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En el instante 23 de junio de 2026, 15:50:50 UTC,
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Modificado el valor del campo
spatial_coverage
a[{'bbox': '{"type": "Polygon", "coordinates": [[[-18.16, 27.64], [4.32, 27.64], [4.32, 43.79], [-18.16, 43.79], [-18.16, 27.64]]]}', 'centroid': '{"type": "Point", "coordinates": [-6.92, 35.715]}', 'text': 'España', 'uri': 'http://datos.gob.es/recurso/sector-publico/territorio/Pais/España'}]
en Effects of woodland islets introduced in a Mediterranean agricultural landscape on local bird communities.
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| 77 | "notes": "This study assesses whether the afforestation approach | 77 | "notes": "This study assesses whether the afforestation approach | ||
| 78 | consisting in the introduction of woodland islets in | 78 | consisting in the introduction of woodland islets in | ||
| 79 | \u201cagricultural seas\u201d can reconcile the restoration of woody | 79 | \u201cagricultural seas\u201d can reconcile the restoration of woody | ||
| 80 | vegetation and the persistence of open-habitat bird populations, | 80 | vegetation and the persistence of open-habitat bird populations, | ||
| 81 | providing further opportunities for other forest species to enrich | 81 | providing further opportunities for other forest species to enrich | ||
| 82 | bird diversity at the landscape level. We compared the species | 82 | bird diversity at the landscape level. We compared the species | ||
| 83 | richness and abundance of bird communities in a field with 16 | 83 | richness and abundance of bird communities in a field with 16 | ||
| 84 | introduced woodland islets and in a nearby abandoned field located in | 84 | introduced woodland islets and in a nearby abandoned field located in | ||
| 85 | central Spain during spring and winter time. The woodland islets | 85 | central Spain during spring and winter time. The woodland islets | ||
| 86 | presented higher accumulated species richness as well as a higher | 86 | presented higher accumulated species richness as well as a higher | ||
| 87 | probability of finding new species if sampling effort were increased | 87 | probability of finding new species if sampling effort were increased | ||
| 88 | only in winter time. These trends were the opposite during spring | 88 | only in winter time. These trends were the opposite during spring | ||
| 89 | time. Mean species richness and mean bird abundance were lower at the | 89 | time. Mean species richness and mean bird abundance were lower at the | ||
| 90 | woodland islets than at the abandoned field in both seasons. We found | 90 | woodland islets than at the abandoned field in both seasons. We found | ||
| 91 | a higher abundance of open-habitat specialist species in the abandoned | 91 | a higher abundance of open-habitat specialist species in the abandoned | ||
| 92 | field. Woodland islets favoured the wintering of chiffchaff | 92 | field. Woodland islets favoured the wintering of chiffchaff | ||
| 93 | Phylloscopus collybita. We did not find any effects on the only forest | 93 | Phylloscopus collybita. We did not find any effects on the only forest | ||
| 94 | specialist species (blue tit Parus caeruleus) in spring. Bird richness | 94 | specialist species (blue tit Parus caeruleus) in spring. Bird richness | ||
| 95 | and abundance were higher in edge islets than in inner islets. The | 95 | and abundance were higher in edge islets than in inner islets. The | ||
| 96 | introduction of larger and mixed plantations connected by hedgerows | 96 | introduction of larger and mixed plantations connected by hedgerows | ||
| 97 | and a management that favoured the development of big trees, a lower | 97 | and a management that favoured the development of big trees, a lower | ||
| 98 | tree density and a diverse shrub layer could promote bird diversity, | 98 | tree density and a diverse shrub layer could promote bird diversity, | ||
| 99 | allowing forest specialists and open-habitat species to coexist at the | 99 | allowing forest specialists and open-habitat species to coexist at the | ||
| 100 | landscape scale.", | 100 | landscape scale.", | ||
| 101 | "notes_translated": { | 101 | "notes_translated": { | ||
| 102 | "en": "This study assesses whether the afforestation approach | 102 | "en": "This study assesses whether the afforestation approach | ||
| 103 | consisting in the introduction of woodland islets in | 103 | consisting in the introduction of woodland islets in | ||
| 104 | \u201cagricultural seas\u201d can reconcile the restoration of woody | 104 | \u201cagricultural seas\u201d can reconcile the restoration of woody | ||
| 105 | vegetation and the persistence of open-habitat bird populations, | 105 | vegetation and the persistence of open-habitat bird populations, | ||
| 106 | providing further opportunities for other forest species to enrich | 106 | providing further opportunities for other forest species to enrich | ||
| 107 | bird diversity at the landscape level. We compared the species | 107 | bird diversity at the landscape level. We compared the species | ||
| 108 | richness and abundance of bird communities in a field with 16 | 108 | richness and abundance of bird communities in a field with 16 | ||
| 109 | introduced woodland islets and in a nearby abandoned field located in | 109 | introduced woodland islets and in a nearby abandoned field located in | ||
| 110 | central Spain during spring and winter time. The woodland islets | 110 | central Spain during spring and winter time. The woodland islets | ||
| 111 | presented higher accumulated species richness as well as a higher | 111 | presented higher accumulated species richness as well as a higher | ||
| 112 | probability of finding new species if sampling effort were increased | 112 | probability of finding new species if sampling effort were increased | ||
| 113 | only in winter time. These trends were the opposite during spring | 113 | only in winter time. These trends were the opposite during spring | ||
| 114 | time. Mean species richness and mean bird abundance were lower at the | 114 | time. Mean species richness and mean bird abundance were lower at the | ||
| 115 | woodland islets than at the abandoned field in both seasons. We found | 115 | woodland islets than at the abandoned field in both seasons. We found | ||
| 116 | a higher abundance of open-habitat specialist species in the abandoned | 116 | a higher abundance of open-habitat specialist species in the abandoned | ||
| 117 | field. Woodland islets favoured the wintering of | 117 | field. Woodland islets favoured the wintering of | ||
| 118 | chiffchaff\u00a0Phylloscopus collybita. We did not find any effects on | 118 | chiffchaff\u00a0Phylloscopus collybita. We did not find any effects on | ||
| 119 | the only forest specialist species (blue tit\u00a0Parus caeruleus) in | 119 | the only forest specialist species (blue tit\u00a0Parus caeruleus) in | ||
| 120 | spring. Bird richness and abundance were higher in edge islets than in | 120 | spring. Bird richness and abundance were higher in edge islets than in | ||
| 121 | inner islets. The introduction of larger and mixed plantations | 121 | inner islets. The introduction of larger and mixed plantations | ||
| 122 | connected by hedgerows and a management that favoured the development | 122 | connected by hedgerows and a management that favoured the development | ||
| 123 | of big trees, a lower tree density and a diverse shrub layer could | 123 | of big trees, a lower tree density and a diverse shrub layer could | ||
| 124 | promote bird diversity, allowing forest specialists and open-habitat | 124 | promote bird diversity, allowing forest specialists and open-habitat | ||
| 125 | species to coexist at the landscape scale.", | 125 | species to coexist at the landscape scale.", | ||
| 126 | "es": "This study assesses whether the afforestation approach | 126 | "es": "This study assesses whether the afforestation approach | ||
| 127 | consisting in the introduction of woodland islets in | 127 | consisting in the introduction of woodland islets in | ||
| 128 | \u201cagricultural seas\u201d can reconcile the restoration of woody | 128 | \u201cagricultural seas\u201d can reconcile the restoration of woody | ||
| 129 | vegetation and the persistence of open-habitat bird populations, | 129 | vegetation and the persistence of open-habitat bird populations, | ||
| 130 | providing further opportunities for other forest species to enrich | 130 | providing further opportunities for other forest species to enrich | ||
| 131 | bird diversity at the landscape level. We compared the species | 131 | bird diversity at the landscape level. We compared the species | ||
| 132 | richness and abundance of bird communities in a field with 16 | 132 | richness and abundance of bird communities in a field with 16 | ||
| 133 | introduced woodland islets and in a nearby abandoned field located in | 133 | introduced woodland islets and in a nearby abandoned field located in | ||
| 134 | central Spain during spring and winter time. The woodland islets | 134 | central Spain during spring and winter time. The woodland islets | ||
| 135 | presented higher accumulated species richness as well as a higher | 135 | presented higher accumulated species richness as well as a higher | ||
| 136 | probability of finding new species if sampling effort were increased | 136 | probability of finding new species if sampling effort were increased | ||
| 137 | only in winter time. These trends were the opposite during spring | 137 | only in winter time. These trends were the opposite during spring | ||
| 138 | time. Mean species richness and mean bird abundance were lower at the | 138 | time. Mean species richness and mean bird abundance were lower at the | ||
| 139 | woodland islets than at the abandoned field in both seasons. We found | 139 | woodland islets than at the abandoned field in both seasons. We found | ||
| 140 | a higher abundance of open-habitat specialist species in the abandoned | 140 | a higher abundance of open-habitat specialist species in the abandoned | ||
| 141 | field. Woodland islets favoured the wintering of chiffchaff | 141 | field. Woodland islets favoured the wintering of chiffchaff | ||
| 142 | Phylloscopus collybita. We did not find any effects on the only forest | 142 | Phylloscopus collybita. We did not find any effects on the only forest | ||
| 143 | specialist species (blue tit Parus caeruleus) in spring. Bird richness | 143 | specialist species (blue tit Parus caeruleus) in spring. Bird richness | ||
| 144 | and abundance were higher in edge islets than in inner islets. The | 144 | and abundance were higher in edge islets than in inner islets. The | ||
| 145 | introduction of larger and mixed plantations connected by hedgerows | 145 | introduction of larger and mixed plantations connected by hedgerows | ||
| 146 | and a management that favoured the development of big trees, a lower | 146 | and a management that favoured the development of big trees, a lower | ||
| 147 | tree density and a diverse shrub layer could promote bird diversity, | 147 | tree density and a diverse shrub layer could promote bird diversity, | ||
| 148 | allowing forest specialists and open-habitat species to coexist at the | 148 | allowing forest specialists and open-habitat species to coexist at the | ||
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