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| 4 | "alternate_identifier": "DOI: 10.1016/j.landurbplan.2018.06.007", | 4 | "alternate_identifier": "DOI: 10.1016/j.landurbplan.2018.06.007", | ||
| 5 | "author": "Carvalho, F., Louren\u00e7o, A., Carvalho, R., Alves, | 5 | "author": "Carvalho, F., Louren\u00e7o, A., Carvalho, R., Alves, | ||
| 6 | P.C., Mira, A. y Beja, P.", | 6 | P.C., Mira, A. y Beja, P.", | ||
| 7 | "author_name": "Carvalho, F., Louren\u00e7o, A., Carvalho, R., | 7 | "author_name": "Carvalho, F., Louren\u00e7o, A., Carvalho, R., | ||
| 8 | Alves, P.C., Mira, A. y Beja, P.", | 8 | Alves, P.C., Mira, A. y Beja, P.", | ||
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| 33 | "created": "2025-05-23", | 33 | "created": "2025-05-23", | ||
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| 36 | "name": "Carvalho, F., Louren\u00e7o, A., Carvalho, R., Alves, | 36 | "name": "Carvalho, F., Louren\u00e7o, A., Carvalho, R., Alves, | ||
| 37 | P.C., Mira, A. y Beja, P." | 37 | P.C., Mira, A. y Beja, P." | ||
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| 60 | "Landscape and Urban Planning. Vol. 178", | 60 | "Landscape and Urban Planning. Vol. 178", | ||
| 61 | "pags. 217-227" | 61 | "pags. 217-227" | ||
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| 79 | "modified": "2026-06-23", | 79 | "modified": "2026-06-23", | ||
| 80 | "name": "dd2ec434-eb84-5ee8-91c1-4ea6b894262d", | 80 | "name": "dd2ec434-eb84-5ee8-91c1-4ea6b894262d", | ||
| 81 | "notes": "Roads represent barriers to animal movement due to | 81 | "notes": "Roads represent barriers to animal movement due to | ||
| 82 | physical obstruction, mortality, or behavioural avoidance. The | 82 | physical obstruction, mortality, or behavioural avoidance. The | ||
| 83 | population-level consequences of such constraints remain poorly | 83 | population-level consequences of such constraints remain poorly | ||
| 84 | understood, because successful crossings may be sufficient to | 84 | understood, because successful crossings may be sufficient to | ||
| 85 | counteract negative effects of fragmentation and isolation. Here we | 85 | counteract negative effects of fragmentation and isolation. Here we | ||
| 86 | examine the individual- and population-level barrier effects of a | 86 | examine the individual- and population-level barrier effects of a | ||
| 87 | motorway on the common genet Genetta genetta, by combining long-term | 87 | motorway on the common genet Genetta genetta, by combining long-term | ||
| 88 | road mortality, radio tracking and population genetics data. We found | 88 | road mortality, radio tracking and population genetics data. We found | ||
| 89 | 84 genets killed at roads, of which 68% were subadults, with a peak | 89 | 84 genets killed at roads, of which 68% were subadults, with a peak | ||
| 90 | mortality during the dispersal period. The home ranges of resident | 90 | mortality during the dispersal period. The home ranges of resident | ||
| 91 | adults often bordered the motorway, and their sizes were similar close | 91 | adults often bordered the motorway, and their sizes were similar close | ||
| 92 | to (314 ha, n = 9) and far from (258 ha, n = 10) the motorway. The | 92 | to (314 ha, n = 9) and far from (258 ha, n = 10) the motorway. The | ||
| 93 | crossing rate was much higher for dispersing subadults (4.1 | 93 | crossing rate was much higher for dispersing subadults (4.1 | ||
| 94 | crossings/100 nights, n = 3) than for resident adults living near the | 94 | crossings/100 nights, n = 3) than for resident adults living near the | ||
| 95 | motorway (0.2 crossings/100 nights, n = 9), though the number of | 95 | motorway (0.2 crossings/100 nights, n = 9), though the number of | ||
| 96 | tracked subadults crossing the motorway was low. Genetic kinship | 96 | tracked subadults crossing the motorway was low. Genetic kinship | ||
| 97 | analysis revealed seven crossings based on father-offspring and | 97 | analysis revealed seven crossings based on father-offspring and | ||
| 98 | half-sibling relationships. There was no significant genetic | 98 | half-sibling relationships. There was no significant genetic | ||
| 99 | differentiation related to the motorway. The movement of residents | 99 | differentiation related to the motorway. The movement of residents | ||
| 100 | were strongly constrained by the motorway, though gene flow mediated | 100 | were strongly constrained by the motorway, though gene flow mediated | ||
| 101 | by successful crossings, particularly by subadults, likely prevented | 101 | by successful crossings, particularly by subadults, likely prevented | ||
| 102 | genetic differentiation. Genet movements across the motorway were | 102 | genetic differentiation. Genet movements across the motorway were | ||
| 103 | probably facilitated by low traffic flow and the presence of crossing | 103 | probably facilitated by low traffic flow and the presence of crossing | ||
| 104 | structures. Our study implies that evaluating mitigation strategies to | 104 | structures. Our study implies that evaluating mitigation strategies to | ||
| 105 | reduce the barrier effects of roads would benefit from the integration | 105 | reduce the barrier effects of roads would benefit from the integration | ||
| 106 | of mortality, animal behaviour, and population genetics data, to | 106 | of mortality, animal behaviour, and population genetics data, to | ||
| 107 | increase effectiveness and avoid wasting scarce conservation | 107 | increase effectiveness and avoid wasting scarce conservation | ||
| 108 | resources.", | 108 | resources.", | ||
| 109 | "notes_translated": { | 109 | "notes_translated": { | ||
| 110 | "en": "Roads represent barriers to animal movement due to physical | 110 | "en": "Roads represent barriers to animal movement due to physical | ||
| 111 | obstruction, mortality, or behavioural avoidance. The population-level | 111 | obstruction, mortality, or behavioural avoidance. The population-level | ||
| 112 | consequences of such constraints remain poorly understood, because | 112 | consequences of such constraints remain poorly understood, because | ||
| 113 | successful crossings may be sufficient to counteract negative effects | 113 | successful crossings may be sufficient to counteract negative effects | ||
| 114 | of fragmentation and isolation. Here we examine the individual- and | 114 | of fragmentation and isolation. Here we examine the individual- and | ||
| 115 | population-level barrier effects of a motorway on the common | 115 | population-level barrier effects of a motorway on the common | ||
| 116 | genet\u00a0Genetta genetta, by combining long-term road mortality, | 116 | genet\u00a0Genetta genetta, by combining long-term road mortality, | ||
| 117 | radio tracking and population genetics data. We found 84 genets killed | 117 | radio tracking and population genetics data. We found 84 genets killed | ||
| 118 | at roads, of which 68% were subadults, with a peak mortality during | 118 | at roads, of which 68% were subadults, with a peak mortality during | ||
| 119 | the dispersal period. The home ranges of resident adults often | 119 | the dispersal period. The home ranges of resident adults often | ||
| 120 | bordered the motorway, and their sizes were similar close to | 120 | bordered the motorway, and their sizes were similar close to | ||
| 121 | (314\u202fha, n\u202f=\u202f9) and far from (258\u202fha, | 121 | (314\u202fha, n\u202f=\u202f9) and far from (258\u202fha, | ||
| 122 | n\u202f=\u202f10) the motorway. The crossing rate was much higher for | 122 | n\u202f=\u202f10) the motorway. The crossing rate was much higher for | ||
| 123 | dispersing subadults (4.1 crossings/100 nights, n\u202f=\u202f3) than | 123 | dispersing subadults (4.1 crossings/100 nights, n\u202f=\u202f3) than | ||
| 124 | for resident adults living near the motorway (0.2 crossings/100 | 124 | for resident adults living near the motorway (0.2 crossings/100 | ||
| 125 | nights, n\u202f=\u202f9), though the number of tracked subadults | 125 | nights, n\u202f=\u202f9), though the number of tracked subadults | ||
| 126 | crossing the motorway was low. Genetic kinship analysis revealed seven | 126 | crossing the motorway was low. Genetic kinship analysis revealed seven | ||
| 127 | crossings based on father-offspring and half-sibling relationships. | 127 | crossings based on father-offspring and half-sibling relationships. | ||
| 128 | There was no significant\u00a0genetic differentiation\u00a0related to | 128 | There was no significant\u00a0genetic differentiation\u00a0related to | ||
| 129 | the motorway. The movement of residents were strongly constrained by | 129 | the motorway. The movement of residents were strongly constrained by | ||
| 130 | the motorway, though gene flow mediated by successful crossings, | 130 | the motorway, though gene flow mediated by successful crossings, | ||
| 131 | particularly by subadults, likely prevented genetic differentiation. | 131 | particularly by subadults, likely prevented genetic differentiation. | ||
| 132 | Genet movements across the motorway were probably facilitated by low | 132 | Genet movements across the motorway were probably facilitated by low | ||
| 133 | traffic flow and the presence of crossing structures. Our study | 133 | traffic flow and the presence of crossing structures. Our study | ||
| 134 | implies that evaluating mitigation strategies to reduce the barrier | 134 | implies that evaluating mitigation strategies to reduce the barrier | ||
| 135 | effects of roads would benefit from the integration of mortality, | 135 | effects of roads would benefit from the integration of mortality, | ||
| 136 | animal behaviour, and population genetics data, to increase | 136 | animal behaviour, and population genetics data, to increase | ||
| 137 | effectiveness and avoid wasting scarce conservation resources.", | 137 | effectiveness and avoid wasting scarce conservation resources.", | ||
| 138 | "es": "Roads represent barriers to animal movement due to physical | 138 | "es": "Roads represent barriers to animal movement due to physical | ||
| 139 | obstruction, mortality, or behavioural avoidance. The population-level | 139 | obstruction, mortality, or behavioural avoidance. The population-level | ||
| 140 | consequences of such constraints remain poorly understood, because | 140 | consequences of such constraints remain poorly understood, because | ||
| 141 | successful crossings may be sufficient to counteract negative effects | 141 | successful crossings may be sufficient to counteract negative effects | ||
| 142 | of fragmentation and isolation. Here we examine the individual- and | 142 | of fragmentation and isolation. Here we examine the individual- and | ||
| 143 | population-level barrier effects of a motorway on the common genet | 143 | population-level barrier effects of a motorway on the common genet | ||
| 144 | Genetta genetta, by combining long-term road mortality, radio tracking | 144 | Genetta genetta, by combining long-term road mortality, radio tracking | ||
| 145 | and population genetics data. We found 84 genets killed at roads, of | 145 | and population genetics data. We found 84 genets killed at roads, of | ||
| 146 | which 68% were subadults, with a peak mortality during the dispersal | 146 | which 68% were subadults, with a peak mortality during the dispersal | ||
| 147 | period. The home ranges of resident adults often bordered the | 147 | period. The home ranges of resident adults often bordered the | ||
| 148 | motorway, and their sizes were similar close to (314 ha, n = 9) and | 148 | motorway, and their sizes were similar close to (314 ha, n = 9) and | ||
| 149 | far from (258 ha, n = 10) the motorway. The crossing rate was much | 149 | far from (258 ha, n = 10) the motorway. The crossing rate was much | ||
| 150 | higher for dispersing subadults (4.1 crossings/100 nights, n = 3) than | 150 | higher for dispersing subadults (4.1 crossings/100 nights, n = 3) than | ||
| 151 | for resident adults living near the motorway (0.2 crossings/100 | 151 | for resident adults living near the motorway (0.2 crossings/100 | ||
| 152 | nights, n = 9), though the number of tracked subadults crossing the | 152 | nights, n = 9), though the number of tracked subadults crossing the | ||
| 153 | motorway was low. Genetic kinship analysis revealed seven crossings | 153 | motorway was low. Genetic kinship analysis revealed seven crossings | ||
| 154 | based on father-offspring and half-sibling relationships. There was no | 154 | based on father-offspring and half-sibling relationships. There was no | ||
| 155 | significant genetic differentiation related to the motorway. The | 155 | significant genetic differentiation related to the motorway. The | ||
| 156 | movement of residents were strongly constrained by the motorway, | 156 | movement of residents were strongly constrained by the motorway, | ||
| 157 | though gene flow mediated by successful crossings, particularly by | 157 | though gene flow mediated by successful crossings, particularly by | ||
| 158 | subadults, likely prevented genetic differentiation. Genet movements | 158 | subadults, likely prevented genetic differentiation. Genet movements | ||
| 159 | across the motorway were probably facilitated by low traffic flow and | 159 | across the motorway were probably facilitated by low traffic flow and | ||
| 160 | the presence of crossing structures. Our study implies that evaluating | 160 | the presence of crossing structures. Our study implies that evaluating | ||
| 161 | mitigation strategies to reduce the barrier effects of roads would | 161 | mitigation strategies to reduce the barrier effects of roads would | ||
| 162 | benefit from the integration of mortality, animal behaviour, and | 162 | benefit from the integration of mortality, animal behaviour, and | ||
| 163 | population genetics data, to increase effectiveness and avoid wasting | 163 | population genetics data, to increase effectiveness and avoid wasting | ||
| 164 | scarce conservation resources." | 164 | scarce conservation resources." | ||
| 165 | }, | 165 | }, | ||
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| 189 | "name": "\u00c1rea de Banco de Datos de la Naturaleza. | 189 | "name": "\u00c1rea de Banco de Datos de la Naturaleza. | ||
| 190 | Direcci\u00f3n General Biodiversidad, Bosques y Desertificaci\u00f3n. | 190 | Direcci\u00f3n General Biodiversidad, Bosques y Desertificaci\u00f3n. | ||
| 191 | Ministerio para la Transici\u00f3n Ecol\u00f3gica y el Reto | 191 | Ministerio para la Transici\u00f3n Ecol\u00f3gica y el Reto | ||
| 192 | Demogr\u00e1fico", | 192 | Demogr\u00e1fico", | ||
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| 201 | Ministerio para la Transici\u00f3n Ecol\u00f3gica y el Reto | 201 | Ministerio para la Transici\u00f3n Ecol\u00f3gica y el Reto | ||
| 202 | Demogr\u00e1fico", | 202 | Demogr\u00e1fico", | ||
| 203 | "publisher_type": | 203 | "publisher_type": | ||
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