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En el instante 25 de junio de 2026, 12:40:01 UTC,
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Modificado el valor del campo
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a2026-06-25
en Traffic noise pollution does not influence habitat selection in the endangered little bustard. -
Modificado el valor del campo
modified
del recurso Acceso al recurso a2026-06-25
(anteriormente2026-06-23
) en Traffic noise pollution does not influence habitat selection in the endangered little bustard.
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| 5 | "author": "Mart\u00ednez-Marivela, I., Morales, M.B., | 5 | "author": "Mart\u00ednez-Marivela, I., Morales, M.B., | ||
| 6 | Iglesias-Merch\u00e1n, C., Delgado, M.P., Tarjuelo, R. y Traba, J.", | 6 | Iglesias-Merch\u00e1n, C., Delgado, M.P., Tarjuelo, R. y Traba, J.", | ||
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| n | 67 | "metadata_modified": "2026-06-23T16:09:54.066862", | n | 81 | "metadata_modified": "2026-06-25T12:40:01.227220", |
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| 71 | "miteco_data_population": { | 85 | "miteco_data_population": { | ||
| 72 | "es": "" | 86 | "es": "" | ||
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| 74 | "miteco_data_territory": { | 88 | "miteco_data_territory": { | ||
| 75 | "es": "" | 89 | "es": "" | ||
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| 77 | "miteco_dataset_type": | 91 | "miteco_dataset_type": | ||
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| n | 80 | "modified": "2026-06-23", | n | 94 | "modified": "2026-06-25", |
| 81 | "name": "3edc2774-5c94-5720-9ab9-4aab9a6d2b6e", | 95 | "name": "3edc2774-5c94-5720-9ab9-4aab9a6d2b6e", | ||
| 82 | "notes": "Traffic noise is an associated effect of roads, | 96 | "notes": "Traffic noise is an associated effect of roads, | ||
| 83 | potentially impacting wildlife. In the case of birds, it may alter | 97 | potentially impacting wildlife. In the case of birds, it may alter | ||
| 84 | spatial distribution, behavioural responses and physiological status, | 98 | spatial distribution, behavioural responses and physiological status, | ||
| 85 | frequently masking the acoustic signals of conspecifics and predators. | 99 | frequently masking the acoustic signals of conspecifics and predators. | ||
| 86 | We analyse how road traffic noise affects habitat selection of Little | 100 | We analyse how road traffic noise affects habitat selection of Little | ||
| 87 | Bustard males during the breeding season, when they produce brief | 101 | Bustard males during the breeding season, when they produce brief | ||
| 88 | territorial snort calls. The study site is in a typical agrarian area | 102 | 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 | 103 | in central Spain, markedly affected by traffic noise. A noise map was | ||
| 90 | built using specific environmental noise modelling software. The | 104 | built using specific environmental noise modelling software. The | ||
| 91 | habitat in the territories of 26 individually-recognisable males (62% | 105 | habitat in the territories of 26 individually-recognisable males (62% | ||
| 92 | of the male population in the study year) was characterised in | 106 | of the male population in the study year) was characterised in | ||
| 93 | relation to noise levels, agrarian substrate composition and distance | 107 | relation to noise levels, agrarian substrate composition and distance | ||
| 94 | to nearest males. Habitat selection models were performed using | 108 | to nearest males. Habitat selection models were performed using | ||
| 95 | MaxEnt, and an averaged model of the first 20 significant ones was | 109 | MaxEnt, and an averaged model of the first 20 significant ones was | ||
| 96 | generated. The noise map revealed high noise pollution levels for the | 110 | 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 | 111 | 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 | 112 | male was the most important variable in habitat selection models, so | ||
| 99 | that as distance increased suitability decreased, while the effect of | 113 | that as distance increased suitability decreased, while the effect of | ||
| 100 | traffic noise was nearly negligible. This lack of traffic noise effect | 114 | traffic noise was nearly negligible. This lack of traffic noise effect | ||
| 101 | on the habitat selection of Little Bustard males might be explained by | 115 | 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 | 116 | 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 | 117 | noise, but it also suggests a poor capacity by this bird to cope with | ||
| 104 | recent, anthropogenic disturbance. In this respect, noisy but | 118 | recent, anthropogenic disturbance. In this respect, noisy but | ||
| 105 | otherwise suitable habitats could be functioning as ecological traps | 119 | otherwise suitable habitats could be functioning as ecological traps | ||
| 106 | for this rapidly declining species\n Palabras clave: Habitat, Noise, | 120 | for this rapidly declining species\n Palabras clave: Habitat, Noise, | ||
| 107 | Pollution", | 121 | Pollution", | ||
| 108 | "notes_translated": { | 122 | "notes_translated": { | ||
| 109 | "en": "Traffic noise is an associated effect of roads, potentially | 123 | "en": "Traffic noise is an associated effect of roads, potentially | ||
| 110 | impacting wildlife. In the case of birds, it may alter spatial | 124 | impacting wildlife. In the case of birds, it may alter spatial | ||
| 111 | distribution, behavioural responses and physiological status, | 125 | distribution, behavioural responses and physiological status, | ||
| 112 | frequently masking the acoustic signals of conspecifics and predators. | 126 | frequently masking the acoustic signals of conspecifics and predators. | ||
| 113 | We analyse how road traffic noise affects habitat selection of Little | 127 | We analyse how road traffic noise affects habitat selection of Little | ||
| 114 | Bustard males during the breeding season, when they produce brief | 128 | Bustard males during the breeding season, when they produce brief | ||
| 115 | territorial snort calls. The study site is in a typical agrarian area | 129 | 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 | 130 | in central Spain, markedly affected by traffic noise. A noise map was | ||
| 117 | built using specific environmental noise modelling software. The | 131 | built using specific environmental noise modelling software. The | ||
| 118 | habitat in the territories of 26 individually-recognisable males (62% | 132 | habitat in the territories of 26 individually-recognisable males (62% | ||
| 119 | of the male population in the study year) was characterised in | 133 | of the male population in the study year) was characterised in | ||
| 120 | relation to noise levels, agrarian substrate composition and distance | 134 | relation to noise levels, agrarian substrate composition and distance | ||
| 121 | to nearest males. Habitat selection models were performed using | 135 | to nearest males. Habitat selection models were performed using | ||
| 122 | MaxEnt, and an averaged model of the first 20 significant ones was | 136 | MaxEnt, and an averaged model of the first 20 significant ones was | ||
| 123 | generated. The noise map revealed high noise pollution levels for the | 137 | 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 | 138 | 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 | 139 | male was the most important variable in habitat selection models, so | ||
| 126 | that as distance increased suitability decreased, while the effect of | 140 | that as distance increased suitability decreased, while the effect of | ||
| 127 | traffic noise was nearly negligible. This lack of traffic noise effect | 141 | traffic noise was nearly negligible. This lack of traffic noise effect | ||
| 128 | on the habitat selection of Little Bustard males might be explained by | 142 | 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 | 143 | 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 | 144 | noise, but it also suggests a poor capacity by this bird to cope with | ||
| 131 | recent, anthropogenic disturbance. In this respect, noisy but | 145 | recent, anthropogenic disturbance. In this respect, noisy but | ||
| 132 | otherwise suitable habitats could be functioning as ecological traps | 146 | otherwise suitable habitats could be functioning as ecological traps | ||
| 133 | for this rapidly declining species", | 147 | for this rapidly declining species", | ||
| 134 | "es": "Traffic noise is an associated effect of roads, potentially | 148 | "es": "Traffic noise is an associated effect of roads, potentially | ||
| 135 | impacting wildlife. In the case of birds, it may alter spatial | 149 | impacting wildlife. In the case of birds, it may alter spatial | ||
| 136 | distribution, behavioural responses and physiological status, | 150 | distribution, behavioural responses and physiological status, | ||
| 137 | frequently masking the acoustic signals of conspecifics and predators. | 151 | frequently masking the acoustic signals of conspecifics and predators. | ||
| 138 | We analyse how road traffic noise affects habitat selection of Little | 152 | We analyse how road traffic noise affects habitat selection of Little | ||
| 139 | Bustard males during the breeding season, when they produce brief | 153 | Bustard males during the breeding season, when they produce brief | ||
| 140 | territorial snort calls. The study site is in a typical agrarian area | 154 | 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 | 155 | in central Spain, markedly affected by traffic noise. A noise map was | ||
| 142 | built using specific environmental noise modelling software. The | 156 | built using specific environmental noise modelling software. The | ||
| 143 | habitat in the territories of 26 individually-recognisable males (62% | 157 | habitat in the territories of 26 individually-recognisable males (62% | ||
| 144 | of the male population in the study year) was characterised in | 158 | of the male population in the study year) was characterised in | ||
| 145 | relation to noise levels, agrarian substrate composition and distance | 159 | relation to noise levels, agrarian substrate composition and distance | ||
| 146 | to nearest males. Habitat selection models were performed using | 160 | to nearest males. Habitat selection models were performed using | ||
| 147 | MaxEnt, and an averaged model of the first 20 significant ones was | 161 | MaxEnt, and an averaged model of the first 20 significant ones was | ||
| 148 | generated. The noise map revealed high noise pollution levels for the | 162 | 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 | 163 | 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 | 164 | male was the most important variable in habitat selection models, so | ||
| 151 | that as distance increased suitability decreased, while the effect of | 165 | that as distance increased suitability decreased, while the effect of | ||
| 152 | traffic noise was nearly negligible. This lack of traffic noise effect | 166 | traffic noise was nearly negligible. This lack of traffic noise effect | ||
| 153 | on the habitat selection of Little Bustard males might be explained by | 167 | 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 | 168 | 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 | 169 | noise, but it also suggests a poor capacity by this bird to cope with | ||
| 156 | recent, anthropogenic disturbance. In this respect, noisy but | 170 | recent, anthropogenic disturbance. In this respect, noisy but | ||
| 157 | otherwise suitable habitats could be functioning as ecological traps | 171 | otherwise suitable habitats could be functioning as ecological traps | ||
| 158 | for this rapidly declining species\n Palabras clave: Habitat, Noise, | 172 | for this rapidly declining species\n Palabras clave: Habitat, Noise, | ||
| 159 | Pollution" | 173 | Pollution" | ||
| 160 | }, | 174 | }, | ||
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| 187 | Demogr\u00e1fico", | 201 | Demogr\u00e1fico", | ||
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