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| 5 | "author": "Delgado Garc\u00eda, J.D., Ar\u00e9valo, J.R. y | 5 | "author": "Delgado Garc\u00eda, J.D., Ar\u00e9valo, J.R. y | ||
| 6 | Fern\u00e1ndez-Palacios, J.M.", | 6 | Fern\u00e1ndez-Palacios, J.M.", | ||
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| 8 | Fern\u00e1ndez-Palacios, J.M.", | 8 | Fern\u00e1ndez-Palacios, J.M.", | ||
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| 59 | "lineage_source": [ | 59 | "lineage_source": [ | ||
| 60 | "Biodiversity and Conservation. Vol. 16", | 60 | "Biodiversity and Conservation. Vol. 16", | ||
| 61 | "Num. 10", | 61 | "Num. 10", | ||
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| 80 | "modified": "2026-06-23", | 80 | "modified": "2026-06-23", | ||
| 81 | "name": "e1eada9b-4049-506d-a35c-30d1b134ae9e", | 81 | "name": "e1eada9b-4049-506d-a35c-30d1b134ae9e", | ||
| 82 | "notes": "Transportation infrastructure is a main cause of | 82 | "notes": "Transportation infrastructure is a main cause of | ||
| 83 | environmental change in forest landscapes worldwide. In the Canary | 83 | environmental change in forest landscapes worldwide. In the Canary | ||
| 84 | Islands, a dense road system fragment the native Canarian pine and | 84 | Islands, a dense road system fragment the native Canarian pine and | ||
| 85 | laurel forests causing potential changes in population densities of | 85 | laurel forests causing potential changes in population densities of | ||
| 86 | endemic lacertid lizards (genus Gallotia). Our aim was to assess road | 86 | endemic lacertid lizards (genus Gallotia). Our aim was to assess road | ||
| 87 | edge effects on relative abundance patterns of the endemic Gallotia | 87 | edge effects on relative abundance patterns of the endemic Gallotia | ||
| 88 | galloti in both forests. We also explored the species\u2013habitat | 88 | galloti in both forests. We also explored the species\u2013habitat | ||
| 89 | relationships in this road-fragmentation context. We found that lizard | 89 | relationships in this road-fragmentation context. We found that lizard | ||
| 90 | relative density in relation to road edges differed between forests. | 90 | relative density in relation to road edges differed between forests. | ||
| 91 | Lizards were more abundant along edges and leeward interior, but | 91 | Lizards were more abundant along edges and leeward interior, but | ||
| 92 | virtually absent from the interior of the windward laurel forest. In | 92 | virtually absent from the interior of the windward laurel forest. In | ||
| 93 | the pine forest, lizards were present at three distances from edge, | 93 | the pine forest, lizards were present at three distances from edge, | ||
| 94 | with a net decrease in abundance from edge to interior. These patterns | 94 | with a net decrease in abundance from edge to interior. These patterns | ||
| 95 | may be explained partly by differences in vegetation structure | 95 | may be explained partly by differences in vegetation structure | ||
| 96 | regarding road proximity in each forest that potentially affect the | 96 | regarding road proximity in each forest that potentially affect the | ||
| 97 | helio- and thigmothermic character of G. galloti, and thus its habitat | 97 | helio- and thigmothermic character of G. galloti, and thus its habitat | ||
| 98 | use. A general suggestion of this study is that road margins create | 98 | use. A general suggestion of this study is that road margins create | ||
| 99 | corridors that may be used by native lizards for dispersal through | 99 | corridors that may be used by native lizards for dispersal through | ||
| 100 | inhospitable forest matrix. The high road density in Tenerife may have | 100 | inhospitable forest matrix. The high road density in Tenerife may have | ||
| 101 | negative implications for the conservation of the genetic variability | 101 | negative implications for the conservation of the genetic variability | ||
| 102 | of G. galloti. At the island scale, increased communication between | 102 | of G. galloti. At the island scale, increased communication between | ||
| 103 | lizard populations through road corridors might increase | 103 | lizard populations through road corridors might increase | ||
| 104 | homogenization of the gene pool. Ecological processes in which this | 104 | homogenization of the gene pool. Ecological processes in which this | ||
| 105 | lizard plays important roles may also experience changes along road | 105 | lizard plays important roles may also experience changes along road | ||
| 106 | edges.", | 106 | edges.", | ||
| 107 | "notes_translated": { | 107 | "notes_translated": { | ||
| 108 | "en": "Transportation infrastructure is a main cause of | 108 | "en": "Transportation infrastructure is a main cause of | ||
| 109 | environmental change in forest landscapes worldwide. In the Canary | 109 | environmental change in forest landscapes worldwide. In the Canary | ||
| 110 | Islands, a dense road system fragment the native Canarian pine and | 110 | Islands, a dense road system fragment the native Canarian pine and | ||
| 111 | laurel forests causing potential changes in population densities of | 111 | laurel forests causing potential changes in population densities of | ||
| 112 | endemic lacertid lizards (genus Gallotia). Our aim was to assess road | 112 | endemic lacertid lizards (genus Gallotia). Our aim was to assess road | ||
| 113 | edge effects on relative abundance patterns of the endemic Gallotia | 113 | edge effects on relative abundance patterns of the endemic Gallotia | ||
| 114 | galloti in both forests. We also explored the species\u2013habitat | 114 | galloti in both forests. We also explored the species\u2013habitat | ||
| 115 | relationships in this road-fragmentation context. We found that lizard | 115 | relationships in this road-fragmentation context. We found that lizard | ||
| 116 | relative density in relation to road edges differed between forests. | 116 | relative density in relation to road edges differed between forests. | ||
| 117 | Lizards were more abundant along edges and leeward interior, but | 117 | Lizards were more abundant along edges and leeward interior, but | ||
| 118 | virtually absent from the interior of the windward laurel forest. In | 118 | virtually absent from the interior of the windward laurel forest. In | ||
| 119 | the pine forest, lizards were present at three distances from edge, | 119 | the pine forest, lizards were present at three distances from edge, | ||
| 120 | with a net decrease in abundance from edge to interior. These patterns | 120 | with a net decrease in abundance from edge to interior. These patterns | ||
| 121 | may be explained partly by differences in vegetation structure | 121 | may be explained partly by differences in vegetation structure | ||
| 122 | regarding road proximity in each forest that potentially affect the | 122 | regarding road proximity in each forest that potentially affect the | ||
| 123 | helio- and thigmothermic character of G. galloti, and thus its habitat | 123 | helio- and thigmothermic character of G. galloti, and thus its habitat | ||
| 124 | use. A general suggestion of this study is that road margins create | 124 | use. A general suggestion of this study is that road margins create | ||
| 125 | corridors that may be used by native lizards for dispersal through | 125 | corridors that may be used by native lizards for dispersal through | ||
| 126 | inhospitable forest matrix. The high road density in Tenerife may have | 126 | inhospitable forest matrix. The high road density in Tenerife may have | ||
| 127 | negative implications for the conservation of the genetic variability | 127 | negative implications for the conservation of the genetic variability | ||
| 128 | of G. galloti. At the island scale, increased communication between | 128 | of G. galloti. At the island scale, increased communication between | ||
| 129 | lizard populations through road corridors might increase | 129 | lizard populations through road corridors might increase | ||
| 130 | homogenization of the gene pool. Ecological processes in which this | 130 | homogenization of the gene pool. Ecological processes in which this | ||
| 131 | lizard plays important roles may also experience changes along road | 131 | lizard plays important roles may also experience changes along road | ||
| 132 | edges.", | 132 | edges.", | ||
| 133 | "es": "Transportation infrastructure is a main cause of | 133 | "es": "Transportation infrastructure is a main cause of | ||
| 134 | environmental change in forest landscapes worldwide. In the Canary | 134 | environmental change in forest landscapes worldwide. In the Canary | ||
| 135 | Islands, a dense road system fragment the native Canarian pine and | 135 | Islands, a dense road system fragment the native Canarian pine and | ||
| 136 | laurel forests causing potential changes in population densities of | 136 | laurel forests causing potential changes in population densities of | ||
| 137 | endemic lacertid lizards (genus Gallotia). Our aim was to assess road | 137 | endemic lacertid lizards (genus Gallotia). Our aim was to assess road | ||
| 138 | edge effects on relative abundance patterns of the endemic Gallotia | 138 | edge effects on relative abundance patterns of the endemic Gallotia | ||
| 139 | galloti in both forests. We also explored the species\u2013habitat | 139 | galloti in both forests. We also explored the species\u2013habitat | ||
| 140 | relationships in this road-fragmentation context. We found that lizard | 140 | relationships in this road-fragmentation context. We found that lizard | ||
| 141 | relative density in relation to road edges differed between forests. | 141 | relative density in relation to road edges differed between forests. | ||
| 142 | Lizards were more abundant along edges and leeward interior, but | 142 | Lizards were more abundant along edges and leeward interior, but | ||
| 143 | virtually absent from the interior of the windward laurel forest. In | 143 | virtually absent from the interior of the windward laurel forest. In | ||
| 144 | the pine forest, lizards were present at three distances from edge, | 144 | the pine forest, lizards were present at three distances from edge, | ||
| 145 | with a net decrease in abundance from edge to interior. These patterns | 145 | with a net decrease in abundance from edge to interior. These patterns | ||
| 146 | may be explained partly by differences in vegetation structure | 146 | may be explained partly by differences in vegetation structure | ||
| 147 | regarding road proximity in each forest that potentially affect the | 147 | regarding road proximity in each forest that potentially affect the | ||
| 148 | helio- and thigmothermic character of G. galloti, and thus its habitat | 148 | helio- and thigmothermic character of G. galloti, and thus its habitat | ||
| 149 | use. A general suggestion of this study is that road margins create | 149 | use. A general suggestion of this study is that road margins create | ||
| 150 | corridors that may be used by native lizards for dispersal through | 150 | corridors that may be used by native lizards for dispersal through | ||
| 151 | inhospitable forest matrix. The high road density in Tenerife may have | 151 | inhospitable forest matrix. The high road density in Tenerife may have | ||
| 152 | negative implications for the conservation of the genetic variability | 152 | negative implications for the conservation of the genetic variability | ||
| 153 | of G. galloti. At the island scale, increased communication between | 153 | of G. galloti. At the island scale, increased communication between | ||
| 154 | lizard populations through road corridors might increase | 154 | lizard populations through road corridors might increase | ||
| 155 | homogenization of the gene pool. Ecological processes in which this | 155 | homogenization of the gene pool. Ecological processes in which this | ||
| 156 | lizard plays important roles may also experience changes along road | 156 | lizard plays important roles may also experience changes along road | ||
| 157 | edges." | 157 | edges." | ||
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| 237 | "name": "Acceso al recurso", | 237 | "name": "Acceso al recurso", | ||
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| 246 | "status": "http://purl.org/adms/status/Completed", | 246 | "status": "http://purl.org/adms/status/Completed", | ||
| 247 | "url": | 247 | "url": | ||
| 248 | "https://link.springer.com/article/10.1007/s10531-007-9154-x", | 248 | "https://link.springer.com/article/10.1007/s10531-007-9154-x", | ||
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| 256 | 27.64]]]}", | 256 | 27.64]]]}", | ||
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| 265 | "uri": | 265 | "uri": | ||
| 266 | ttp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a" | 266 | ttp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a" | ||
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| 270 | "spatial_uri": | 270 | "spatial_uri": | ||
| 271 | tp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a", | 271 | tp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a", | ||
| 272 | "state": "active", | 272 | "state": "active", | ||
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| 277 | 277 | ||||
| 278 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | 278 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | ||
| 279 | ], | 279 | ], | ||
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| 281 | { | 281 | { | ||
| 282 | "display_name": "efectos-de-borde-y-margen-asociados-a-la", | 282 | "display_name": "efectos-de-borde-y-margen-asociados-a-la", | ||
| 283 | "id": "430b41a3-9e45-421d-92e3-00d12878405d", | 283 | "id": "430b41a3-9e45-421d-92e3-00d12878405d", | ||
| 284 | "name": "efectos-de-borde-y-margen-asociados-a-la", | 284 | "name": "efectos-de-borde-y-margen-asociados-a-la", | ||
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| 290 | "id": "627f9c0a-a199-4c69-b563-0c8d626e3194", | 290 | "id": "627f9c0a-a199-4c69-b563-0c8d626e3194", | ||
| 291 | "name": "fragmentacion", | 291 | "name": "fragmentacion", | ||
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| 294 | } | 294 | } | ||
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| 297 | "especies_silvestres" | 297 | "especies_silvestres" | ||
| 298 | ], | 298 | ], | ||
| 299 | "theme_es": [ | 299 | "theme_es": [ | ||
| 300 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | 300 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | ||
| 301 | ], | 301 | ], | ||
| 302 | "title": "Road edge effect on the abundance of the lizard Gallotia | 302 | "title": "Road edge effect on the abundance of the lizard Gallotia | ||
| 303 | galloti (Sauria: Lacertidae) in two Canary Islands forests.", | 303 | galloti (Sauria: Lacertidae) in two Canary Islands forests.", | ||
| 304 | "title_translated": { | 304 | "title_translated": { | ||
| 305 | "en": "", | 305 | "en": "", | ||
| 306 | "es": "Road edge effect on the abundance of the lizard Gallotia | 306 | "es": "Road edge effect on the abundance of the lizard Gallotia | ||
| 307 | galloti (Sauria: Lacertidae) in two Canary Islands forests." | 307 | galloti (Sauria: Lacertidae) in two Canary Islands forests." | ||
| 308 | }, | 308 | }, | ||
| 309 | "topic": | 309 | "topic": | ||
| 310 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | 310 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | ||
| 311 | "type": "dataset", | 311 | "type": "dataset", | ||
| 312 | "url": | 312 | "url": | ||
| 313 | //iepnb.es:443/catalogo/dataset/e1eada9b-4049-506d-a35c-30d1b134ae9e", | 313 | //iepnb.es:443/catalogo/dataset/e1eada9b-4049-506d-a35c-30d1b134ae9e", | ||
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| 316 | "en": "", | 316 | "en": "", | ||
| 317 | "es": "" | 317 | "es": "" | ||
| 318 | } | 318 | } | ||
| 319 | } | 319 | } |