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En el instante 25 de junio de 2026, 12:35:52 UTC,
-
Modificado el valor del campo
modified
a2026-06-25
en Road encroachment mediates species occupancy, trait filtering and dissimilarity of passerine communities. -
Modificado el valor del campo
modified
del recurso Acceso al recurso a2026-06-25
(anteriormente2026-06-23
) en Road encroachment mediates species occupancy, trait filtering and dissimilarity of passerine communities.
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| 80 | "name": "735fca35-5114-5aa7-a6b1-0725ea3cb4d6", | 94 | "name": "735fca35-5114-5aa7-a6b1-0725ea3cb4d6", | ||
| 81 | "notes": "Assessing the road effects on biodiversity is challenging | 95 | "notes": "Assessing the road effects on biodiversity is challenging | ||
| 82 | because impacts may depend on both wildlife responses to roads and on | 96 | because impacts may depend on both wildlife responses to roads and on | ||
| 83 | the spatial arrangement of roads. We questioned whether an increase in | 97 | the spatial arrangement of roads. We questioned whether an increase in | ||
| 84 | road encroachment leads to significant changes in species occurrence | 98 | road encroachment leads to significant changes in species occurrence | ||
| 85 | and community composition. Using a large citizen-science dataset of | 99 | and community composition. Using a large citizen-science dataset of | ||
| 86 | point-counts performed throughout Iberian Peninsula, we modelled the | 100 | point-counts performed throughout Iberian Peninsula, we modelled the | ||
| 87 | effect of road density on the occurrence of common birds (n = 78 | 101 | effect of road density on the occurrence of common birds (n = 78 | ||
| 88 | species), while accounting for potential confounding effects of | 102 | species), while accounting for potential confounding effects of | ||
| 89 | environment and survey effort. We then tested if species' occurrence | 103 | environment and survey effort. We then tested if species' occurrence | ||
| 90 | patterns would be linked to specific traits related to the ability to | 104 | patterns would be linked to specific traits related to the ability to | ||
| 91 | cope with human presence. Finally, we assessed how road density | 105 | cope with human presence. Finally, we assessed how road density | ||
| 92 | affects the community compositional dissimilarity. We estimated 36 | 106 | affects the community compositional dissimilarity. We estimated 36 | ||
| 93 | (46%) and 18 (23%) species to be negatively and positively affected by | 107 | (46%) and 18 (23%) species to be negatively and positively affected by | ||
| 94 | roads, respectively. Increased road encroachment was positively | 108 | roads, respectively. Increased road encroachment was positively | ||
| 95 | related with urban dwelling and fecundity, and negatively related with | 109 | related with urban dwelling and fecundity, and negatively related with | ||
| 96 | nesting on the ground. Furthermore, increasing road density translated | 110 | nesting on the ground. Furthermore, increasing road density translated | ||
| 97 | into an increasing community compositional dissimilarity, mostly due | 111 | into an increasing community compositional dissimilarity, mostly due | ||
| 98 | to species turnover. Overall, we found that different species-specific | 112 | to species turnover. Overall, we found that different species-specific | ||
| 99 | responses to roads translate into changes at the community level. | 113 | responses to roads translate into changes at the community level. | ||
| 100 | Landscape and road-network management should be conceived | 114 | Landscape and road-network management should be conceived | ||
| 101 | acknowledging that roads are contributing to biodiversity changes. As | 115 | acknowledging that roads are contributing to biodiversity changes. As | ||
| 102 | so, building upon the concepts of land sharing/land sparing, | 116 | so, building upon the concepts of land sharing/land sparing, | ||
| 103 | conservation actions should be tailored according to the different | 117 | conservation actions should be tailored according to the different | ||
| 104 | species responses e.g., road verge management targeting species having | 118 | species responses e.g., road verge management targeting species having | ||
| 105 | a positive relation with road density; and compensation actions | 119 | a positive relation with road density; and compensation actions | ||
| 106 | targeting species showing a negative response toward roads.", | 120 | targeting species showing a negative response toward roads.", | ||
| 107 | "notes_translated": { | 121 | "notes_translated": { | ||
| 108 | "en": "Assessing the road effects on biodiversity is challenging | 122 | "en": "Assessing the road effects on biodiversity is challenging | ||
| 109 | because impacts may depend on both wildlife responses to roads and on | 123 | because impacts may depend on both wildlife responses to roads and on | ||
| 110 | the spatial arrangement of roads. We questioned whether an increase in | 124 | the spatial arrangement of roads. We questioned whether an increase in | ||
| 111 | road encroachment leads to significant changes in species occurrence | 125 | road encroachment leads to significant changes in species occurrence | ||
| 112 | and community composition. Using a large citizen-science dataset of | 126 | and community composition. Using a large citizen-science dataset of | ||
| 113 | point-counts performed throughout Iberian\u00a0Peninsula, we modelled | 127 | point-counts performed throughout Iberian\u00a0Peninsula, we modelled | ||
| 114 | the effect of road density on the occurrence of common birds | 128 | the effect of road density on the occurrence of common birds | ||
| 115 | (n\u00a0=\u00a078 species), while accounting for potential confounding | 129 | (n\u00a0=\u00a078 species), while accounting for potential confounding | ||
| 116 | effects of environment and survey effort. We then tested if species' | 130 | effects of environment and survey effort. We then tested if species' | ||
| 117 | occurrence patterns would be linked to specific traits related to the | 131 | occurrence patterns would be linked to specific traits related to the | ||
| 118 | ability to cope with human presence. Finally, we assessed how road | 132 | ability to cope with human presence. Finally, we assessed how road | ||
| 119 | density affects the community compositional dissimilarity. We | 133 | density affects the community compositional dissimilarity. We | ||
| 120 | estimated 36 (46%) and 18 (23%) species to be negatively and | 134 | estimated 36 (46%) and 18 (23%) species to be negatively and | ||
| 121 | positively affected by roads, respectively. Increased road | 135 | positively affected by roads, respectively. Increased road | ||
| 122 | encroachment was positively related with urban dwelling and fecundity, | 136 | encroachment was positively related with urban dwelling and fecundity, | ||
| 123 | and negatively related with nesting on the ground. Furthermore, | 137 | and negatively related with nesting on the ground. Furthermore, | ||
| 124 | increasing road density translated into an increasing community | 138 | increasing road density translated into an increasing community | ||
| 125 | compositional dissimilarity, mostly due to species turnover. Overall, | 139 | compositional dissimilarity, mostly due to species turnover. Overall, | ||
| 126 | we found that different species-specific responses to roads translate | 140 | we found that different species-specific responses to roads translate | ||
| 127 | into changes at the community level. Landscape and road-network | 141 | into changes at the community level. Landscape and road-network | ||
| 128 | management should be conceived acknowledging that roads are | 142 | management should be conceived acknowledging that roads are | ||
| 129 | contributing to biodiversity changes. As so, building upon the | 143 | contributing to biodiversity changes. As so, building upon the | ||
| 130 | concepts of land sharing/land sparing, conservation actions should be | 144 | concepts of land sharing/land sparing, conservation actions should be | ||
| 131 | tailored according to the different species responses e.g., road verge | 145 | tailored according to the different species responses e.g., road verge | ||
| 132 | management targeting species having a positive relation with road | 146 | management targeting species having a positive relation with road | ||
| 133 | density; and compensation actions targeting species showing a negative | 147 | density; and compensation actions targeting species showing a negative | ||
| 134 | response toward roads.", | 148 | response toward roads.", | ||
| 135 | "es": "Assessing the road effects on biodiversity is challenging | 149 | "es": "Assessing the road effects on biodiversity is challenging | ||
| 136 | because impacts may depend on both wildlife responses to roads and on | 150 | because impacts may depend on both wildlife responses to roads and on | ||
| 137 | the spatial arrangement of roads. We questioned whether an increase in | 151 | the spatial arrangement of roads. We questioned whether an increase in | ||
| 138 | road encroachment leads to significant changes in species occurrence | 152 | road encroachment leads to significant changes in species occurrence | ||
| 139 | and community composition. Using a large citizen-science dataset of | 153 | and community composition. Using a large citizen-science dataset of | ||
| 140 | point-counts performed throughout Iberian Peninsula, we modelled the | 154 | point-counts performed throughout Iberian Peninsula, we modelled the | ||
| 141 | effect of road density on the occurrence of common birds (n = 78 | 155 | effect of road density on the occurrence of common birds (n = 78 | ||
| 142 | species), while accounting for potential confounding effects of | 156 | species), while accounting for potential confounding effects of | ||
| 143 | environment and survey effort. We then tested if species' occurrence | 157 | environment and survey effort. We then tested if species' occurrence | ||
| 144 | patterns would be linked to specific traits related to the ability to | 158 | patterns would be linked to specific traits related to the ability to | ||
| 145 | cope with human presence. Finally, we assessed how road density | 159 | cope with human presence. Finally, we assessed how road density | ||
| 146 | affects the community compositional dissimilarity. We estimated 36 | 160 | affects the community compositional dissimilarity. We estimated 36 | ||
| 147 | (46%) and 18 (23%) species to be negatively and positively affected by | 161 | (46%) and 18 (23%) species to be negatively and positively affected by | ||
| 148 | roads, respectively. Increased road encroachment was positively | 162 | roads, respectively. Increased road encroachment was positively | ||
| 149 | related with urban dwelling and fecundity, and negatively related with | 163 | related with urban dwelling and fecundity, and negatively related with | ||
| 150 | nesting on the ground. Furthermore, increasing road density translated | 164 | nesting on the ground. Furthermore, increasing road density translated | ||
| 151 | into an increasing community compositional dissimilarity, mostly due | 165 | into an increasing community compositional dissimilarity, mostly due | ||
| 152 | to species turnover. Overall, we found that different species-specific | 166 | to species turnover. Overall, we found that different species-specific | ||
| 153 | responses to roads translate into changes at the community level. | 167 | responses to roads translate into changes at the community level. | ||
| 154 | Landscape and road-network management should be conceived | 168 | Landscape and road-network management should be conceived | ||
| 155 | acknowledging that roads are contributing to biodiversity changes. As | 169 | acknowledging that roads are contributing to biodiversity changes. As | ||
| 156 | so, building upon the concepts of land sharing/land sparing, | 170 | so, building upon the concepts of land sharing/land sparing, | ||
| 157 | conservation actions should be tailored according to the different | 171 | conservation actions should be tailored according to the different | ||
| 158 | species responses e.g., road verge management targeting species having | 172 | species responses e.g., road verge management targeting species having | ||
| 159 | a positive relation with road density; and compensation actions | 173 | a positive relation with road density; and compensation actions | ||
| 160 | targeting species showing a negative response toward roads." | 174 | targeting species showing a negative response toward roads." | ||
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