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) en On the road: the different impacts of motorized traffic on animal populations.
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| 83 | the aim to plan the most suitable mitigation measures. The main | 97 | the aim to plan the most suitable mitigation measures. The main | ||
| 84 | objective of this thesis was to produce a relevant contribution to | 98 | objective of this thesis was to produce a relevant contribution to | ||
| 85 | Road ecology, suggesting how to investigate the mechanisms potentially | 99 | Road ecology, suggesting how to investigate the mechanisms potentially | ||
| 86 | determining road-kills, barrier effects and the effectiveness of | 100 | determining road-kills, barrier effects and the effectiveness of | ||
| 87 | mitigation measures, but also increasing the knowledge about | 101 | mitigation measures, but also increasing the knowledge about | ||
| 88 | little-known road-related impacts such as changes in behavior and | 102 | little-known road-related impacts such as changes in behavior and | ||
| 89 | biological invasions. The first chapter of this thesis aimed to | 103 | biological invasions. The first chapter of this thesis aimed to | ||
| 90 | determine the life history, temporal and spatial factors affecting | 104 | determine the life history, temporal and spatial factors affecting | ||
| 91 | road-kill probability for vertebrate species in a Mediterranean | 105 | road-kill probability for vertebrate species in a Mediterranean | ||
| 92 | landscape (Do\u00f1ana Natural Park, southwestern Spain). Abundant | 106 | landscape (Do\u00f1ana Natural Park, southwestern Spain). Abundant | ||
| 93 | species were more road-killed than rare species, but also ectotherms | 107 | species were more road-killed than rare species, but also ectotherms | ||
| 94 | had higher road-kill probability than endotherms (including birds). | 108 | had higher road-kill probability than endotherms (including birds). | ||
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| 100 | study investigating the factors determining barrier effect along a | 114 | study investigating the factors determining barrier effect along a | ||
| 101 | heterogeneous roadnetwork (ie paved and unpaved roads with different | 115 | heterogeneous roadnetwork (ie paved and unpaved roads with different | ||
| 102 | traffic intensity). Our study area \u2026\n Palabras clave: | 116 | traffic intensity). Our study area \u2026\n Palabras clave: | ||
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| 109 | approximations. Contrarily, the primary purpose of Road ecology should | 123 | approximations. Contrarily, the primary purpose of Road ecology should | ||
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| 116 | little-known road-related impacts such as changes in behavior and | 130 | little-known road-related impacts such as changes in behavior and | ||
| 117 | biological invasions. The first chapter of this thesis aimed to | 131 | biological invasions. The first chapter of this thesis aimed to | ||
| 118 | determine the life history, temporal and spatial factors affecting | 132 | determine the life history, temporal and spatial factors affecting | ||
| 119 | road-kill probability for vertebrate species in a Mediterranean | 133 | road-kill probability for vertebrate species in a Mediterranean | ||
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| 121 | species were more road-killed than rare species, but also ectotherms | 135 | species were more road-killed than rare species, but also ectotherms | ||
| 122 | had higher road-kill probability than endotherms (including birds). | 136 | had higher road-kill probability than endotherms (including birds). | ||
| 123 | Species abundance was also the most relevant factor determining | 137 | Species abundance was also the most relevant factor determining | ||
| 124 | road-kill probability (both temporally and spatially) for different | 138 | road-kill probability (both temporally and spatially) for different | ||
| 125 | functional groups of species (for example resident, breeding, | 139 | functional groups of species (for example resident, breeding, | ||
| 126 | wintering and migrant birds in the temporal analysis and small | 140 | wintering and migrant birds in the temporal analysis and small | ||
| 127 | passerines in the spatial analysis). The second chapter was the first | 141 | passerines in the spatial analysis). The second chapter was the first | ||
| 128 | study investigating the factors determining barrier effect along a | 142 | study investigating the factors determining barrier effect along a | ||
| 129 | heterogeneous roadnetwork (ie paved and unpaved roads with different | 143 | heterogeneous roadnetwork (ie paved and unpaved roads with different | ||
| 130 | traffic intensity). Our study area \u2026", | 144 | traffic intensity). Our study area \u2026", | ||
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| 135 | approximations. Contrarily, the primary purpose of Road ecology should | 149 | approximations. Contrarily, the primary purpose of Road ecology should | ||
| 136 | be to determine the mechanisms producing road-related impacts, with | 150 | be to determine the mechanisms producing road-related impacts, with | ||
| 137 | the aim to plan the most suitable mitigation measures. The main | 151 | the aim to plan the most suitable mitigation measures. The main | ||
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| 309 | "title": "On the road: the different impacts of motorized traffic on | 323 | "title": "On the road: the different impacts of motorized traffic on | ||
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