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En el instante 25 de junio de 2026, 12:36:41 UTC,
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Modificado el valor del campo
modified
a2026-06-25
en Importance of roadside habitats for biodiversity: what do we know? -
Modificado el valor del campo
modified
del recurso Acceso al recurso a2026-06-25
(anteriormente2026-06-23
) en Importance of roadside habitats for biodiversity: what do we know?
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| 82 | "notes": "In an ever-expanding world, impacts of human activity on | 96 | "notes": "In an ever-expanding world, impacts of human activity on | ||
| 83 | the global environment are inevitable. The construction of roads and | 97 | the global environment are inevitable. The construction of roads and | ||
| 84 | other linear transport infrastructure leads not only to the | 98 | other linear transport infrastructure leads not only to the | ||
| 85 | destruction of habitats, but has long-term impacts on populations and | 99 | destruction of habitats, but has long-term impacts on populations and | ||
| 86 | biodiversity,\n including the introduction of edge and barrier | 100 | biodiversity,\n including the introduction of edge and barrier | ||
| 87 | effects, mortality of individuals in vehicle collisions, facilitation | 101 | effects, mortality of individuals in vehicle collisions, facilitation | ||
| 88 | of invasive species dispersal, and numerous others. On the other hand, | 102 | of invasive species dispersal, and numerous others. On the other hand, | ||
| 89 | roadsides have been found to have positive effects on biodiversity, as | 103 | roadsides have been found to have positive effects on biodiversity, as | ||
| 90 | they can constitute important habitats for some species. Previous | 104 | they can constitute important habitats for some species. Previous | ||
| 91 | studies have quantified negative or positive impacts of roadside | 105 | studies have quantified negative or positive impacts of roadside | ||
| 92 | habitats on select species or under select management regimes, but the | 106 | habitats on select species or under select management regimes, but the | ||
| 93 | grand picture of the importance of roadside habitats for biodiversity | 107 | grand picture of the importance of roadside habitats for biodiversity | ||
| 94 | conservation remains unclear. In EpicRoads, a project by the | 108 | conservation remains unclear. In EpicRoads, a project by the | ||
| 95 | Conference of European Directors of Roads (CEDR), we aimed to quantify | 109 | Conference of European Directors of Roads (CEDR), we aimed to quantify | ||
| 96 | impacts of habitats related to transport infrastructure (HTI) on a | 110 | impacts of habitats related to transport infrastructure (HTI) on a | ||
| 97 | range of taxa through meta-analyses. We used an existing database from | 111 | range of taxa through meta-analyses. We used an existing database from | ||
| 98 | a similar project by the Swedish Mistra Council for Evidence-Based | 112 | a similar project by the Swedish Mistra Council for Evidence-Based | ||
| 99 | Environmental Management (EviEM), while expanding our search to | 113 | Environmental Management (EviEM), while expanding our search to | ||
| 100 | include studies carried out in more recent years. We quantified HTI | 114 | include studies carried out in more recent years. We quantified HTI | ||
| 101 | impacts on species richness, a community-level measure, and on | 115 | impacts on species richness, a community-level measure, and on | ||
| 102 | population abundance, a population-level measure. HTI impacts are | 116 | population abundance, a population-level measure. HTI impacts are | ||
| 103 | measured through variables like road presence (versus absence), | 117 | measured through variables like road presence (versus absence), | ||
| 104 | distance to road, and different variables related to roadside | 118 | distance to road, and different variables related to roadside | ||
| 105 | vegetation and road-related disturbance. Results from the | 119 | vegetation and road-related disturbance. Results from the | ||
| 106 | meta-analyses will be presented to give an overview of what has been | 120 | meta-analyses will be presented to give an overview of what has been | ||
| 107 | found in the past 10 years regarding positive and negative effects of | 121 | found in the past 10 years regarding positive and negative effects of | ||
| 108 | factors related to HTI on all taxa with sufficient data. One of our | 122 | factors related to HTI on all taxa with sufficient data. One of our | ||
| 109 | objectives is to enhance our understanding of the extent to which HTI | 123 | objectives is to enhance our understanding of the extent to which HTI | ||
| 110 | can be beneficial for biodiversity conservation and how observed | 124 | can be beneficial for biodiversity conservation and how observed | ||
| 111 | patterns vary among species and road types. Thus, the results of this | 125 | patterns vary among species and road types. Thus, the results of this | ||
| 112 | study are relevant for making decisions on road construction and | 126 | study are relevant for making decisions on road construction and | ||
| 113 | roadside management, as they offer a multi-species perspective | 127 | roadside management, as they offer a multi-species perspective | ||
| 114 | regarding impacts of HTI. However, in addition, our study will | 128 | regarding impacts of HTI. However, in addition, our study will | ||
| 115 | identify important knowledge gaps that can direct future studies in | 129 | identify important knowledge gaps that can direct future studies in | ||
| 116 | road ecology.", | 130 | road ecology.", | ||
| 117 | "notes_translated": { | 131 | "notes_translated": { | ||
| 118 | "en": "In an ever-expanding world, impacts of human activity on | 132 | "en": "In an ever-expanding world, impacts of human activity on | ||
| 119 | the global environment are inevitable. The construction of roads and | 133 | the global environment are inevitable. The construction of roads and | ||
| 120 | other linear transport infrastructure leads not only to the | 134 | other linear transport infrastructure leads not only to the | ||
| 121 | destruction of habitats, but has long-term impacts on populations and | 135 | destruction of habitats, but has long-term impacts on populations and | ||
| 122 | biodiversity,\nincluding the introduction of edge and barrier effects, | 136 | biodiversity,\nincluding the introduction of edge and barrier effects, | ||
| 123 | mortality of individuals in vehicle collisions, facilitation of | 137 | mortality of individuals in vehicle collisions, facilitation of | ||
| 124 | invasive species dispersal, and numerous others. On the other hand, | 138 | invasive species dispersal, and numerous others. On the other hand, | ||
| 125 | roadsides have been found to have positive effects on biodiversity, as | 139 | roadsides have been found to have positive effects on biodiversity, as | ||
| 126 | they can constitute important habitats for some species. Previous | 140 | they can constitute important habitats for some species. Previous | ||
| 127 | studies have quantified negative or positive impacts of roadside | 141 | studies have quantified negative or positive impacts of roadside | ||
| 128 | habitats on select species or under select management regimes, but the | 142 | habitats on select species or under select management regimes, but the | ||
| 129 | grand picture of the importance of roadside habitats for biodiversity | 143 | grand picture of the importance of roadside habitats for biodiversity | ||
| 130 | conservation remains unclear. In EpicRoads, a project by the | 144 | conservation remains unclear. In EpicRoads, a project by the | ||
| 131 | Conference of European Directors of Roads (CEDR), we aimed to quantify | 145 | Conference of European Directors of Roads (CEDR), we aimed to quantify | ||
| 132 | impacts of habitats related to transport infrastructure (HTI) on a | 146 | impacts of habitats related to transport infrastructure (HTI) on a | ||
| 133 | range of taxa through meta-analyses. We used an existing database from | 147 | range of taxa through meta-analyses. We used an existing database from | ||
| 134 | a similar project by the Swedish Mistra Council for Evidence-Based | 148 | a similar project by the Swedish Mistra Council for Evidence-Based | ||
| 135 | Environmental Management (EviEM), while expanding our search to | 149 | Environmental Management (EviEM), while expanding our search to | ||
| 136 | include studies carried out in more recent years. We quantified HTI | 150 | include studies carried out in more recent years. We quantified HTI | ||
| 137 | impacts on species richness, a community-level measure, and on | 151 | impacts on species richness, a community-level measure, and on | ||
| 138 | population abundance, a population-level measure. HTI impacts are | 152 | population abundance, a population-level measure. HTI impacts are | ||
| 139 | measured through variables like road presence (versus absence), | 153 | measured through variables like road presence (versus absence), | ||
| 140 | distance to road, and different variables related to roadside | 154 | distance to road, and different variables related to roadside | ||
| 141 | vegetation and road-related disturbance. Results from the | 155 | vegetation and road-related disturbance. Results from the | ||
| 142 | meta-analyses will be presented to give an overview of what has been | 156 | meta-analyses will be presented to give an overview of what has been | ||
| 143 | found in the past 10 years regarding positive and negative effects of | 157 | found in the past 10 years regarding positive and negative effects of | ||
| 144 | factors related to HTI on all taxa with sufficient data. One of our | 158 | factors related to HTI on all taxa with sufficient data. One of our | ||
| 145 | objectives is to enhance our understanding of the extent to which HTI | 159 | objectives is to enhance our understanding of the extent to which HTI | ||
| 146 | can be beneficial for biodiversity conservation and how observed | 160 | can be beneficial for biodiversity conservation and how observed | ||
| 147 | patterns vary among species and road types. Thus, the results of this | 161 | patterns vary among species and road types. Thus, the results of this | ||
| 148 | study are relevant for making decisions on road construction and | 162 | study are relevant for making decisions on road construction and | ||
| 149 | roadside management, as they offer a multi-species perspective | 163 | roadside management, as they offer a multi-species perspective | ||
| 150 | regarding impacts of HTI. However, in addition, our study will | 164 | regarding impacts of HTI. However, in addition, our study will | ||
| 151 | identify important knowledge gaps that can direct future studies in | 165 | identify important knowledge gaps that can direct future studies in | ||
| 152 | road ecology.", | 166 | road ecology.", | ||
| 153 | "es": "In an ever-expanding world, impacts of human activity on | 167 | "es": "In an ever-expanding world, impacts of human activity on | ||
| 154 | the global environment are inevitable. The construction of roads and | 168 | the global environment are inevitable. The construction of roads and | ||
| 155 | other linear transport infrastructure leads not only to the | 169 | other linear transport infrastructure leads not only to the | ||
| 156 | destruction of habitats, but has long-term impacts on populations and | 170 | destruction of habitats, but has long-term impacts on populations and | ||
| 157 | biodiversity,\n including the introduction of edge and barrier | 171 | biodiversity,\n including the introduction of edge and barrier | ||
| 158 | effects, mortality of individuals in vehicle collisions, facilitation | 172 | effects, mortality of individuals in vehicle collisions, facilitation | ||
| 159 | of invasive species dispersal, and numerous others. On the other hand, | 173 | of invasive species dispersal, and numerous others. On the other hand, | ||
| 160 | roadsides have been found to have positive effects on biodiversity, as | 174 | roadsides have been found to have positive effects on biodiversity, as | ||
| 161 | they can constitute important habitats for some species. Previous | 175 | they can constitute important habitats for some species. Previous | ||
| 162 | studies have quantified negative or positive impacts of roadside | 176 | studies have quantified negative or positive impacts of roadside | ||
| 163 | habitats on select species or under select management regimes, but the | 177 | habitats on select species or under select management regimes, but the | ||
| 164 | grand picture of the importance of roadside habitats for biodiversity | 178 | grand picture of the importance of roadside habitats for biodiversity | ||
| 165 | conservation remains unclear. In EpicRoads, a project by the | 179 | conservation remains unclear. In EpicRoads, a project by the | ||
| 166 | Conference of European Directors of Roads (CEDR), we aimed to quantify | 180 | Conference of European Directors of Roads (CEDR), we aimed to quantify | ||
| 167 | impacts of habitats related to transport infrastructure (HTI) on a | 181 | impacts of habitats related to transport infrastructure (HTI) on a | ||
| 168 | range of taxa through meta-analyses. We used an existing database from | 182 | range of taxa through meta-analyses. We used an existing database from | ||
| 169 | a similar project by the Swedish Mistra Council for Evidence-Based | 183 | a similar project by the Swedish Mistra Council for Evidence-Based | ||
| 170 | Environmental Management (EviEM), while expanding our search to | 184 | Environmental Management (EviEM), while expanding our search to | ||
| 171 | include studies carried out in more recent years. We quantified HTI | 185 | include studies carried out in more recent years. We quantified HTI | ||
| 172 | impacts on species richness, a community-level measure, and on | 186 | impacts on species richness, a community-level measure, and on | ||
| 173 | population abundance, a population-level measure. HTI impacts are | 187 | population abundance, a population-level measure. HTI impacts are | ||
| 174 | measured through variables like road presence (versus absence), | 188 | measured through variables like road presence (versus absence), | ||
| 175 | distance to road, and different variables related to roadside | 189 | distance to road, and different variables related to roadside | ||
| 176 | vegetation and road-related disturbance. Results from the | 190 | vegetation and road-related disturbance. Results from the | ||
| 177 | meta-analyses will be presented to give an overview of what has been | 191 | meta-analyses will be presented to give an overview of what has been | ||
| 178 | found in the past 10 years regarding positive and negative effects of | 192 | found in the past 10 years regarding positive and negative effects of | ||
| 179 | factors related to HTI on all taxa with sufficient data. One of our | 193 | factors related to HTI on all taxa with sufficient data. One of our | ||
| 180 | objectives is to enhance our understanding of the extent to which HTI | 194 | objectives is to enhance our understanding of the extent to which HTI | ||
| 181 | can be beneficial for biodiversity conservation and how observed | 195 | can be beneficial for biodiversity conservation and how observed | ||
| 182 | patterns vary among species and road types. Thus, the results of this | 196 | patterns vary among species and road types. Thus, the results of this | ||
| 183 | study are relevant for making decisions on road construction and | 197 | study are relevant for making decisions on road construction and | ||
| 184 | roadside management, as they offer a multi-species perspective | 198 | roadside management, as they offer a multi-species perspective | ||
| 185 | regarding impacts of HTI. However, in addition, our study will | 199 | regarding impacts of HTI. However, in addition, our study will | ||
| 186 | identify important knowledge gaps that can direct future studies in | 200 | identify important knowledge gaps that can direct future studies in | ||
| 187 | road ecology." | 201 | road ecology." | ||
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