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a2026-06-25
en Spatial and species‐level predictions of road mortality risk using trait data. -
Modificado el valor del campo
modified
del recurso Acceso al recurso a2026-06-25
(anteriormente2026-06-23
) en Spatial and species‐level predictions of road mortality risk using trait data.
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| 81 | "name": "7e63ba62-6e42-5430-8c4a-01cef7b6d2e3", | 95 | "name": "7e63ba62-6e42-5430-8c4a-01cef7b6d2e3", | ||
| 82 | "notes": "Collisions between wildlife and vehicles are recognized as | 96 | "notes": "Collisions between wildlife and vehicles are recognized as | ||
| 83 | one of the major causes of mortality for many species. Empirical | 97 | one of the major causes of mortality for many species. Empirical | ||
| 84 | estimates of road mortality show that some species are more likely to | 98 | estimates of road mortality show that some species are more likely to | ||
| 85 | be killed than others, but to what extent this variation can be | 99 | be killed than others, but to what extent this variation can be | ||
| 86 | explained and predicted using intrinsic species characteristics | 100 | explained and predicted using intrinsic species characteristics | ||
| 87 | remains poorly understood. This study aims to identify general | 101 | remains poorly understood. This study aims to identify general | ||
| 88 | macroecological patterns associated with road mortality and generate | 102 | macroecological patterns associated with road mortality and generate | ||
| 89 | spatial and species-level predictions of risks. Location: Brazil. Time | 103 | spatial and species-level predictions of risks. Location: Brazil. Time | ||
| 90 | period: 2001\u20132014. Major taxa: Birds and mammals. We fitted | 104 | period: 2001\u20132014. Major taxa: Birds and mammals. We fitted | ||
| 91 | trait-based random forest regression models (controlling for survey | 105 | trait-based random forest regression models (controlling for survey | ||
| 92 | characteristics) to explain 783 empirical road mortality rates from | 106 | characteristics) to explain 783 empirical road mortality rates from | ||
| 93 | Brazil, representing 170 bird and 73 mammalian species. Fitted models | 107 | Brazil, representing 170 bird and 73 mammalian species. Fitted models | ||
| 94 | were then used to make spatial and species-level predictions of road | 108 | were then used to make spatial and species-level predictions of road | ||
| 95 | mortality risk in Brazil, considering 1,775 birds and 623 mammals that | 109 | mortality risk in Brazil, considering 1,775 birds and 623 mammals that | ||
| 96 | occur within the continental boundaries of the country. Survey | 110 | occur within the continental boundaries of the country. Survey | ||
| 97 | frequency and geographical location were key predictors of observed | 111 | frequency and geographical location were key predictors of observed | ||
| 98 | rates, but mortality was also explained by the body size, reproductive | 112 | rates, but mortality was also explained by the body size, reproductive | ||
| 99 | speed and ecological specialization of the species. Spatial | 113 | speed and ecological specialization of the species. Spatial | ||
| 100 | predictions revealed a high potential standardized (per kilometre of | 114 | predictions revealed a high potential standardized (per kilometre of | ||
| 101 | road) mortality risk in Amazonia for birds and mammals and, | 115 | road) mortality risk in Amazonia for birds and mammals and, | ||
| 102 | additionally, a high risk in Southern Brazil for mammals. Given the | 116 | additionally, a high risk in Southern Brazil for mammals. Given the | ||
| 103 | existing road network, these predictions mean that >8 million birds | 117 | existing road network, these predictions mean that >8 million birds | ||
| 104 | and >2 million mammals could be killed per year on Brazilian roads. | 118 | and >2 million mammals could be killed per year on Brazilian roads. | ||
| 105 | Furthermore, predicted rates for all Brazilian endotherms uncovered | 119 | Furthermore, predicted rates for all Brazilian endotherms uncovered | ||
| 106 | potential vulnerability to road mortality of several understudied | 120 | potential vulnerability to road mortality of several understudied | ||
| 107 | species that are currently listed as threatened by the International | 121 | species that are currently listed as threatened by the International | ||
| 108 | Union for Conservation of Nature. With a rapidly expanding global road | 122 | Union for Conservation of Nature. With a rapidly expanding global road | ||
| 109 | network, there is an urgent need to develop improved approaches to | 123 | network, there is an urgent need to develop improved approaches to | ||
| 110 | assess and predict road-related impacts. This study illustrates the | 124 | assess and predict road-related impacts. This study illustrates the | ||
| 111 | potential of trait-based models as assessment tools to gain a better | 125 | potential of trait-based models as assessment tools to gain a better | ||
| 112 | understanding of the correlates of vulnerability to road mortality | 126 | understanding of the correlates of vulnerability to road mortality | ||
| 113 | across species, and as predictive tools for difficult-to-sample or | 127 | across species, and as predictive tools for difficult-to-sample or | ||
| 114 | understudied species and areas.", | 128 | understudied species and areas.", | ||
| 115 | "notes_translated": { | 129 | "notes_translated": { | ||
| 116 | "en": "Collisions between wildlife and vehicles are recognized as | 130 | "en": "Collisions between wildlife and vehicles are recognized as | ||
| 117 | one of the major causes of mortality for many species. Empirical | 131 | one of the major causes of mortality for many species. Empirical | ||
| 118 | estimates of road mortality show that some species are more likely to | 132 | estimates of road mortality show that some species are more likely to | ||
| 119 | be killed than others, but to what extent this variation can be | 133 | be killed than others, but to what extent this variation can be | ||
| 120 | explained and predicted using intrinsic species characteristics | 134 | explained and predicted using intrinsic species characteristics | ||
| 121 | remains poorly understood. This study aims to identify general | 135 | remains poorly understood. This study aims to identify general | ||
| 122 | macroecological patterns associated with road mortality and generate | 136 | macroecological patterns associated with road mortality and generate | ||
| 123 | spatial and species-level predictions of risks. Location: Brazil. Time | 137 | spatial and species-level predictions of risks. Location: Brazil. Time | ||
| 124 | period: 2001\u20132014. Major taxa: Birds and mammals. We fitted | 138 | period: 2001\u20132014. Major taxa: Birds and mammals. We fitted | ||
| 125 | trait-based random forest regression models (controlling for survey | 139 | trait-based random forest regression models (controlling for survey | ||
| 126 | characteristics) to explain 783 empirical road mortality rates from | 140 | characteristics) to explain 783 empirical road mortality rates from | ||
| 127 | Brazil, representing 170 bird and 73 mammalian species. Fitted models | 141 | Brazil, representing 170 bird and 73 mammalian species. Fitted models | ||
| 128 | were then used to make spatial and species-level predictions of road | 142 | were then used to make spatial and species-level predictions of road | ||
| 129 | mortality risk in Brazil, considering 1,775 birds and 623 mammals that | 143 | mortality risk in Brazil, considering 1,775 birds and 623 mammals that | ||
| 130 | occur within the continental boundaries of the country. Survey | 144 | occur within the continental boundaries of the country. Survey | ||
| 131 | frequency and geographical location were key predictors of observed | 145 | frequency and geographical location were key predictors of observed | ||
| 132 | rates, but mortality was also explained by the body size, reproductive | 146 | rates, but mortality was also explained by the body size, reproductive | ||
| 133 | speed and ecological specialization of the species. Spatial | 147 | speed and ecological specialization of the species. Spatial | ||
| 134 | predictions revealed a high potential standardized (per kilometre of | 148 | predictions revealed a high potential standardized (per kilometre of | ||
| 135 | road) mortality risk in Amazonia for birds and mammals and, | 149 | road) mortality risk in Amazonia for birds and mammals and, | ||
| 136 | additionally, a high risk in Southern Brazil for mammals. Given the | 150 | additionally, a high risk in Southern Brazil for mammals. Given the | ||
| 137 | existing road network, these predictions mean that >8 million birds | 151 | existing road network, these predictions mean that >8 million birds | ||
| 138 | and >2 million mammals could be killed per year on Brazilian roads. | 152 | and >2 million mammals could be killed per year on Brazilian roads. | ||
| 139 | Furthermore, predicted rates for all Brazilian endotherms uncovered | 153 | Furthermore, predicted rates for all Brazilian endotherms uncovered | ||
| 140 | potential vulnerability to road mortality of several understudied | 154 | potential vulnerability to road mortality of several understudied | ||
| 141 | species that are currently listed as threatened by the International | 155 | species that are currently listed as threatened by the International | ||
| 142 | Union for Conservation of Nature. With a rapidly expanding global road | 156 | Union for Conservation of Nature. With a rapidly expanding global road | ||
| 143 | network, there is an urgent need to develop improved approaches to | 157 | network, there is an urgent need to develop improved approaches to | ||
| 144 | assess and predict road-related impacts. This study illustrates the | 158 | assess and predict road-related impacts. This study illustrates the | ||
| 145 | potential of trait-based models as assessment tools to gain a better | 159 | potential of trait-based models as assessment tools to gain a better | ||
| 146 | understanding of the correlates of vulnerability to road mortality | 160 | understanding of the correlates of vulnerability to road mortality | ||
| 147 | across species, and as predictive tools for difficult-to-sample or | 161 | across species, and as predictive tools for difficult-to-sample or | ||
| 148 | understudied species and areas.", | 162 | understudied species and areas.", | ||
| 149 | "es": "Collisions between wildlife and vehicles are recognized as | 163 | "es": "Collisions between wildlife and vehicles are recognized as | ||
| 150 | one of the major causes of mortality for many species. Empirical | 164 | one of the major causes of mortality for many species. Empirical | ||
| 151 | estimates of road mortality show that some species are more likely to | 165 | estimates of road mortality show that some species are more likely to | ||
| 152 | be killed than others, but to what extent this variation can be | 166 | be killed than others, but to what extent this variation can be | ||
| 153 | explained and predicted using intrinsic species characteristics | 167 | explained and predicted using intrinsic species characteristics | ||
| 154 | remains poorly understood. This study aims to identify general | 168 | remains poorly understood. This study aims to identify general | ||
| 155 | macroecological patterns associated with road mortality and generate | 169 | macroecological patterns associated with road mortality and generate | ||
| 156 | spatial and species-level predictions of risks. Location: Brazil. Time | 170 | spatial and species-level predictions of risks. Location: Brazil. Time | ||
| 157 | period: 2001\u20132014. Major taxa: Birds and mammals. We fitted | 171 | period: 2001\u20132014. Major taxa: Birds and mammals. We fitted | ||
| 158 | trait-based random forest regression models (controlling for survey | 172 | trait-based random forest regression models (controlling for survey | ||
| 159 | characteristics) to explain 783 empirical road mortality rates from | 173 | characteristics) to explain 783 empirical road mortality rates from | ||
| 160 | Brazil, representing 170 bird and 73 mammalian species. Fitted models | 174 | Brazil, representing 170 bird and 73 mammalian species. Fitted models | ||
| 161 | were then used to make spatial and species-level predictions of road | 175 | were then used to make spatial and species-level predictions of road | ||
| 162 | mortality risk in Brazil, considering 1,775 birds and 623 mammals that | 176 | mortality risk in Brazil, considering 1,775 birds and 623 mammals that | ||
| 163 | occur within the continental boundaries of the country. Survey | 177 | occur within the continental boundaries of the country. Survey | ||
| 164 | frequency and geographical location were key predictors of observed | 178 | frequency and geographical location were key predictors of observed | ||
| 165 | rates, but mortality was also explained by the body size, reproductive | 179 | rates, but mortality was also explained by the body size, reproductive | ||
| 166 | speed and ecological specialization of the species. Spatial | 180 | speed and ecological specialization of the species. Spatial | ||
| 167 | predictions revealed a high potential standardized (per kilometre of | 181 | predictions revealed a high potential standardized (per kilometre of | ||
| 168 | road) mortality risk in Amazonia for birds and mammals and, | 182 | road) mortality risk in Amazonia for birds and mammals and, | ||
| 169 | additionally, a high risk in Southern Brazil for mammals. Given the | 183 | additionally, a high risk in Southern Brazil for mammals. Given the | ||
| 170 | existing road network, these predictions mean that >8 million birds | 184 | existing road network, these predictions mean that >8 million birds | ||
| 171 | and >2 million mammals could be killed per year on Brazilian roads. | 185 | and >2 million mammals could be killed per year on Brazilian roads. | ||
| 172 | Furthermore, predicted rates for all Brazilian endotherms uncovered | 186 | Furthermore, predicted rates for all Brazilian endotherms uncovered | ||
| 173 | potential vulnerability to road mortality of several understudied | 187 | potential vulnerability to road mortality of several understudied | ||
| 174 | species that are currently listed as threatened by the International | 188 | species that are currently listed as threatened by the International | ||
| 175 | Union for Conservation of Nature. With a rapidly expanding global road | 189 | Union for Conservation of Nature. With a rapidly expanding global road | ||
| 176 | network, there is an urgent need to develop improved approaches to | 190 | network, there is an urgent need to develop improved approaches to | ||
| 177 | assess and predict road-related impacts. This study illustrates the | 191 | assess and predict road-related impacts. This study illustrates the | ||
| 178 | potential of trait-based models as assessment tools to gain a better | 192 | potential of trait-based models as assessment tools to gain a better | ||
| 179 | understanding of the correlates of vulnerability to road mortality | 193 | understanding of the correlates of vulnerability to road mortality | ||
| 180 | across species, and as predictive tools for difficult-to-sample or | 194 | across species, and as predictive tools for difficult-to-sample or | ||
| 181 | understudied species and areas." | 195 | understudied species and areas." | ||
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