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En el instante 23 de junio de 2026, 16:09:54 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 Traffic noise pollution does not influence habitat selection in the endangered little bustard.
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| 81 | "name": "3edc2774-5c94-5720-9ab9-4aab9a6d2b6e", | 81 | "name": "3edc2774-5c94-5720-9ab9-4aab9a6d2b6e", | ||
| 82 | "notes": "Traffic noise is an associated effect of roads, | 82 | "notes": "Traffic noise is an associated effect of roads, | ||
| 83 | potentially impacting wildlife. In the case of birds, it may alter | 83 | potentially impacting wildlife. In the case of birds, it may alter | ||
| 84 | spatial distribution, behavioural responses and physiological status, | 84 | spatial distribution, behavioural responses and physiological status, | ||
| 85 | frequently masking the acoustic signals of conspecifics and predators. | 85 | frequently masking the acoustic signals of conspecifics and predators. | ||
| 86 | We analyse how road traffic noise affects habitat selection of Little | 86 | We analyse how road traffic noise affects habitat selection of Little | ||
| 87 | Bustard males during the breeding season, when they produce brief | 87 | Bustard males during the breeding season, when they produce brief | ||
| 88 | territorial snort calls. The study site is in a typical agrarian area | 88 | territorial snort calls. The study site is in a typical agrarian area | ||
| 89 | in central Spain, markedly affected by traffic noise. A noise map was | 89 | in central Spain, markedly affected by traffic noise. A noise map was | ||
| 90 | built using specific environmental noise modelling software. The | 90 | built using specific environmental noise modelling software. The | ||
| 91 | habitat in the territories of 26 individually-recognisable males (62% | 91 | habitat in the territories of 26 individually-recognisable males (62% | ||
| 92 | of the male population in the study year) was characterised in | 92 | of the male population in the study year) was characterised in | ||
| 93 | relation to noise levels, agrarian substrate composition and distance | 93 | relation to noise levels, agrarian substrate composition and distance | ||
| 94 | to nearest males. Habitat selection models were performed using | 94 | to nearest males. Habitat selection models were performed using | ||
| 95 | MaxEnt, and an averaged model of the first 20 significant ones was | 95 | MaxEnt, and an averaged model of the first 20 significant ones was | ||
| 96 | generated. The noise map revealed high noise pollution levels for the | 96 | generated. The noise map revealed high noise pollution levels for the | ||
| 97 | whole study area (range: 50.13\u201362.35 dB). Distance to the nearest | 97 | whole study area (range: 50.13\u201362.35 dB). Distance to the nearest | ||
| 98 | male was the most important variable in habitat selection models, so | 98 | male was the most important variable in habitat selection models, so | ||
| 99 | that as distance increased suitability decreased, while the effect of | 99 | that as distance increased suitability decreased, while the effect of | ||
| 100 | traffic noise was nearly negligible. This lack of traffic noise effect | 100 | traffic noise was nearly negligible. This lack of traffic noise effect | ||
| 101 | on the habitat selection of Little Bustard males might be explained by | 101 | on the habitat selection of Little Bustard males might be explained by | ||
| 102 | the low overlap between their snort call frequency and that of traffic | 102 | the low overlap between their snort call frequency and that of traffic | ||
| 103 | noise, but it also suggests a poor capacity by this bird to cope with | 103 | noise, but it also suggests a poor capacity by this bird to cope with | ||
| 104 | recent, anthropogenic disturbance. In this respect, noisy but | 104 | recent, anthropogenic disturbance. In this respect, noisy but | ||
| 105 | otherwise suitable habitats could be functioning as ecological traps | 105 | otherwise suitable habitats could be functioning as ecological traps | ||
| 106 | for this rapidly declining species\n Palabras clave: Habitat, Noise, | 106 | for this rapidly declining species\n Palabras clave: Habitat, Noise, | ||
| 107 | Pollution", | 107 | Pollution", | ||
| 108 | "notes_translated": { | 108 | "notes_translated": { | ||
| 109 | "en": "Traffic noise is an associated effect of roads, potentially | 109 | "en": "Traffic noise is an associated effect of roads, potentially | ||
| 110 | impacting wildlife. In the case of birds, it may alter spatial | 110 | impacting wildlife. In the case of birds, it may alter spatial | ||
| 111 | distribution, behavioural responses and physiological status, | 111 | distribution, behavioural responses and physiological status, | ||
| 112 | frequently masking the acoustic signals of conspecifics and predators. | 112 | frequently masking the acoustic signals of conspecifics and predators. | ||
| 113 | We analyse how road traffic noise affects habitat selection of Little | 113 | We analyse how road traffic noise affects habitat selection of Little | ||
| 114 | Bustard males during the breeding season, when they produce brief | 114 | Bustard males during the breeding season, when they produce brief | ||
| 115 | territorial snort calls. The study site is in a typical agrarian area | 115 | territorial snort calls. The study site is in a typical agrarian area | ||
| 116 | in central Spain, markedly affected by traffic noise. A noise map was | 116 | in central Spain, markedly affected by traffic noise. A noise map was | ||
| 117 | built using specific environmental noise modelling software. The | 117 | built using specific environmental noise modelling software. The | ||
| 118 | habitat in the territories of 26 individually-recognisable males (62% | 118 | habitat in the territories of 26 individually-recognisable males (62% | ||
| 119 | of the male population in the study year) was characterised in | 119 | of the male population in the study year) was characterised in | ||
| 120 | relation to noise levels, agrarian substrate composition and distance | 120 | relation to noise levels, agrarian substrate composition and distance | ||
| 121 | to nearest males. Habitat selection models were performed using | 121 | to nearest males. Habitat selection models were performed using | ||
| 122 | MaxEnt, and an averaged model of the first 20 significant ones was | 122 | MaxEnt, and an averaged model of the first 20 significant ones was | ||
| 123 | generated. The noise map revealed high noise pollution levels for the | 123 | generated. The noise map revealed high noise pollution levels for the | ||
| 124 | whole study area (range: 50.13\u201362.35 dB). Distance to the nearest | 124 | whole study area (range: 50.13\u201362.35 dB). Distance to the nearest | ||
| 125 | male was the most important variable in habitat selection models, so | 125 | male was the most important variable in habitat selection models, so | ||
| 126 | that as distance increased suitability decreased, while the effect of | 126 | that as distance increased suitability decreased, while the effect of | ||
| 127 | traffic noise was nearly negligible. This lack of traffic noise effect | 127 | traffic noise was nearly negligible. This lack of traffic noise effect | ||
| 128 | on the habitat selection of Little Bustard males might be explained by | 128 | on the habitat selection of Little Bustard males might be explained by | ||
| 129 | the low overlap between their snort call frequency and that of traffic | 129 | the low overlap between their snort call frequency and that of traffic | ||
| 130 | noise, but it also suggests a poor capacity by this bird to cope with | 130 | noise, but it also suggests a poor capacity by this bird to cope with | ||
| 131 | recent, anthropogenic disturbance. In this respect, noisy but | 131 | recent, anthropogenic disturbance. In this respect, noisy but | ||
| 132 | otherwise suitable habitats could be functioning as ecological traps | 132 | otherwise suitable habitats could be functioning as ecological traps | ||
| 133 | for this rapidly declining species", | 133 | for this rapidly declining species", | ||
| 134 | "es": "Traffic noise is an associated effect of roads, potentially | 134 | "es": "Traffic noise is an associated effect of roads, potentially | ||
| 135 | impacting wildlife. In the case of birds, it may alter spatial | 135 | impacting wildlife. In the case of birds, it may alter spatial | ||
| 136 | distribution, behavioural responses and physiological status, | 136 | distribution, behavioural responses and physiological status, | ||
| 137 | frequently masking the acoustic signals of conspecifics and predators. | 137 | frequently masking the acoustic signals of conspecifics and predators. | ||
| 138 | We analyse how road traffic noise affects habitat selection of Little | 138 | We analyse how road traffic noise affects habitat selection of Little | ||
| 139 | Bustard males during the breeding season, when they produce brief | 139 | Bustard males during the breeding season, when they produce brief | ||
| 140 | territorial snort calls. The study site is in a typical agrarian area | 140 | territorial snort calls. The study site is in a typical agrarian area | ||
| 141 | in central Spain, markedly affected by traffic noise. A noise map was | 141 | in central Spain, markedly affected by traffic noise. A noise map was | ||
| 142 | built using specific environmental noise modelling software. The | 142 | built using specific environmental noise modelling software. The | ||
| 143 | habitat in the territories of 26 individually-recognisable males (62% | 143 | habitat in the territories of 26 individually-recognisable males (62% | ||
| 144 | of the male population in the study year) was characterised in | 144 | of the male population in the study year) was characterised in | ||
| 145 | relation to noise levels, agrarian substrate composition and distance | 145 | relation to noise levels, agrarian substrate composition and distance | ||
| 146 | to nearest males. Habitat selection models were performed using | 146 | to nearest males. Habitat selection models were performed using | ||
| 147 | MaxEnt, and an averaged model of the first 20 significant ones was | 147 | MaxEnt, and an averaged model of the first 20 significant ones was | ||
| 148 | generated. The noise map revealed high noise pollution levels for the | 148 | generated. The noise map revealed high noise pollution levels for the | ||
| 149 | whole study area (range: 50.13\u201362.35 dB). Distance to the nearest | 149 | whole study area (range: 50.13\u201362.35 dB). Distance to the nearest | ||
| 150 | male was the most important variable in habitat selection models, so | 150 | male was the most important variable in habitat selection models, so | ||
| 151 | that as distance increased suitability decreased, while the effect of | 151 | that as distance increased suitability decreased, while the effect of | ||
| 152 | traffic noise was nearly negligible. This lack of traffic noise effect | 152 | traffic noise was nearly negligible. This lack of traffic noise effect | ||
| 153 | on the habitat selection of Little Bustard males might be explained by | 153 | on the habitat selection of Little Bustard males might be explained by | ||
| 154 | the low overlap between their snort call frequency and that of traffic | 154 | the low overlap between their snort call frequency and that of traffic | ||
| 155 | noise, but it also suggests a poor capacity by this bird to cope with | 155 | noise, but it also suggests a poor capacity by this bird to cope with | ||
| 156 | recent, anthropogenic disturbance. In this respect, noisy but | 156 | recent, anthropogenic disturbance. In this respect, noisy but | ||
| 157 | otherwise suitable habitats could be functioning as ecological traps | 157 | otherwise suitable habitats could be functioning as ecological traps | ||
| 158 | for this rapidly declining species\n Palabras clave: Habitat, Noise, | 158 | for this rapidly declining species\n Palabras clave: Habitat, Noise, | ||
| 159 | Pollution" | 159 | Pollution" | ||
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