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En el instante 25 de junio de 2026, 12:37:03 UTC,
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Modificado el valor del campo
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a2026-06-25
en Preventing wildlife roadkill can offset mitigation investments in short-medium term. -
Modificado el valor del campo
modified
del recurso Acceso al recurso a2026-06-25
(anteriormente2026-06-23
) en Preventing wildlife roadkill can offset mitigation investments in short-medium term.
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| 80 | "name": "64cd5666-07af-5c0c-8e83-b79e8a70bc96", | 94 | "name": "64cd5666-07af-5c0c-8e83-b79e8a70bc96", | ||
| 81 | "notes": "Wildlife vehicle collisions (WVC) are a threat to wildlife | 95 | "notes": "Wildlife vehicle collisions (WVC) are a threat to wildlife | ||
| 82 | and humans, killing millions of animals of numerous species, as well | 96 | and humans, killing millions of animals of numerous species, as well | ||
| 83 | as causing significant damage to vehicles, drivers and passengers. | 97 | as causing significant damage to vehicles, drivers and passengers. | ||
| 84 | Road fencing is a highly effective mitigation measure at reducing WVC, | 98 | Road fencing is a highly effective mitigation measure at reducing WVC, | ||
| 85 | however its large-scale implementation requires a high investment. We | 99 | however its large-scale implementation requires a high investment. We | ||
| 86 | questioned how long it would take for savings from avoided collisions | 100 | questioned how long it would take for savings from avoided collisions | ||
| 87 | to offset the investments in road fencing mitigation, focusing on | 101 | to offset the investments in road fencing mitigation, focusing on | ||
| 88 | vehicle damage costs. Using the information of a 3-year systematic | 102 | vehicle damage costs. Using the information of a 3-year systematic | ||
| 89 | roadkill monitoring of 1158 km in Mato Grosso do Sul, Brazil, we | 103 | roadkill monitoring of 1158 km in Mato Grosso do Sul, Brazil, we | ||
| 90 | estimated the real number of casualties accounting for bias in | 104 | estimated the real number of casualties accounting for bias in | ||
| 91 | roadkill counting. We obtained information on the material costs on | 105 | roadkill counting. We obtained information on the material costs on | ||
| 92 | cars and trucks due to WVC and, considering the road traffic volume | 106 | cars and trucks due to WVC and, considering the road traffic volume | ||
| 93 | characteristics, estimated the total material costs resulting from | 107 | characteristics, estimated the total material costs resulting from | ||
| 94 | collisions with larger animals. Cost-benefit analyses allowed | 108 | collisions with larger animals. Cost-benefit analyses allowed | ||
| 95 | estimating the time required to amortize the investment in fencing, | 109 | estimating the time required to amortize the investment in fencing, | ||
| 96 | considering its application along the full surveyed roads or only in | 110 | considering its application along the full surveyed roads or only in | ||
| 97 | hotspots of mortality. We recorded over 10,000 WVC, 40% of which | 111 | hotspots of mortality. We recorded over 10,000 WVC, 40% of which | ||
| 98 | involved animals that can cause significant material damage to | 112 | involved animals that can cause significant material damage to | ||
| 99 | vehicles, namely the endangered lowland tapir (Tapirus terrestris, n = | 113 | vehicles, namely the endangered lowland tapir (Tapirus terrestris, n = | ||
| 100 | 267) and giant anteater (Myrmecophaga tridactyla, n = 608). The | 114 | 267) and giant anteater (Myrmecophaga tridactyla, n = 608). The | ||
| 101 | average material cost per accident was US$ 885 \u00b1 1575 (mean | 115 | average material cost per accident was US$ 885 \u00b1 1575 (mean | ||
| 102 | \u00b1 SD). We show that investments are likely to pay off in | 116 | \u00b1 SD). We show that investments are likely to pay off in | ||
| 103 | 16\u201340 years for the mitigation of the full roads, and in | 117 | 16\u201340 years for the mitigation of the full roads, and in | ||
| 104 | 9\u201325 years for hotspots of mortality. Thus, road mitigation is a | 118 | 9\u201325 years for hotspots of mortality. Thus, road mitigation is a | ||
| 105 | win-win solution for increasing traffic safety for humans and reduces | 119 | win-win solution for increasing traffic safety for humans and reduces | ||
| 106 | road-related negative effects on biodiversity.", | 120 | road-related negative effects on biodiversity.", | ||
| 107 | "notes_translated": { | 121 | "notes_translated": { | ||
| 108 | "en": "Wildlife vehicle collisions (WVC) are a threat to wildlife | 122 | "en": "Wildlife vehicle collisions (WVC) are a threat to wildlife | ||
| 109 | and humans, killing millions of animals of numerous species, as well | 123 | and humans, killing millions of animals of numerous species, as well | ||
| 110 | as causing significant damage to vehicles, drivers and passengers. | 124 | as causing significant damage to vehicles, drivers and passengers. | ||
| 111 | Road fencing is a highly effective\u00a0mitigation measure\u00a0at | 125 | Road fencing is a highly effective\u00a0mitigation measure\u00a0at | ||
| 112 | reducing WVC, however its large-scale implementation requires a high | 126 | reducing WVC, however its large-scale implementation requires a high | ||
| 113 | investment. We questioned how long it would take for savings from | 127 | investment. We questioned how long it would take for savings from | ||
| 114 | avoided collisions to offset the investments in road fencing | 128 | avoided collisions to offset the investments in road fencing | ||
| 115 | mitigation, focusing on vehicle damage costs. Using the information of | 129 | mitigation, focusing on vehicle damage costs. Using the information of | ||
| 116 | a 3-year systematic\u00a0roadkill\u00a0monitoring of 1158\u00a0km in | 130 | a 3-year systematic\u00a0roadkill\u00a0monitoring of 1158\u00a0km in | ||
| 117 | Mato Grosso do Sul, Brazil, we estimated the real number of casualties | 131 | Mato Grosso do Sul, Brazil, we estimated the real number of casualties | ||
| 118 | accounting for bias in\u00a0roadkill\u00a0counting. We obtained | 132 | accounting for bias in\u00a0roadkill\u00a0counting. We obtained | ||
| 119 | information on the material costs on cars and trucks due to WVC and, | 133 | information on the material costs on cars and trucks due to WVC and, | ||
| 120 | considering the road traffic volume characteristics, estimated the | 134 | considering the road traffic volume characteristics, estimated the | ||
| 121 | total material costs resulting from collisions with larger animals. | 135 | total material costs resulting from collisions with larger animals. | ||
| 122 | Cost-benefit analyses allowed estimating the time required to amortize | 136 | Cost-benefit analyses allowed estimating the time required to amortize | ||
| 123 | the investment in fencing, considering its application along the full | 137 | the investment in fencing, considering its application along the full | ||
| 124 | surveyed roads or only in hotspots of mortality. We recorded over | 138 | surveyed roads or only in hotspots of mortality. We recorded over | ||
| 125 | 10,000 WVC, 40% of which involved animals that can cause significant | 139 | 10,000 WVC, 40% of which involved animals that can cause significant | ||
| 126 | material damage to vehicles, namely the | 140 | material damage to vehicles, namely the | ||
| 127 | endangered\u00a0lowland\u00a0tapir\u00a0(Tapirus terrestris, | 141 | endangered\u00a0lowland\u00a0tapir\u00a0(Tapirus terrestris, | ||
| 128 | n\u00a0=\u00a0267) and giant anteater (Myrmecophaga tridactyla, | 142 | n\u00a0=\u00a0267) and giant anteater (Myrmecophaga tridactyla, | ||
| 129 | n\u00a0=\u00a0608). The average material cost per accident was US$ | 143 | n\u00a0=\u00a0608). The average material cost per accident was US$ | ||
| 130 | 885\u00a0\u00b1\u00a01575 (mean\u00a0\u00b1\u00a0SD). We show that | 144 | 885\u00a0\u00b1\u00a01575 (mean\u00a0\u00b1\u00a0SD). We show that | ||
| 131 | investments are likely to pay off in 16\u201340\u00a0years for the | 145 | investments are likely to pay off in 16\u201340\u00a0years for the | ||
| 132 | mitigation of the full roads, and in 9\u201325\u00a0years for hotspots | 146 | mitigation of the full roads, and in 9\u201325\u00a0years for hotspots | ||
| 133 | of mortality. Thus, road mitigation is a win-win solution for | 147 | of mortality. Thus, road mitigation is a win-win solution for | ||
| 134 | increasing traffic safety for humans and reduces road-related negative | 148 | increasing traffic safety for humans and reduces road-related negative | ||
| 135 | effects on biodiversity.", | 149 | effects on biodiversity.", | ||
| 136 | "es": "Wildlife vehicle collisions (WVC) are a threat to wildlife | 150 | "es": "Wildlife vehicle collisions (WVC) are a threat to wildlife | ||
| 137 | and humans, killing millions of animals of numerous species, as well | 151 | and humans, killing millions of animals of numerous species, as well | ||
| 138 | as causing significant damage to vehicles, drivers and passengers. | 152 | as causing significant damage to vehicles, drivers and passengers. | ||
| 139 | Road fencing is a highly effective mitigation measure at reducing WVC, | 153 | Road fencing is a highly effective mitigation measure at reducing WVC, | ||
| 140 | however its large-scale implementation requires a high investment. We | 154 | however its large-scale implementation requires a high investment. We | ||
| 141 | questioned how long it would take for savings from avoided collisions | 155 | questioned how long it would take for savings from avoided collisions | ||
| 142 | to offset the investments in road fencing mitigation, focusing on | 156 | to offset the investments in road fencing mitigation, focusing on | ||
| 143 | vehicle damage costs. Using the information of a 3-year systematic | 157 | vehicle damage costs. Using the information of a 3-year systematic | ||
| 144 | roadkill monitoring of 1158 km in Mato Grosso do Sul, Brazil, we | 158 | roadkill monitoring of 1158 km in Mato Grosso do Sul, Brazil, we | ||
| 145 | estimated the real number of casualties accounting for bias in | 159 | estimated the real number of casualties accounting for bias in | ||
| 146 | roadkill counting. We obtained information on the material costs on | 160 | roadkill counting. We obtained information on the material costs on | ||
| 147 | cars and trucks due to WVC and, considering the road traffic volume | 161 | cars and trucks due to WVC and, considering the road traffic volume | ||
| 148 | characteristics, estimated the total material costs resulting from | 162 | characteristics, estimated the total material costs resulting from | ||
| 149 | collisions with larger animals. Cost-benefit analyses allowed | 163 | collisions with larger animals. Cost-benefit analyses allowed | ||
| 150 | estimating the time required to amortize the investment in fencing, | 164 | estimating the time required to amortize the investment in fencing, | ||
| 151 | considering its application along the full surveyed roads or only in | 165 | considering its application along the full surveyed roads or only in | ||
| 152 | hotspots of mortality. We recorded over 10,000 WVC, 40% of which | 166 | hotspots of mortality. We recorded over 10,000 WVC, 40% of which | ||
| 153 | involved animals that can cause significant material damage to | 167 | involved animals that can cause significant material damage to | ||
| 154 | vehicles, namely the endangered lowland tapir (Tapirus terrestris, n = | 168 | vehicles, namely the endangered lowland tapir (Tapirus terrestris, n = | ||
| 155 | 267) and giant anteater (Myrmecophaga tridactyla, n = 608). The | 169 | 267) and giant anteater (Myrmecophaga tridactyla, n = 608). The | ||
| 156 | average material cost per accident was US$ 885 \u00b1 1575 (mean | 170 | average material cost per accident was US$ 885 \u00b1 1575 (mean | ||
| 157 | \u00b1 SD). We show that investments are likely to pay off in | 171 | \u00b1 SD). We show that investments are likely to pay off in | ||
| 158 | 16\u201340 years for the mitigation of the full roads, and in | 172 | 16\u201340 years for the mitigation of the full roads, and in | ||
| 159 | 9\u201325 years for hotspots of mortality. Thus, road mitigation is a | 173 | 9\u201325 years for hotspots of mortality. Thus, road mitigation is a | ||
| 160 | win-win solution for increasing traffic safety for humans and reduces | 174 | win-win solution for increasing traffic safety for humans and reduces | ||
| 161 | road-related negative effects on biodiversity." | 175 | road-related negative effects on biodiversity." | ||
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