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En el instante 25 de junio de 2026, 12:27:32 UTC,
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a2026-06-25
en Influence of anthropogenic noise for predicting cinereous vulture nest distribution. -
Modificado el valor del campo
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(anteriormente2026-06-23
) en Influence of anthropogenic noise for predicting cinereous vulture nest distribution.
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| 84 | becoming particularly relevant in the case of natural areas affected | 98 | becoming particularly relevant in the case of natural areas affected | ||
| 85 | by roads. The expansion of road networks is considered among the main | 99 | by roads. The expansion of road networks is considered among the main | ||
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| 87 | natural ecosystems on large scales. Indeed, traffic noise pollution | 101 | natural ecosystems on large scales. Indeed, traffic noise pollution | ||
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| 89 | species are frequently used as indicators of natural ecosystem health. | 103 | species are frequently used as indicators of natural ecosystem health. | ||
| 90 | In this sense, there is a variety of GIS-based ecological modeling | 104 | In this sense, there is a variety of GIS-based ecological modeling | ||
| 91 | tools that allow evaluation of the factors that influence species | 105 | tools that allow evaluation of the factors that influence species | ||
| 92 | distributions in order to accurately predict habitat selection. In | 106 | distributions in order to accurately predict habitat selection. In | ||
| 93 | this study, we have combined the use of noise modeling tools and | 107 | this study, we have combined the use of noise modeling tools and | ||
| 94 | maximum entropy modeling (MaxEnt) to evaluate the relative importance | 108 | maximum entropy modeling (MaxEnt) to evaluate the relative importance | ||
| 95 | of environmental variables for Cinereous vulture (Aegypius monachus) | 109 | of environmental variables for Cinereous vulture (Aegypius monachus) | ||
| 96 | nesting habitat selection within a mountainous forest in Spain. As a | 110 | nesting habitat selection within a mountainous forest in Spain. As a | ||
| 97 | result, we found that spatial negative influence of roads on wildlife | 111 | result, we found that spatial negative influence of roads on wildlife | ||
| 98 | due to road traffic disturbance may have been traditionally | 112 | due to road traffic disturbance may have been traditionally | ||
| 99 | overestimated when it has been inferred from distance measurements of | 113 | overestimated when it has been inferred from distance measurements of | ||
| 100 | wildlife behavior in road surroundings instead of from considering | 114 | wildlife behavior in road surroundings instead of from considering | ||
| 101 | road traffic noise level exposure. In addition, we found a potential | 115 | road traffic noise level exposure. In addition, we found a potential | ||
| 102 | risk threshold for cinereous vulture breeding around roads, which ties | 116 | risk threshold for cinereous vulture breeding around roads, which ties | ||
| 103 | in with a Leq24h level of 40 dB(A). This may be a useful indicator for | 117 | in with a Leq24h level of 40 dB(A). This may be a useful indicator for | ||
| 104 | assessing the potential impact of human activities on an umbrella | 118 | assessing the potential impact of human activities on an umbrella | ||
| 105 | species such as, for instance, the cinereous vulture, whose breeding | 119 | species such as, for instance, the cinereous vulture, whose breeding | ||
| 106 | does not take place where road traffic Leq24h levels are higher than | 120 | does not take place where road traffic Leq24h levels are higher than | ||
| 107 | 40 dB(A).", | 121 | 40 dB(A).", | ||
| 108 | "notes_translated": { | 122 | "notes_translated": { | ||
| 109 | "en": "Natural landscapes are increasingly under anthropogenic | 123 | "en": "Natural landscapes are increasingly under anthropogenic | ||
| 110 | pressures, and concern about human impacts on wildlife populations is | 124 | pressures, and concern about human impacts on wildlife populations is | ||
| 111 | becoming particularly relevant in the case of natural areas affected | 125 | becoming particularly relevant in the case of natural areas affected | ||
| 112 | by roads. The expansion of road networks is considered among the main | 126 | by roads. The expansion of road networks is considered among the main | ||
| 113 | factors threatening biodiversity due to their potential for disturbing | 127 | factors threatening biodiversity due to their potential for disturbing | ||
| 114 | natural ecosystems on large scales. Indeed, traffic noise pollution | 128 | natural ecosystems on large scales. Indeed, traffic noise pollution | ||
| 115 | reduces the quantity and the quality of natural habitats, and umbrella | 129 | reduces the quantity and the quality of natural habitats, and umbrella | ||
| 116 | species are frequently used as indicators of natural ecosystem health. | 130 | species are frequently used as indicators of natural ecosystem health. | ||
| 117 | In this sense, there is a variety of GIS-based ecological modeling | 131 | In this sense, there is a variety of GIS-based ecological modeling | ||
| 118 | tools that allow evaluation of the factors that influence species | 132 | tools that allow evaluation of the factors that influence species | ||
| 119 | distributions in order to accurately predict habitat selection. In | 133 | distributions in order to accurately predict habitat selection. In | ||
| 120 | this study, we have combined the use of noise modeling tools and | 134 | this study, we have combined the use of noise modeling tools and | ||
| 121 | maximum entropy modeling (MaxEnt) to evaluate the relative importance | 135 | maximum entropy modeling (MaxEnt) to evaluate the relative importance | ||
| 122 | of environmental variables for Cinereous vulture (Aegypius monachus) | 136 | of environmental variables for Cinereous vulture (Aegypius monachus) | ||
| 123 | nesting habitat selection within a mountainous forest in Spain. As a | 137 | nesting habitat selection within a mountainous forest in Spain. As a | ||
| 124 | result, we found that spatial negative influence of roads on wildlife | 138 | result, we found that spatial negative influence of roads on wildlife | ||
| 125 | due to road traffic disturbance may have been traditionally | 139 | due to road traffic disturbance may have been traditionally | ||
| 126 | overestimated when it has been inferred from distance measurements of | 140 | overestimated when it has been inferred from distance measurements of | ||
| 127 | wildlife behavior in road surroundings instead of from considering | 141 | wildlife behavior in road surroundings instead of from considering | ||
| 128 | road traffic noise level exposure. In addition, we found a potential | 142 | road traffic noise level exposure. In addition, we found a potential | ||
| 129 | risk threshold for cinereous vulture breeding around roads, which ties | 143 | risk threshold for cinereous vulture breeding around roads, which ties | ||
| 130 | in with a Leq24h\u00a0level of 40 dB(A). This may be a useful | 144 | in with a Leq24h\u00a0level of 40 dB(A). This may be a useful | ||
| 131 | indicator for assessing the potential impact of human activities on an | 145 | indicator for assessing the potential impact of human activities on an | ||
| 132 | umbrella species such as, for instance, the cinereous vulture, whose | 146 | umbrella species such as, for instance, the cinereous vulture, whose | ||
| 133 | breeding does not take place where road traffic Leq24h\u00a0levels are | 147 | breeding does not take place where road traffic Leq24h\u00a0levels are | ||
| 134 | higher than 40 dB(A).", | 148 | higher than 40 dB(A).", | ||
| 135 | "es": "Natural landscapes are increasingly under anthropogenic | 149 | "es": "Natural landscapes are increasingly under anthropogenic | ||
| 136 | pressures, and concern about human impacts on wildlife populations is | 150 | pressures, and concern about human impacts on wildlife populations is | ||
| 137 | becoming particularly relevant in the case of natural areas affected | 151 | becoming particularly relevant in the case of natural areas affected | ||
| 138 | by roads. The expansion of road networks is considered among the main | 152 | by roads. The expansion of road networks is considered among the main | ||
| 139 | factors threatening biodiversity due to their potential for disturbing | 153 | factors threatening biodiversity due to their potential for disturbing | ||
| 140 | natural ecosystems on large scales. Indeed, traffic noise pollution | 154 | natural ecosystems on large scales. Indeed, traffic noise pollution | ||
| 141 | reduces the quantity and the quality of natural habitats, and umbrella | 155 | reduces the quantity and the quality of natural habitats, and umbrella | ||
| 142 | species are frequently used as indicators of natural ecosystem health. | 156 | species are frequently used as indicators of natural ecosystem health. | ||
| 143 | In this sense, there is a variety of GIS-based ecological modeling | 157 | In this sense, there is a variety of GIS-based ecological modeling | ||
| 144 | tools that allow evaluation of the factors that influence species | 158 | tools that allow evaluation of the factors that influence species | ||
| 145 | distributions in order to accurately predict habitat selection. In | 159 | distributions in order to accurately predict habitat selection. In | ||
| 146 | this study, we have combined the use of noise modeling tools and | 160 | this study, we have combined the use of noise modeling tools and | ||
| 147 | maximum entropy modeling (MaxEnt) to evaluate the relative importance | 161 | maximum entropy modeling (MaxEnt) to evaluate the relative importance | ||
| 148 | of environmental variables for Cinereous vulture (Aegypius monachus) | 162 | of environmental variables for Cinereous vulture (Aegypius monachus) | ||
| 149 | nesting habitat selection within a mountainous forest in Spain. As a | 163 | nesting habitat selection within a mountainous forest in Spain. As a | ||
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| 154 | road traffic noise level exposure. In addition, we found a potential | 168 | road traffic noise level exposure. In addition, we found a potential | ||
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