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en Road traffic noise impact assessment in a breeding colony of cinereous vultures (Aegypius monachus) in Spain. -
Modificado el valor del campo
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del recurso Acceso al recurso a2026-06-25
(anteriormente2026-06-23
) en Road traffic noise impact assessment in a breeding colony of cinereous vultures (Aegypius monachus) in Spain.
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| 83 | anthropogenic noise impact on wildlife and natural habitats, but it is | 97 | anthropogenic noise impact on wildlife and natural habitats, but it is | ||
| 84 | difficult to find consensus regarding scoping and assessment tools. | 98 | difficult to find consensus regarding scoping and assessment tools. | ||
| 85 | This study adapts noise mapping procedures, common to most European | 99 | This study adapts noise mapping procedures, common to most European | ||
| 86 | countries, to a low traffic road (below 1000 vehicles per day) noise | 100 | countries, to a low traffic road (below 1000 vehicles per day) noise | ||
| 87 | impact assessment in a breeding colony of the largest bird of prey in | 101 | impact assessment in a breeding colony of the largest bird of prey in | ||
| 88 | Europe. Results show that nest sites are located avoiding road traffic | 102 | Europe. Results show that nest sites are located avoiding road traffic | ||
| 89 | Leq levels higher than 40 dB. This means a road-effect zone of up to | 103 | Leq levels higher than 40 dB. This means a road-effect zone of up to | ||
| 90 | 500 m width from road margins, which previous scientific literature | 104 | 500 m width from road margins, which previous scientific literature | ||
| 91 | only refers in cases of traffic volumes higher than 10 000 vehicles | 105 | only refers in cases of traffic volumes higher than 10 000 vehicles | ||
| 92 | per day. This finding is a noticeable impact by road traffic noise | 106 | per day. This finding is a noticeable impact by road traffic noise | ||
| 93 | that reduces the breeding potential habitat more than 11% within the | 107 | that reduces the breeding potential habitat more than 11% within the | ||
| 94 | study area. This work shows the feasibility of expanding common | 108 | study area. This work shows the feasibility of expanding common | ||
| 95 | methods and mapping tools for assessing and managing environmental | 109 | methods and mapping tools for assessing and managing environmental | ||
| 96 | noise in protected areas, which has worthwhile implications for both | 110 | noise in protected areas, which has worthwhile implications for both | ||
| 97 | acoustics and conservation.\n Palabras clave: Breeding, Noise", | 111 | acoustics and conservation.\n Palabras clave: Breeding, Noise", | ||
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| 101 | difficult to find consensus regarding scoping and assessment tools. | 115 | difficult to find consensus regarding scoping and assessment tools. | ||
| 102 | This study adapts noise mapping procedures, common to most European | 116 | This study adapts noise mapping procedures, common to most European | ||
| 103 | countries, to a low traffic road (below 1000 vehicles per day) noise | 117 | countries, to a low traffic road (below 1000 vehicles per day) noise | ||
| 104 | impact assessment in a breeding colony of the largest bird of prey in | 118 | impact assessment in a breeding colony of the largest bird of prey in | ||
| 105 | Europe. Results show that nest sites are located avoiding road traffic | 119 | Europe. Results show that nest sites are located avoiding road traffic | ||
| 106 | Leq levels higher than 40\u2009dB. This means a road-effect zone of up | 120 | Leq levels higher than 40\u2009dB. This means a road-effect zone of up | ||
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| 108 | literature only refers in cases of traffic volumes higher than | 122 | literature only refers in cases of traffic volumes higher than | ||
| 109 | 10\u2009000 vehicles per day. This finding is a noticeable impact by | 123 | 10\u2009000 vehicles per day. This finding is a noticeable impact by | ||
| 110 | road traffic noise that reduces the breeding potential habitat more | 124 | road traffic noise that reduces the breeding potential habitat more | ||
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| 289 | "title": "Road traffic noise impact assessment in a breeding colony | 303 | "title": "Road traffic noise impact assessment in a breeding colony | ||
| 290 | of cinereous vultures (Aegypius monachus) in Spain.", | 304 | of cinereous vultures (Aegypius monachus) in Spain.", | ||
| 291 | "title_translated": { | 305 | "title_translated": { | ||
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| 293 | "es": "Road traffic noise impact assessment in a breeding colony | 307 | "es": "Road traffic noise impact assessment in a breeding colony | ||
| 294 | of cinereous vultures (Aegypius monachus) in Spain." | 308 | of cinereous vultures (Aegypius monachus) in Spain." | ||
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| 298 | "type": "dataset", | 312 | "type": "dataset", | ||
| 299 | "url": | 313 | "url": | ||
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