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En el instante 23 de junio de 2026, 16:14:04 UTC,
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Modificado el valor del campo
spatial_coverage
a[{'bbox': '{"type": "Polygon", "coordinates": [[[-2.34, 37.38], [-0.69, 37.38], [-0.69, 38.76], [-2.34, 38.76], [-2.34, 37.38]]]}', 'centroid': '{"type": "Point", "coordinates": [-1.515, 38.07]}', 'text': 'Región de Murcia', 'uri': 'http://datos.gob.es/recurso/sector-publico/territorio/Autonomia/Region-Murcia'}]
en Terrestrial birds as indicators of agricultural-induced changes and associated loss in conservation value of Mediterranean wetlands
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| 93 | "notes": "During the last decades, agricultural intensification has | 93 | "notes": "During the last decades, agricultural intensification has | ||
| 94 | modified the hydrology of Mediterranean wetlands, as has occurred in | 94 | modified the hydrology of Mediterranean wetlands, as has occurred in | ||
| 95 | the Mar Menor coastal lagoon (SE Spain). Salt-steppe dominated | 95 | the Mar Menor coastal lagoon (SE Spain). Salt-steppe dominated | ||
| 96 | wetlands, characteristic of transitional areas surrounding this lagoon | 96 | wetlands, characteristic of transitional areas surrounding this lagoon | ||
| 97 | and rich in biodiversity values, are threatened by changes in their | 97 | and rich in biodiversity values, are threatened by changes in their | ||
| 98 | water regime originated by land-use changes in the watershed. | 98 | water regime originated by land-use changes in the watershed. | ||
| 99 | Traditional dryland cultures have also been replaced by irrigated | 99 | Traditional dryland cultures have also been replaced by irrigated | ||
| 100 | ones. We assess the direct and indirect changes induced by agriculture | 100 | ones. We assess the direct and indirect changes induced by agriculture | ||
| 101 | on a terrestrial vertebrate community (steppe birds) especially | 101 | on a terrestrial vertebrate community (steppe birds) especially | ||
| 102 | sensitive to these ecosystem changes. This is made on the basis of | 102 | sensitive to these ecosystem changes. This is made on the basis of | ||
| 103 | several surveys of terrestrial birds (excluding aerial feeders and | 103 | several surveys of terrestrial birds (excluding aerial feeders and | ||
| 104 | raptors) carried out between 1984 and 2008 in a representative wetland | 104 | raptors) carried out between 1984 and 2008 in a representative wetland | ||
| 105 | of the lagoon's continental margin (Marina del Carmoli). The changes | 105 | of the lagoon's continental margin (Marina del Carmoli). The changes | ||
| 106 | in this bird assemblage reflect the hydrological modifications induced | 106 | in this bird assemblage reflect the hydrological modifications induced | ||
| 107 | by agriculture at the watershed scale, which have significant effects | 107 | by agriculture at the watershed scale, which have significant effects | ||
| 108 | on the relative representation of wetland habitats. Bird metrics and | 108 | on the relative representation of wetland habitats. Bird metrics and | ||
| 109 | indices (species abundance, taxonomic composition, conservation value) | 109 | indices (species abundance, taxonomic composition, conservation value) | ||
| 110 | describe these community changes as the combination of early declines | 110 | describe these community changes as the combination of early declines | ||
| 111 | in some species and families, and transient or late increases in | 111 | in some species and families, and transient or late increases in | ||
| 112 | other. In the long term, the family Alaudidae (and particularly | 112 | other. In the long term, the family Alaudidae (and particularly | ||
| 113 | species like Melanocorypha calandra) have lost importance to the | 113 | species like Melanocorypha calandra) have lost importance to the | ||
| 114 | benefit of Turdidae and Fringillidae. The area of salt-steppe explains | 114 | benefit of Turdidae and Fringillidae. The area of salt-steppe explains | ||
| 115 | a large part of the variation in the abundance of Alaudidae, while | 115 | a large part of the variation in the abundance of Alaudidae, while | ||
| 116 | most variation of Turdidae and Fringillidae respond to the area of | 116 | most variation of Turdidae and Fringillidae respond to the area of | ||
| 117 | saltmarsh. Some Alaudidae seem to take advantage of the intermediate | 117 | saltmarsh. Some Alaudidae seem to take advantage of the intermediate | ||
| 118 | stages of saltmarsh expansion (Calandrella rufescens), or from the | 118 | stages of saltmarsh expansion (Calandrella rufescens), or from the | ||
| 119 | marginal irrigated crops fringing the wetland (Calandrella | 119 | marginal irrigated crops fringing the wetland (Calandrella | ||
| 120 | brachydactyla) that could compensate the loss of original agricultural | 120 | brachydactyla) that could compensate the loss of original agricultural | ||
| 121 | habitats. Habitat changes in the wetland have occurred in three | 121 | habitats. Habitat changes in the wetland have occurred in three | ||
| 122 | differentiated stages, and modify the steppe bird community towards a | 122 | differentiated stages, and modify the steppe bird community towards a | ||
| 123 | more heterogeneous assemblage including scrubland and palustrine | 123 | more heterogeneous assemblage including scrubland and palustrine | ||
| 124 | species. Among three indices of ornithological value, only that based | 124 | species. Among three indices of ornithological value, only that based | ||
| 125 | on the EU Bird's Directive Annex I species was negatively affected, | 125 | on the EU Bird's Directive Annex I species was negatively affected, | ||
| 126 | but since the wetland has been designated a Specially Protected Area | 126 | but since the wetland has been designated a Specially Protected Area | ||
| 127 | under this regulation, this represents a management failure. There | 127 | under this regulation, this represents a management failure. There | ||
| 128 | exists some chance, however, to manage peripheral cropland in favour | 128 | exists some chance, however, to manage peripheral cropland in favour | ||
| 129 | of biodiversity. The importance of monitoring in conservation | 129 | of biodiversity. The importance of monitoring in conservation | ||
| 130 | evaluation and management is also stressed, since the terrestrial bird | 130 | evaluation and management is also stressed, since the terrestrial bird | ||
| 131 | community of this wetland has not been regularly surveyed. In fact, | 131 | community of this wetland has not been regularly surveyed. In fact, | ||
| 132 | its evaluation against the Bird's Directive criteria was made in a | 132 | its evaluation against the Bird's Directive criteria was made in a | ||
| 133 | period of quick departure from the original, good ecological state of | 133 | period of quick departure from the original, good ecological state of | ||
| 134 | the wetland. (C) 2009 Elsevier Ltd. All rights reserved.", | 134 | the wetland. (C) 2009 Elsevier Ltd. All rights reserved.", | ||
| 135 | "notes_translated": { | 135 | "notes_translated": { | ||
| 136 | "es": "During the last decades, agricultural intensification has | 136 | "es": "During the last decades, agricultural intensification has | ||
| 137 | modified the hydrology of Mediterranean wetlands, as has occurred in | 137 | modified the hydrology of Mediterranean wetlands, as has occurred in | ||
| 138 | the Mar Menor coastal lagoon (SE Spain). Salt-steppe dominated | 138 | the Mar Menor coastal lagoon (SE Spain). Salt-steppe dominated | ||
| 139 | wetlands, characteristic of transitional areas surrounding this lagoon | 139 | wetlands, characteristic of transitional areas surrounding this lagoon | ||
| 140 | and rich in biodiversity values, are threatened by changes in their | 140 | and rich in biodiversity values, are threatened by changes in their | ||
| 141 | water regime originated by land-use changes in the watershed. | 141 | water regime originated by land-use changes in the watershed. | ||
| 142 | Traditional dryland cultures have also been replaced by irrigated | 142 | Traditional dryland cultures have also been replaced by irrigated | ||
| 143 | ones. We assess the direct and indirect changes induced by agriculture | 143 | ones. We assess the direct and indirect changes induced by agriculture | ||
| 144 | on a terrestrial vertebrate community (steppe birds) especially | 144 | on a terrestrial vertebrate community (steppe birds) especially | ||
| 145 | sensitive to these ecosystem changes. This is made on the basis of | 145 | sensitive to these ecosystem changes. This is made on the basis of | ||
| 146 | several surveys of terrestrial birds (excluding aerial feeders and | 146 | several surveys of terrestrial birds (excluding aerial feeders and | ||
| 147 | raptors) carried out between 1984 and 2008 in a representative wetland | 147 | raptors) carried out between 1984 and 2008 in a representative wetland | ||
| 148 | of the lagoon's continental margin (Marina del Carmoli). The changes | 148 | of the lagoon's continental margin (Marina del Carmoli). The changes | ||
| 149 | in this bird assemblage reflect the hydrological modifications induced | 149 | in this bird assemblage reflect the hydrological modifications induced | ||
| 150 | by agriculture at the watershed scale, which have significant effects | 150 | by agriculture at the watershed scale, which have significant effects | ||
| 151 | on the relative representation of wetland habitats. Bird metrics and | 151 | on the relative representation of wetland habitats. Bird metrics and | ||
| 152 | indices (species abundance, taxonomic composition, conservation value) | 152 | indices (species abundance, taxonomic composition, conservation value) | ||
| 153 | describe these community changes as the combination of early declines | 153 | describe these community changes as the combination of early declines | ||
| 154 | in some species and families, and transient or late increases in | 154 | in some species and families, and transient or late increases in | ||
| 155 | other. In the long term, the family Alaudidae (and particularly | 155 | other. In the long term, the family Alaudidae (and particularly | ||
| 156 | species like Melanocorypha calandra) have lost importance to the | 156 | species like Melanocorypha calandra) have lost importance to the | ||
| 157 | benefit of Turdidae and Fringillidae. The area of salt-steppe explains | 157 | benefit of Turdidae and Fringillidae. The area of salt-steppe explains | ||
| 158 | a large part of the variation in the abundance of Alaudidae, while | 158 | a large part of the variation in the abundance of Alaudidae, while | ||
| 159 | most variation of Turdidae and Fringillidae respond to the area of | 159 | most variation of Turdidae and Fringillidae respond to the area of | ||
| 160 | saltmarsh. Some Alaudidae seem to take advantage of the intermediate | 160 | saltmarsh. Some Alaudidae seem to take advantage of the intermediate | ||
| 161 | stages of saltmarsh expansion (Calandrella rufescens), or from the | 161 | stages of saltmarsh expansion (Calandrella rufescens), or from the | ||
| 162 | marginal irrigated crops fringing the wetland (Calandrella | 162 | marginal irrigated crops fringing the wetland (Calandrella | ||
| 163 | brachydactyla) that could compensate the loss of original agricultural | 163 | brachydactyla) that could compensate the loss of original agricultural | ||
| 164 | habitats. Habitat changes in the wetland have occurred in three | 164 | habitats. Habitat changes in the wetland have occurred in three | ||
| 165 | differentiated stages, and modify the steppe bird community towards a | 165 | differentiated stages, and modify the steppe bird community towards a | ||
| 166 | more heterogeneous assemblage including scrubland and palustrine | 166 | more heterogeneous assemblage including scrubland and palustrine | ||
| 167 | species. Among three indices of ornithological value, only that based | 167 | species. Among three indices of ornithological value, only that based | ||
| 168 | on the EU Bird's Directive Annex I species was negatively affected, | 168 | on the EU Bird's Directive Annex I species was negatively affected, | ||
| 169 | but since the wetland has been designated a Specially Protected Area | 169 | but since the wetland has been designated a Specially Protected Area | ||
| 170 | under this regulation, this represents a management failure. There | 170 | under this regulation, this represents a management failure. There | ||
| 171 | exists some chance, however, to manage peripheral cropland in favour | 171 | exists some chance, however, to manage peripheral cropland in favour | ||
| 172 | of biodiversity. The importance of monitoring in conservation | 172 | of biodiversity. The importance of monitoring in conservation | ||
| 173 | evaluation and management is also stressed, since the terrestrial bird | 173 | evaluation and management is also stressed, since the terrestrial bird | ||
| 174 | community of this wetland has not been regularly surveyed. In fact, | 174 | community of this wetland has not been regularly surveyed. In fact, | ||
| 175 | its evaluation against the Bird's Directive criteria was made in a | 175 | its evaluation against the Bird's Directive criteria was made in a | ||
| 176 | period of quick departure from the original, good ecological state of | 176 | period of quick departure from the original, good ecological state of | ||
| 177 | the wetland. (C) 2009 Elsevier Ltd. All rights reserved." | 177 | the wetland. (C) 2009 Elsevier Ltd. All rights reserved." | ||
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