 | regions by preventing habitat deterioration and decreases in fragment | ||
| 128 | size, and by conserving all woods >100 ha.", | 142 | size, and by conserving all woods >100 ha.", | ||
| 129 | "es": "The effects of habitat fragmentation on forest bird | 143 | "es": "The effects of habitat fragmentation on forest bird | ||
| 130 | assemblages were analysed in 214 holm oak (Quercus ilex) remnants | 144 | assemblages were analysed in 214 holm oak (Quercus ilex) remnants | ||
| 131 | spread across the northern and southern plateaux of central Spain. | 145 | spread across the northern and southern plateaux of central Spain. | ||
| 132 | Bird richness was highly dependent on fragment area for all species | 146 | Bird richness was highly dependent on fragment area for all species | ||
| 133 | regardless of isolation, and barely affected by habitat traits. | 147 | regardless of isolation, and barely affected by habitat traits. | ||
| 134 | Geographical location was associated with high differences in richness | 148 | Geographical location was associated with high differences in richness | ||
| 135 | of bird assemblages, which included 17 species exclusive to northern | 149 | of bird assemblages, which included 17 species exclusive to northern | ||
| 136 | remnants and one exclusive to southern remnants. This supports the | 150 | remnants and one exclusive to southern remnants. This supports the | ||
| 137 | hypothesis that habitat suitability deteriorates sharply from north to | 151 | hypothesis that habitat suitability deteriorates sharply from north to | ||
| 138 | south for forest birds in Spain. The species-area relationships of | 152 | south for forest birds in Spain. The species-area relationships of | ||
| 139 | bird assemblages sampled in fragmented forests along a broad | 153 | bird assemblages sampled in fragmented forests along a broad | ||
| 140 | continental gradient (from Norway to southern Spain) showed that true | 154 | continental gradient (from Norway to southern Spain) showed that true | ||
| 141 | forest birds only nest in woodlands >100 ha in southern Spain, whereas | 155 | forest birds only nest in woodlands >100 ha in southern Spain, whereas | ||
| 142 | the full complement of forest species occurs in much smaller fragments | 156 | the full complement of forest species occurs in much smaller fragments | ||
| 143 | in central-western Europe. Loss of species that are particularly | 157 | in central-western Europe. Loss of species that are particularly | ||
| 144 | sensitive to habitat fragmentation accounts for these differences | 158 | sensitive to habitat fragmentation accounts for these differences | ||
| 145 | between dry Spanish and mesic European woodlands. These results are | 159 | between dry Spanish and mesic European woodlands. These results are | ||
| 146 | explained by the low habitat suitability of Spanish woodlands, | 160 | explained by the low habitat suitability of Spanish woodlands, | ||
| 147 | associated with the restrictive conditions for plant regeneration in | 161 | associated with the restrictive conditions for plant regeneration in | ||
| 148 | the Mediterranean climate and long-standing human usage. There is, | 162 | the Mediterranean climate and long-standing human usage. There is, | ||
| 149 | therefore, a particular need to develop management strategies that | 163 | therefore, a particular need to develop management strategies that | ||
| 150 | conserve birds, and probably other forest organisms, in Mediterranean | 164 | conserve birds, and probably other forest organisms, in Mediterranean | ||
| 151 | regions by preventing habitat deterioration and decreases in fragment | 165 | regions by preventing habitat deterioration and decreases in fragment | ||
| 152 | size, and by conserving all woods >100 ha.\n Palabras clave: Bird, | 166 | size, and by conserving all woods >100 ha.\n Palabras clave: Bird, | ||
| 153 | Forest, Habitat fragmentation" | 167 | Forest, Habitat fragmentation" | ||
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