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En el instante 25 de junio de 2026, 12:22:03 UTC,
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Modificado el valor del campo
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a2026-06-25
en Edge effects of roads on temperature, light, canopy cover, and canopy height in laurel and pine forests (Tenerife, Canary Islands). -
Modificado el valor del campo
modified
del recurso Acceso al recurso a2026-06-25
(anteriormente2026-06-23
) en Edge effects of roads on temperature, light, canopy cover, and canopy height in laurel and pine forests (Tenerife, Canary Islands).
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| 82 | "notes": "The estimation of the road edge effect is useful to | 96 | "notes": "The estimation of the road edge effect is useful to | ||
| 83 | understand changes induced by the road network on ecosystems. Road | 97 | understand changes induced by the road network on ecosystems. Road | ||
| 84 | networks on islands may break ecosystem integrity through microclimate | 98 | networks on islands may break ecosystem integrity through microclimate | ||
| 85 | edge effects, which are known to be associated with disturbances to | 99 | edge effects, which are known to be associated with disturbances to | ||
| 86 | animal and plant communities. Road edge effects have been scarcely | 100 | animal and plant communities. Road edge effects have been scarcely | ||
| 87 | studied on oceanic islands. In this paper we studied road edge effects | 101 | studied on oceanic islands. In this paper we studied road edge effects | ||
| 88 | on microclimate and canopy structure in laurel and pine forests in | 102 | on microclimate and canopy structure in laurel and pine forests in | ||
| 89 | Tenerife (Canary Islands). We assessed depth of road edge effect for | 103 | Tenerife (Canary Islands). We assessed depth of road edge effect for | ||
| 90 | temperature at four vertical layers (soil, litter and air at 5 cm and | 104 | temperature at four vertical layers (soil, litter and air at 5 cm and | ||
| 91 | 1.3 m above ground), light intensity, canopy cover and height, in | 105 | 1.3 m above ground), light intensity, canopy cover and height, in | ||
| 92 | transects running from narrow (6\u20137 m width) asphalt roads and | 106 | transects running from narrow (6\u20137 m width) asphalt roads and | ||
| 93 | dust trails to 100 m to the interior of both forests. We used an ANOVA | 107 | dust trails to 100 m to the interior of both forests. We used an ANOVA | ||
| 94 | procedure with Helmert difference contrasts to identify the distances | 108 | procedure with Helmert difference contrasts to identify the distances | ||
| 95 | along transects over which edge effects were significant. We detected | 109 | along transects over which edge effects were significant. We detected | ||
| 96 | significant gradients for most parameters but they were consistently | 110 | significant gradients for most parameters but they were consistently | ||
| 97 | narrow both within and between forests. In the laurel forest, we | 111 | narrow both within and between forests. In the laurel forest, we | ||
| 98 | detected highly significant gradients for soil temperature, light, and | 112 | detected highly significant gradients for soil temperature, light, and | ||
| 99 | canopy cover and height in both asphalt and unpaved roads. In the pine | 113 | canopy cover and height in both asphalt and unpaved roads. In the pine | ||
| 100 | forest, we detected a highly significant gradient for soil temperature | 114 | forest, we detected a highly significant gradient for soil temperature | ||
| 101 | at asphalt roads, and a significant light gradient for both asphalt | 115 | at asphalt roads, and a significant light gradient for both asphalt | ||
| 102 | and unpaved roads. From the road edge to the forest interior, | 116 | and unpaved roads. From the road edge to the forest interior, | ||
| 103 | significant temperature changes persisted for only 3 m, light | 117 | significant temperature changes persisted for only 3 m, light | ||
| 104 | variation persisted for 6 m, and canopy cover and height changed | 118 | variation persisted for 6 m, and canopy cover and height changed | ||
| 105 | significantly within the first 10 m. Asphalt roads and dust trails | 119 | significantly within the first 10 m. Asphalt roads and dust trails | ||
| 106 | revealed different patterns of variation for temperature between edge | 120 | revealed different patterns of variation for temperature between edge | ||
| 107 | and interior. No differences were found between the two types of roads | 121 | and interior. No differences were found between the two types of roads | ||
| 108 | in edge-interior trends for light or canopy structure. The abruptness | 122 | in edge-interior trends for light or canopy structure. The abruptness | ||
| 109 | of microclimate and canopy gradients was slightly higher in the laurel | 123 | of microclimate and canopy gradients was slightly higher in the laurel | ||
| 110 | forest than in the pine forest, caused by a higher edge contrast in | 124 | forest than in the pine forest, caused by a higher edge contrast in | ||
| 111 | the former. The depth of the road edge effect found in laurel and pine | 125 | the former. The depth of the road edge effect found in laurel and pine | ||
| 112 | forests was small, but it could have cumulative effects on forest | 126 | forests was small, but it could have cumulative effects on forest | ||
| 113 | microclimate and forest associated biota at the island scale. Such | 127 | microclimate and forest associated biota at the island scale. Such | ||
| 114 | changes deserve attention by local road managers for planning and | 128 | changes deserve attention by local road managers for planning and | ||
| 115 | design purposes.", | 129 | design purposes.", | ||
| 116 | "notes_translated": { | 130 | "notes_translated": { | ||
| 117 | "en": "The estimation of the road edge effect is useful to | 131 | "en": "The estimation of the road edge effect is useful to | ||
| 118 | understand changes induced by the road network on ecosystems. Road | 132 | understand changes induced by the road network on ecosystems. Road | ||
| 119 | networks on islands may break ecosystem integrity through microclimate | 133 | networks on islands may break ecosystem integrity through microclimate | ||
| 120 | edge effects, which are known to be associated with disturbances to | 134 | edge effects, which are known to be associated with disturbances to | ||
| 121 | animal and plant communities. Road edge effects have been scarcely | 135 | animal and plant communities. Road edge effects have been scarcely | ||
| 122 | studied on oceanic islands. In this paper we studied road edge effects | 136 | studied on oceanic islands. In this paper we studied road edge effects | ||
| 123 | on microclimate and canopy structure in laurel and pine forests in | 137 | on microclimate and canopy structure in laurel and pine forests in | ||
| 124 | Tenerife (Canary Islands). We assessed depth of road edge effect for | 138 | Tenerife (Canary Islands). We assessed depth of road edge effect for | ||
| 125 | temperature at four vertical layers (soil, litter and air at 5 cm and | 139 | temperature at four vertical layers (soil, litter and air at 5 cm and | ||
| 126 | 1.3 m above ground), light intensity, canopy cover and height, in | 140 | 1.3 m above ground), light intensity, canopy cover and height, in | ||
| 127 | transects running from narrow (6\u20137 m width) asphalt roads and | 141 | transects running from narrow (6\u20137 m width) asphalt roads and | ||
| 128 | dust trails to 100 m to the interior of both forests. We used an ANOVA | 142 | dust trails to 100 m to the interior of both forests. We used an ANOVA | ||
| 129 | procedure with Helmert difference contrasts to identify the distances | 143 | procedure with Helmert difference contrasts to identify the distances | ||
| 130 | along transects over which edge effects were significant. We detected | 144 | along transects over which edge effects were significant. We detected | ||
| 131 | significant gradients for most parameters but they were consistently | 145 | significant gradients for most parameters but they were consistently | ||
| 132 | narrow both within and between forests. In the laurel forest, we | 146 | narrow both within and between forests. In the laurel forest, we | ||
| 133 | detected highly significant gradients for soil temperature, light, and | 147 | detected highly significant gradients for soil temperature, light, and | ||
| 134 | canopy cover and height in both asphalt and unpaved roads. In the pine | 148 | canopy cover and height in both asphalt and unpaved roads. In the pine | ||
| 135 | forest, we detected a highly significant gradient for soil temperature | 149 | forest, we detected a highly significant gradient for soil temperature | ||
| 136 | at asphalt roads, and a significant light gradient for both asphalt | 150 | at asphalt roads, and a significant light gradient for both asphalt | ||
| 137 | and unpaved roads. From the road edge to the forest interior, | 151 | and unpaved roads. From the road edge to the forest interior, | ||
| 138 | significant temperature changes persisted for only 3 m, light | 152 | significant temperature changes persisted for only 3 m, light | ||
| 139 | variation persisted for 6 m, and canopy cover and height changed | 153 | variation persisted for 6 m, and canopy cover and height changed | ||
| 140 | significantly within the first 10 m. Asphalt roads and dust trails | 154 | significantly within the first 10 m. Asphalt roads and dust trails | ||
| 141 | revealed different patterns of variation for temperature between edge | 155 | revealed different patterns of variation for temperature between edge | ||
| 142 | and interior. No differences were found between the two types of roads | 156 | and interior. No differences were found between the two types of roads | ||
| 143 | in edge-interior trends for light or canopy structure. The abruptness | 157 | in edge-interior trends for light or canopy structure. The abruptness | ||
| 144 | of microclimate and canopy gradients was slightly higher in the laurel | 158 | of microclimate and canopy gradients was slightly higher in the laurel | ||
| 145 | forest than in the pine forest, caused by a higher edge contrast in | 159 | forest than in the pine forest, caused by a higher edge contrast in | ||
| 146 | the former. The depth of the road edge effect found in laurel and pine | 160 | the former. The depth of the road edge effect found in laurel and pine | ||
| 147 | forests was small, but it could have cumulative effects on forest | 161 | forests was small, but it could have cumulative effects on forest | ||
| 148 | microclimate and forest associated biota at the island scale. Such | 162 | microclimate and forest associated biota at the island scale. Such | ||
| 149 | changes deserve attention by local road managers for planning and | 163 | changes deserve attention by local road managers for planning and | ||
| 150 | design purposes.", | 164 | design purposes.", | ||
| 151 | "es": "The estimation of the road edge effect is useful to | 165 | "es": "The estimation of the road edge effect is useful to | ||
| 152 | understand changes induced by the road network on ecosystems. Road | 166 | understand changes induced by the road network on ecosystems. Road | ||
| 153 | networks on islands may break ecosystem integrity through microclimate | 167 | networks on islands may break ecosystem integrity through microclimate | ||
| 154 | edge effects, which are known to be associated with disturbances to | 168 | edge effects, which are known to be associated with disturbances to | ||
| 155 | animal and plant communities. Road edge effects have been scarcely | 169 | animal and plant communities. Road edge effects have been scarcely | ||
| 156 | studied on oceanic islands. In this paper we studied road edge effects | 170 | studied on oceanic islands. In this paper we studied road edge effects | ||
| 157 | on microclimate and canopy structure in laurel and pine forests in | 171 | on microclimate and canopy structure in laurel and pine forests in | ||
| 158 | Tenerife (Canary Islands). We assessed depth of road edge effect for | 172 | Tenerife (Canary Islands). We assessed depth of road edge effect for | ||
| 159 | temperature at four vertical layers (soil, litter and air at 5 cm and | 173 | temperature at four vertical layers (soil, litter and air at 5 cm and | ||
| 160 | 1.3 m above ground), light intensity, canopy cover and height, in | 174 | 1.3 m above ground), light intensity, canopy cover and height, in | ||
| 161 | transects running from narrow (6\u20137 m width) asphalt roads and | 175 | transects running from narrow (6\u20137 m width) asphalt roads and | ||
| 162 | dust trails to 100 m to the interior of both forests. We used an ANOVA | 176 | dust trails to 100 m to the interior of both forests. We used an ANOVA | ||
| 163 | procedure with Helmert difference contrasts to identify the distances | 177 | procedure with Helmert difference contrasts to identify the distances | ||
| 164 | along transects over which edge effects were significant. We detected | 178 | along transects over which edge effects were significant. We detected | ||
| 165 | significant gradients for most parameters but they were consistently | 179 | significant gradients for most parameters but they were consistently | ||
| 166 | narrow both within and between forests. In the laurel forest, we | 180 | narrow both within and between forests. In the laurel forest, we | ||
| 167 | detected highly significant gradients for soil temperature, light, and | 181 | detected highly significant gradients for soil temperature, light, and | ||
| 168 | canopy cover and height in both asphalt and unpaved roads. In the pine | 182 | canopy cover and height in both asphalt and unpaved roads. In the pine | ||
| 169 | forest, we detected a highly significant gradient for soil temperature | 183 | forest, we detected a highly significant gradient for soil temperature | ||
| 170 | at asphalt roads, and a significant light gradient for both asphalt | 184 | at asphalt roads, and a significant light gradient for both asphalt | ||
| 171 | and unpaved roads. From the road edge to the forest interior, | 185 | and unpaved roads. From the road edge to the forest interior, | ||
| 172 | significant temperature changes persisted for only 3 m, light | 186 | significant temperature changes persisted for only 3 m, light | ||
| 173 | variation persisted for 6 m, and canopy cover and height changed | 187 | variation persisted for 6 m, and canopy cover and height changed | ||
| 174 | significantly within the first 10 m. Asphalt roads and dust trails | 188 | significantly within the first 10 m. Asphalt roads and dust trails | ||
| 175 | revealed different patterns of variation for temperature between edge | 189 | revealed different patterns of variation for temperature between edge | ||
| 176 | and interior. No differences were found between the two types of roads | 190 | and interior. No differences were found between the two types of roads | ||
| 177 | in edge-interior trends for light or canopy structure. The abruptness | 191 | in edge-interior trends for light or canopy structure. The abruptness | ||
| 178 | of microclimate and canopy gradients was slightly higher in the laurel | 192 | of microclimate and canopy gradients was slightly higher in the laurel | ||
| 179 | forest than in the pine forest, caused by a higher edge contrast in | 193 | forest than in the pine forest, caused by a higher edge contrast in | ||
| 180 | the former. The depth of the road edge effect found in laurel and pine | 194 | the former. The depth of the road edge effect found in laurel and pine | ||
| 181 | forests was small, but it could have cumulative effects on forest | 195 | forests was small, but it could have cumulative effects on forest | ||
| 182 | microclimate and forest associated biota at the island scale. Such | 196 | microclimate and forest associated biota at the island scale. Such | ||
| 183 | changes deserve attention by local road managers for planning and | 197 | changes deserve attention by local road managers for planning and | ||
| 184 | design purposes." | 198 | design purposes." | ||
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