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En el instante 23 de junio de 2026, 16:09:44 UTC,
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Modificado el valor del campo
spatial_coverage
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en Are animal-vehicle collisions a random event? – Analysis of the spatial distribution of accident data.
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| 82 | "name": "400e428c-3a5d-5678-af73-a9db29f9b4d6", | 82 | "name": "400e428c-3a5d-5678-af73-a9db29f9b4d6", | ||
| 83 | "notes": "Ungulate-vehicle collisions (UVC) in Sweden, Catalonia (NE | 83 | "notes": "Ungulate-vehicle collisions (UVC) in Sweden, Catalonia (NE | ||
| 84 | Spain), the Czech republic as well as in many other European countries | 84 | Spain), the Czech republic as well as in many other European countries | ||
| 85 | are an increasing traffic safety issue, causing an escalating loss in | 85 | are an increasing traffic safety issue, causing an escalating loss in | ||
| 86 | wildlife and a growing socioeconomic burden. Conventional prevention | 86 | wildlife and a growing socioeconomic burden. Conventional prevention | ||
| 87 | methods appear as little cost-effective and both Transport and | 87 | methods appear as little cost-effective and both Transport and | ||
| 88 | Wildlife administrations call for better targeted mitigation | 88 | Wildlife administrations call for better targeted mitigation | ||
| 89 | strategies. An essential requisite for this is a good understanding of | 89 | strategies. An essential requisite for this is a good understanding of | ||
| 90 | how accidents are distributed and where they aggregate. Since 2010, in | 90 | how accidents are distributed and where they aggregate. Since 2010, in | ||
| 91 | Sweden car drivers are legally obliged to report any UVC to the police | 91 | Sweden car drivers are legally obliged to report any UVC to the police | ||
| 92 | and a majority of these reports is followed-up by contracted hunters | 92 | and a majority of these reports is followed-up by contracted hunters | ||
| 93 | who take care of the wounded or dead animal and report the exact | 93 | who take care of the wounded or dead animal and report the exact | ||
| 94 | accident location. In Catalonia and Czech republic, UVC are registered | 94 | accident location. In Catalonia and Czech republic, UVC are registered | ||
| 95 | by traffic police and road management teams as drivers and not obliged | 95 | by traffic police and road management teams as drivers and not obliged | ||
| 96 | to report the data. We present a thorough analysis of these reports, | 96 | to report the data. We present a thorough analysis of these reports, | ||
| 97 | using a modified kernel density estimation technique (KDE+) to | 97 | using a modified kernel density estimation technique (KDE+) to | ||
| 98 | identify significant clusters in accident frequencies and compare | 98 | identify significant clusters in accident frequencies and compare | ||
| 99 | their spatial coherence between ungulate species and between years. | 99 | their spatial coherence between ungulate species and between years. | ||
| 100 | During the 5-year period of 2010 to 2014, some 79000 accidents with | 100 | During the 5-year period of 2010 to 2014, some 79000 accidents with | ||
| 101 | roe deer (Capreolus capreolus), 19000 with moose (Alces alces), 11000 | 101 | roe deer (Capreolus capreolus), 19000 with moose (Alces alces), 11000 | ||
| 102 | with wild boar (Sus scrofa) and 7000 with fallow deer (Dama dama) or | 102 | with wild boar (Sus scrofa) and 7000 with fallow deer (Dama dama) or | ||
| 103 | red deer (Cervus elaphus) have been reported by hunters in Sweden. Of | 103 | red deer (Cervus elaphus) have been reported by hunters in Sweden. Of | ||
| 104 | these, 30% to 45% were distributed in a significantly aggregated | 104 | these, 30% to 45% were distributed in a significantly aggregated | ||
| 105 | pattern. UVC clusters covered less than 3% of the entire road network. | 105 | pattern. UVC clusters covered less than 3% of the entire road network. | ||
| 106 | Within these clusters, accident densities were on average 45 times | 106 | Within these clusters, accident densities were on average 45 times | ||
| 107 | higher than elsewhere on the roads. In Catalonia during 2007 to 2011, | 107 | higher than elsewhere on the roads. In Catalonia during 2007 to 2011, | ||
| 108 | the analyses were performed on 2110 UVC of which 1987 were with wild | 108 | the analyses were performed on 2110 UVC of which 1987 were with wild | ||
| 109 | boar. About 20% of these accidents were included in the significant | 109 | boar. About 20% of these accidents were included in the significant | ||
| 110 | clusters, covering less than 0,3% of the entire road network. In the | 110 | clusters, covering less than 0,3% of the entire road network. In the | ||
| 111 | Czech Republic, 2009 \u2013 2013, 16 612 UVC (not species specific) | 111 | Czech Republic, 2009 \u2013 2013, 16 612 UVC (not species specific) | ||
| 112 | were recorded by the police during 2009 \u2013 2013. Of these, 33,2% | 112 | were recorded by the police during 2009 \u2013 2013. Of these, 33,2% | ||
| 113 | were significantly aggregated in 2060 clusters covering 0,71 % (267 | 113 | were significantly aggregated in 2060 clusters covering 0,71 % (267 | ||
| 114 | km) of the Czech road network. There were important differences in | 114 | km) of the Czech road network. There were important differences in | ||
| 115 | aggregation and in cluster locations between species and some | 115 | aggregation and in cluster locations between species and some | ||
| 116 | differences between time periods as well. Factors associated with | 116 | differences between time periods as well. Factors associated with | ||
| 117 | clustering can be generalize as providing increased attractiveness and | 117 | clustering can be generalize as providing increased attractiveness and | ||
| 118 | increased openness of the road to wildlife. We conclude that, despite | 118 | increased openness of the road to wildlife. We conclude that, despite | ||
| 119 | species specific and temporal differences in clusters, only a small | 119 | species specific and temporal differences in clusters, only a small | ||
| 120 | portion of the road network needs to be mitigated by physical | 120 | portion of the road network needs to be mitigated by physical | ||
| 121 | mitigation measures such as fences or fauna passages to affect a | 121 | mitigation measures such as fences or fauna passages to affect a | ||
| 122 | substantial part of UVC. Yet, for the remaining part of UVC that are | 122 | substantial part of UVC. Yet, for the remaining part of UVC that are | ||
| 123 | not aggregated, a different mitigation approach is needed that | 123 | not aggregated, a different mitigation approach is needed that | ||
| 124 | corresponds to regional or global factors such as wildlife population | 124 | corresponds to regional or global factors such as wildlife population | ||
| 125 | densities or driver behaviour. Note: The study is stillongoing and | 125 | densities or driver behaviour. Note: The study is stillongoing and | ||
| 126 | will produce further results before the conference that shall be | 126 | will produce further results before the conference that shall be | ||
| 127 | included in an updated version of the abstract.", | 127 | included in an updated version of the abstract.", | ||
| 128 | "notes_translated": { | 128 | "notes_translated": { | ||
| 129 | "en": "Ungulate-vehicle collisions (UVC) in Sweden, Catalonia (NE | 129 | "en": "Ungulate-vehicle collisions (UVC) in Sweden, Catalonia (NE | ||
| 130 | Spain), the Czech republic as well as in many other European countries | 130 | Spain), the Czech republic as well as in many other European countries | ||
| 131 | are an increasing traffic safety issue, causing an escalating loss in | 131 | are an increasing traffic safety issue, causing an escalating loss in | ||
| 132 | wildlife and a growing socioeconomic burden. Conventional | 132 | wildlife and a growing socioeconomic burden. Conventional | ||
| 133 | prevention\nmethods appear as little cost-effective and both Transport | 133 | prevention\nmethods appear as little cost-effective and both Transport | ||
| 134 | and Wildlife administrations call for better targeted mitigation | 134 | and Wildlife administrations call for better targeted mitigation | ||
| 135 | strategies. An essential requisite for this is a good understanding of | 135 | strategies. An essential requisite for this is a good understanding of | ||
| 136 | how accidents are distributed and where they aggregate. Since 2010, in | 136 | how accidents are distributed and where they aggregate. Since 2010, in | ||
| 137 | Sweden car drivers are legally obliged to report any UVC to the police | 137 | Sweden car drivers are legally obliged to report any UVC to the police | ||
| 138 | and a majority of these reports is followed-up by contracted hunters | 138 | and a majority of these reports is followed-up by contracted hunters | ||
| 139 | who take care of the wounded or dead animal and report the exact | 139 | who take care of the wounded or dead animal and report the exact | ||
| 140 | accident location. In Catalonia and Czech republic, UVC are registered | 140 | accident location. In Catalonia and Czech republic, UVC are registered | ||
| 141 | by\ntraffic police and road management teams as drivers and not | 141 | by\ntraffic police and road management teams as drivers and not | ||
| 142 | obliged to report the data. We present a thorough analysis of these | 142 | obliged to report the data. We present a thorough analysis of these | ||
| 143 | reports, using a modified kernel density estimation technique (KDE+) | 143 | reports, using a modified kernel density estimation technique (KDE+) | ||
| 144 | to identify significant clusters in accident frequencies and compare | 144 | to identify significant clusters in accident frequencies and compare | ||
| 145 | their\nspatial coherence between ungulate species and between years. | 145 | their\nspatial coherence between ungulate species and between years. | ||
| 146 | During the 5-year period of 2010 to 2014, some 79000 accidents with | 146 | During the 5-year period of 2010 to 2014, some 79000 accidents with | ||
| 147 | roe deer (Capreolus capreolus), 19000 with moose (Alces alces), 11000 | 147 | roe deer (Capreolus capreolus), 19000 with moose (Alces alces), 11000 | ||
| 148 | with wild boar (Sus scrofa) and 7000 with fallow deer (Dama dama) or | 148 | with wild boar (Sus scrofa) and 7000 with fallow deer (Dama dama) or | ||
| 149 | red deer (Cervus elaphus) have been reported by hunters in Sweden. Of | 149 | red deer (Cervus elaphus) have been reported by hunters in Sweden. Of | ||
| 150 | these, 30% to 45% were distributed in a significantly aggregated | 150 | these, 30% to 45% were distributed in a significantly aggregated | ||
| 151 | pattern. UVC clusters covered less than 3% of the entire road network. | 151 | pattern. UVC clusters covered less than 3% of the entire road network. | ||
| 152 | Within these clusters, accident densities were on average 45 times | 152 | Within these clusters, accident densities were on average 45 times | ||
| 153 | higher than elsewhere on the roads. In Catalonia during 2007 to 2011, | 153 | higher than elsewhere on the roads. In Catalonia during 2007 to 2011, | ||
| 154 | the analyses were performed on 2110 UVC of which 1987 were with wild | 154 | the analyses were performed on 2110 UVC of which 1987 were with wild | ||
| 155 | boar. About 20% of these accidents were included in the significant | 155 | boar. About 20% of these accidents were included in the significant | ||
| 156 | clusters, covering less than 0,3% of the entire road network. In the | 156 | clusters, covering less than 0,3% of the entire road network. In the | ||
| 157 | Czech Republic, 2009 \u2013 2013, 16 612 UVC (not species specific) | 157 | Czech Republic, 2009 \u2013 2013, 16 612 UVC (not species specific) | ||
| 158 | were recorded by the police during 2009 \u2013 2013. Of these, 33,2% | 158 | were recorded by the police during 2009 \u2013 2013. Of these, 33,2% | ||
| 159 | were significantly aggregated in 2060 clusters covering 0,71 % (267 | 159 | were significantly aggregated in 2060 clusters covering 0,71 % (267 | ||
| 160 | km) of the Czech road network. There were important differences in | 160 | km) of the Czech road network. There were important differences in | ||
| 161 | aggregation and in cluster locations between species and some | 161 | aggregation and in cluster locations between species and some | ||
| 162 | differences between time periods as well. Factors associated with | 162 | differences between time periods as well. Factors associated with | ||
| 163 | clustering can be generalize as providing increased attractiveness and | 163 | clustering can be generalize as providing increased attractiveness and | ||
| 164 | increased openness of the road to wildlife. We conclude that, despite | 164 | increased openness of the road to wildlife. We conclude that, despite | ||
| 165 | species specific and temporal differences in clusters, only a small | 165 | species specific and temporal differences in clusters, only a small | ||
| 166 | portion of the road network needs to be mitigated by physical | 166 | portion of the road network needs to be mitigated by physical | ||
| 167 | mitigation measures such as fences or fauna passages to affect a | 167 | mitigation measures such as fences or fauna passages to affect a | ||
| 168 | substantial part of UVC. Yet, for the remaining part of UVC that are | 168 | substantial part of UVC. Yet, for the remaining part of UVC that are | ||
| 169 | not aggregated, a different mitigation approach is needed that | 169 | not aggregated, a different mitigation approach is needed that | ||
| 170 | corresponds to regional or global factors such as wildlife population | 170 | corresponds to regional or global factors such as wildlife population | ||
| 171 | densities or driver behaviour. Note: The study is stillongoing and | 171 | densities or driver behaviour. Note: The study is stillongoing and | ||
| 172 | will produce further results before the conference that shall be | 172 | will produce further results before the conference that shall be | ||
| 173 | included in an updated version of the abstract.", | 173 | included in an updated version of the abstract.", | ||
| 174 | "es": "Ungulate-vehicle collisions (UVC) in Sweden, Catalonia (NE | 174 | "es": "Ungulate-vehicle collisions (UVC) in Sweden, Catalonia (NE | ||
| 175 | Spain), the Czech republic as well as in many other European countries | 175 | Spain), the Czech republic as well as in many other European countries | ||
| 176 | are an increasing traffic safety issue, causing an escalating loss in | 176 | are an increasing traffic safety issue, causing an escalating loss in | ||
| 177 | wildlife and a growing socioeconomic burden. Conventional prevention | 177 | wildlife and a growing socioeconomic burden. Conventional prevention | ||
| 178 | methods appear as little cost-effective and both Transport and | 178 | methods appear as little cost-effective and both Transport and | ||
| 179 | Wildlife administrations call for better targeted mitigation | 179 | Wildlife administrations call for better targeted mitigation | ||
| 180 | strategies. An essential requisite for this is a good understanding of | 180 | strategies. An essential requisite for this is a good understanding of | ||
| 181 | how accidents are distributed and where they aggregate. Since 2010, in | 181 | how accidents are distributed and where they aggregate. Since 2010, in | ||
| 182 | Sweden car drivers are legally obliged to report any UVC to the police | 182 | Sweden car drivers are legally obliged to report any UVC to the police | ||
| 183 | and a majority of these reports is followed-up by contracted hunters | 183 | and a majority of these reports is followed-up by contracted hunters | ||
| 184 | who take care of the wounded or dead animal and report the exact | 184 | who take care of the wounded or dead animal and report the exact | ||
| 185 | accident location. In Catalonia and Czech republic, UVC are registered | 185 | accident location. In Catalonia and Czech republic, UVC are registered | ||
| 186 | by traffic police and road management teams as drivers and not obliged | 186 | by traffic police and road management teams as drivers and not obliged | ||
| 187 | to report the data. We present a thorough analysis of these reports, | 187 | to report the data. We present a thorough analysis of these reports, | ||
| 188 | using a modified kernel density estimation technique (KDE+) to | 188 | using a modified kernel density estimation technique (KDE+) to | ||
| 189 | identify significant clusters in accident frequencies and compare | 189 | identify significant clusters in accident frequencies and compare | ||
| 190 | their spatial coherence between ungulate species and between years. | 190 | their spatial coherence between ungulate species and between years. | ||
| 191 | During the 5-year period of 2010 to 2014, some 79000 accidents with | 191 | During the 5-year period of 2010 to 2014, some 79000 accidents with | ||
| 192 | roe deer (Capreolus capreolus), 19000 with moose (Alces alces), 11000 | 192 | roe deer (Capreolus capreolus), 19000 with moose (Alces alces), 11000 | ||
| 193 | with wild boar (Sus scrofa) and 7000 with fallow deer (Dama dama) or | 193 | with wild boar (Sus scrofa) and 7000 with fallow deer (Dama dama) or | ||
| 194 | red deer (Cervus elaphus) have been reported by hunters in Sweden. Of | 194 | red deer (Cervus elaphus) have been reported by hunters in Sweden. Of | ||
| 195 | these, 30% to 45% were distributed in a significantly aggregated | 195 | these, 30% to 45% were distributed in a significantly aggregated | ||
| 196 | pattern. UVC clusters covered less than 3% of the entire road network. | 196 | pattern. UVC clusters covered less than 3% of the entire road network. | ||
| 197 | Within these clusters, accident densities were on average 45 times | 197 | Within these clusters, accident densities were on average 45 times | ||
| 198 | higher than elsewhere on the roads. In Catalonia during 2007 to 2011, | 198 | higher than elsewhere on the roads. In Catalonia during 2007 to 2011, | ||
| 199 | the analyses were performed on 2110 UVC of which 1987 were with wild | 199 | the analyses were performed on 2110 UVC of which 1987 were with wild | ||
| 200 | boar. About 20% of these accidents were included in the significant | 200 | boar. About 20% of these accidents were included in the significant | ||
| 201 | clusters, covering less than 0,3% of the entire road network. In the | 201 | clusters, covering less than 0,3% of the entire road network. In the | ||
| 202 | Czech Republic, 2009 \u2013 2013, 16 612 UVC (not species specific) | 202 | Czech Republic, 2009 \u2013 2013, 16 612 UVC (not species specific) | ||
| 203 | were recorded by the police during 2009 \u2013 2013. Of these, 33,2% | 203 | were recorded by the police during 2009 \u2013 2013. Of these, 33,2% | ||
| 204 | were significantly aggregated in 2060 clusters covering 0,71 % (267 | 204 | were significantly aggregated in 2060 clusters covering 0,71 % (267 | ||
| 205 | km) of the Czech road network. There were important differences in | 205 | km) of the Czech road network. There were important differences in | ||
| 206 | aggregation and in cluster locations between species and some | 206 | aggregation and in cluster locations between species and some | ||
| 207 | differences between time periods as well. Factors associated with | 207 | differences between time periods as well. Factors associated with | ||
| 208 | clustering can be generalize as providing increased attractiveness and | 208 | clustering can be generalize as providing increased attractiveness and | ||
| 209 | increased openness of the road to wildlife. We conclude that, despite | 209 | increased openness of the road to wildlife. We conclude that, despite | ||
| 210 | species specific and temporal differences in clusters, only a small | 210 | species specific and temporal differences in clusters, only a small | ||
| 211 | portion of the road network needs to be mitigated by physical | 211 | portion of the road network needs to be mitigated by physical | ||
| 212 | mitigation measures such as fences or fauna passages to affect a | 212 | mitigation measures such as fences or fauna passages to affect a | ||
| 213 | substantial part of UVC. Yet, for the remaining part of UVC that are | 213 | substantial part of UVC. Yet, for the remaining part of UVC that are | ||
| 214 | not aggregated, a different mitigation approach is needed that | 214 | not aggregated, a different mitigation approach is needed that | ||
| 215 | corresponds to regional or global factors such as wildlife population | 215 | corresponds to regional or global factors such as wildlife population | ||
| 216 | densities or driver behaviour. Note: The study is stillongoing and | 216 | densities or driver behaviour. Note: The study is stillongoing and | ||
| 217 | will produce further results before the conference that shall be | 217 | will produce further results before the conference that shall be | ||
| 218 | included in an updated version of the abstract." | 218 | included in an updated version of the abstract." | ||
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