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| 4 | "alternate_identifier": "DOI: 10.1371/journal.pone.0151500", | 4 | "alternate_identifier": "DOI: 10.1371/journal.pone.0151500", | ||
| 5 | "author": "Ascens\u00e3o, F., Mata, C., Malo, J.E., Ruiz-Capillas, | 5 | "author": "Ascens\u00e3o, F., Mata, C., Malo, J.E., Ruiz-Capillas, | ||
| 6 | P., Silva, C., Silva, A.P., Santos-Reis, M. y Fernandes, C.", | 6 | P., Silva, C., Silva, A.P., Santos-Reis, M. y Fernandes, C.", | ||
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| 8 | Ruiz-Capillas, P., Silva, C., Silva, A.P., Santos-Reis, M. y | 8 | Ruiz-Capillas, P., Silva, C., Silva, A.P., Santos-Reis, M. y | ||
| 9 | Fernandes, C.", | 9 | Fernandes, C.", | ||
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| 60 | "lineage_source": [ | 60 | "lineage_source": [ | ||
| 61 | "PLoS ONE. Vol. 11", | 61 | "PLoS ONE. Vol. 11", | ||
| 62 | "Num. 3", | 62 | "Num. 3", | ||
| 63 | "pags. e015150" | 63 | "pags. e015150" | ||
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| 82 | "name": "f53abddd-3887-5c31-85f8-e00ed6679d09", | 82 | "name": "f53abddd-3887-5c31-85f8-e00ed6679d09", | ||
| 83 | "notes": "Road barrier effect is among the foremost negative impacts | 83 | "notes": "Road barrier effect is among the foremost negative impacts | ||
| 84 | of roads on wildlife. Knowledge of the factors responsible for the | 84 | of roads on wildlife. Knowledge of the factors responsible for the | ||
| 85 | road barrier effect is crucial to understand and predict species\u2019 | 85 | road barrier effect is crucial to understand and predict species\u2019 | ||
| 86 | responses to roads, and to improve mitigation measures in the context | 86 | responses to roads, and to improve mitigation measures in the context | ||
| 87 | of management and conservation. We built a set of hypothesis aiming to | 87 | of management and conservation. We built a set of hypothesis aiming to | ||
| 88 | infer the most probable cause of road barrier effect (traffic effect | 88 | infer the most probable cause of road barrier effect (traffic effect | ||
| 89 | or road surface avoidance), while controlling for the potentially | 89 | or road surface avoidance), while controlling for the potentially | ||
| 90 | confounding effects road width, traffic volume and road age. The wood | 90 | confounding effects road width, traffic volume and road age. The wood | ||
| 91 | mouse Apodemus sylvaticus was used as a model species of small and | 91 | mouse Apodemus sylvaticus was used as a model species of small and | ||
| 92 | forest-dwelling mammals, which are more likely to be affected by gaps | 92 | forest-dwelling mammals, which are more likely to be affected by gaps | ||
| 93 | in cover such as those resulting from road construction. We confront | 93 | in cover such as those resulting from road construction. We confront | ||
| 94 | genetic patterns from opposite and same roadsides from samples of | 94 | genetic patterns from opposite and same roadsides from samples of | ||
| 95 | three highways and used computer simulations to infer migration rates | 95 | three highways and used computer simulations to infer migration rates | ||
| 96 | between opposite roadsides. Genetic patterns from 302 samples (ca. 100 | 96 | between opposite roadsides. Genetic patterns from 302 samples (ca. 100 | ||
| 97 | per highway) suggest that the highway barrier effect for wood mouse is | 97 | per highway) suggest that the highway barrier effect for wood mouse is | ||
| 98 | due to road surface avoidance. However, from the simulations we | 98 | due to road surface avoidance. However, from the simulations we | ||
| 99 | estimated a migration rate of about 5% between opposite roadsides, | 99 | estimated a migration rate of about 5% between opposite roadsides, | ||
| 100 | indicating that some limited gene flow across highways does occur. To | 100 | indicating that some limited gene flow across highways does occur. To | ||
| 101 | reduce highway impact on population genetic diversity and structure, | 101 | reduce highway impact on population genetic diversity and structure, | ||
| 102 | possible mitigation measures could include retrofitting of culverts | 102 | possible mitigation measures could include retrofitting of culverts | ||
| 103 | and underpasses to increase their attractiveness and facilitate their | 103 | and underpasses to increase their attractiveness and facilitate their | ||
| 104 | use by wood mice and other species, and setting aside roadside strips | 104 | use by wood mice and other species, and setting aside roadside strips | ||
| 105 | without vegetation removal to facilitate establishment and dispersal | 105 | without vegetation removal to facilitate establishment and dispersal | ||
| 106 | of small mammals.\n Palabras clave: Barrier, Mammal", | 106 | of small mammals.\n Palabras clave: Barrier, Mammal", | ||
| 107 | "notes_translated": { | 107 | "notes_translated": { | ||
| 108 | "en": "Road barrier effect is among the foremost negative impacts | 108 | "en": "Road barrier effect is among the foremost negative impacts | ||
| 109 | of roads on wildlife. Knowledge of the factors responsible for the | 109 | of roads on wildlife. Knowledge of the factors responsible for the | ||
| 110 | road barrier effect is crucial to understand and predict species\u2019 | 110 | road barrier effect is crucial to understand and predict species\u2019 | ||
| 111 | responses to roads, and to improve mitigation measures in the context | 111 | responses to roads, and to improve mitigation measures in the context | ||
| 112 | of management and conservation. We built a set of hypothesis aiming to | 112 | of management and conservation. We built a set of hypothesis aiming to | ||
| 113 | infer the most probable cause of road barrier effect (traffic effect | 113 | infer the most probable cause of road barrier effect (traffic effect | ||
| 114 | or road surface avoidance), while controlling for the potentially | 114 | or road surface avoidance), while controlling for the potentially | ||
| 115 | confounding effects road width, traffic volume and road age. The wood | 115 | confounding effects road width, traffic volume and road age. The wood | ||
| 116 | mouse Apodemus sylvaticus was used as a model species of small and | 116 | mouse Apodemus sylvaticus was used as a model species of small and | ||
| 117 | forest-dwelling mammals, which are more likely to be affected by gaps | 117 | forest-dwelling mammals, which are more likely to be affected by gaps | ||
| 118 | in cover such as those resulting from road construction. We confront | 118 | in cover such as those resulting from road construction. We confront | ||
| 119 | genetic patterns from opposite and same roadsides from samples of | 119 | genetic patterns from opposite and same roadsides from samples of | ||
| 120 | three highways and used computer simulations to infer migration rates | 120 | three highways and used computer simulations to infer migration rates | ||
| 121 | between opposite roadsides. Genetic patterns from 302 samples (ca. 100 | 121 | between opposite roadsides. Genetic patterns from 302 samples (ca. 100 | ||
| 122 | per highway) suggest that the highway barrier effect for wood mouse is | 122 | per highway) suggest that the highway barrier effect for wood mouse is | ||
| 123 | due to road surface avoidance. However, from the simulations we | 123 | due to road surface avoidance. However, from the simulations we | ||
| 124 | estimated a migration rate of about 5% between opposite roadsides, | 124 | estimated a migration rate of about 5% between opposite roadsides, | ||
| 125 | indicating that some limited gene flow across highways does occur. To | 125 | indicating that some limited gene flow across highways does occur. To | ||
| 126 | reduce highway impact on population genetic diversity and structure, | 126 | reduce highway impact on population genetic diversity and structure, | ||
| 127 | possible mitigation measures could include retrofitting of culverts | 127 | possible mitigation measures could include retrofitting of culverts | ||
| 128 | and underpasses to increase their attractiveness and facilitate their | 128 | and underpasses to increase their attractiveness and facilitate their | ||
| 129 | use by wood mice and other species, and setting aside roadside strips | 129 | use by wood mice and other species, and setting aside roadside strips | ||
| 130 | without vegetation removal to facilitate establishment and dispersal | 130 | without vegetation removal to facilitate establishment and dispersal | ||
| 131 | of small mammals.", | 131 | of small mammals.", | ||
| 132 | "es": "Road barrier effect is among the foremost negative impacts | 132 | "es": "Road barrier effect is among the foremost negative impacts | ||
| 133 | of roads on wildlife. Knowledge of the factors responsible for the | 133 | of roads on wildlife. Knowledge of the factors responsible for the | ||
| 134 | road barrier effect is crucial to understand and predict species\u2019 | 134 | road barrier effect is crucial to understand and predict species\u2019 | ||
| 135 | responses to roads, and to improve mitigation measures in the context | 135 | responses to roads, and to improve mitigation measures in the context | ||
| 136 | of management and conservation. We built a set of hypothesis aiming to | 136 | of management and conservation. We built a set of hypothesis aiming to | ||
| 137 | infer the most probable cause of road barrier effect (traffic effect | 137 | infer the most probable cause of road barrier effect (traffic effect | ||
| 138 | or road surface avoidance), while controlling for the potentially | 138 | or road surface avoidance), while controlling for the potentially | ||
| 139 | confounding effects road width, traffic volume and road age. The wood | 139 | confounding effects road width, traffic volume and road age. The wood | ||
| 140 | mouse Apodemus sylvaticus was used as a model species of small and | 140 | mouse Apodemus sylvaticus was used as a model species of small and | ||
| 141 | forest-dwelling mammals, which are more likely to be affected by gaps | 141 | forest-dwelling mammals, which are more likely to be affected by gaps | ||
| 142 | in cover such as those resulting from road construction. We confront | 142 | in cover such as those resulting from road construction. We confront | ||
| 143 | genetic patterns from opposite and same roadsides from samples of | 143 | genetic patterns from opposite and same roadsides from samples of | ||
| 144 | three highways and used computer simulations to infer migration rates | 144 | three highways and used computer simulations to infer migration rates | ||
| 145 | between opposite roadsides. Genetic patterns from 302 samples (ca. 100 | 145 | between opposite roadsides. Genetic patterns from 302 samples (ca. 100 | ||
| 146 | per highway) suggest that the highway barrier effect for wood mouse is | 146 | per highway) suggest that the highway barrier effect for wood mouse is | ||
| 147 | due to road surface avoidance. However, from the simulations we | 147 | due to road surface avoidance. However, from the simulations we | ||
| 148 | estimated a migration rate of about 5% between opposite roadsides, | 148 | estimated a migration rate of about 5% between opposite roadsides, | ||
| 149 | indicating that some limited gene flow across highways does occur. To | 149 | indicating that some limited gene flow across highways does occur. To | ||
| 150 | reduce highway impact on population genetic diversity and structure, | 150 | reduce highway impact on population genetic diversity and structure, | ||
| 151 | possible mitigation measures could include retrofitting of culverts | 151 | possible mitigation measures could include retrofitting of culverts | ||
| 152 | and underpasses to increase their attractiveness and facilitate their | 152 | and underpasses to increase their attractiveness and facilitate their | ||
| 153 | use by wood mice and other species, and setting aside roadside strips | 153 | use by wood mice and other species, and setting aside roadside strips | ||
| 154 | without vegetation removal to facilitate establishment and dispersal | 154 | without vegetation removal to facilitate establishment and dispersal | ||
| 155 | of small mammals.\n Palabras clave: Barrier, Mammal" | 155 | of small mammals.\n Palabras clave: Barrier, Mammal" | ||
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| 182 | Ministerio para la Transici\u00f3n Ecol\u00f3gica y el Reto | 182 | Ministerio para la Transici\u00f3n Ecol\u00f3gica y el Reto | ||
| 183 | Demogr\u00e1fico", | 183 | Demogr\u00e1fico", | ||
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| 312 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | 312 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | ||
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| 314 | "title": "Disentangle the causes of the road barrier effect in small | 314 | "title": "Disentangle the causes of the road barrier effect in small | ||
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| 316 | "title_translated": { | 316 | "title_translated": { | ||
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