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del recurso Acceso al recurso a2026-06-25
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) en Simulating the consequences of roads for wildlife population dynamics.
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| 81 | "notes": "Rapidly expanding road networks have been a key driver of | 95 | "notes": "Rapidly expanding road networks have been a key driver of | ||
| 82 | the fragmentation and isolation of many wildlife species, and are a | 96 | the fragmentation and isolation of many wildlife species, and are a | ||
| 83 | source of significant mortality due to collisions with vehicles. But | 97 | source of significant mortality due to collisions with vehicles. But | ||
| 84 | not all animals are affected equally by transportation infrastructure, | 98 | not all animals are affected equally by transportation infrastructure, | ||
| 85 | and in most cases little is known about the population-scale | 99 | and in most cases little is known about the population-scale | ||
| 86 | consequences of roads for wildlife. Even less information is available | 100 | consequences of roads for wildlife. Even less information is available | ||
| 87 | to characterize species\u2019 behavioral responses to roads. Although | 101 | to characterize species\u2019 behavioral responses to roads. Although | ||
| 88 | research shows that maned wolves (Chrysocyon brachyurus) in Brazil are | 102 | research shows that maned wolves (Chrysocyon brachyurus) in Brazil are | ||
| 89 | experiencing considerable fragmentation and road mortality, the degree | 103 | experiencing considerable fragmentation and road mortality, the degree | ||
| 90 | to which these disturbances are impacting the species\u2019 viability | 104 | to which these disturbances are impacting the species\u2019 viability | ||
| 91 | is unknown. The goal of this study was to analyze the potential | 105 | is unknown. The goal of this study was to analyze the potential | ||
| 92 | effects of roads on maned wolf population size and structure. We used | 106 | effects of roads on maned wolf population size and structure. We used | ||
| 93 | a simulation model to evaluate the population-scale consequences of | 107 | a simulation model to evaluate the population-scale consequences of | ||
| 94 | individual maned wolf interactions with roads, which can result in | 108 | individual maned wolf interactions with roads, which can result in | ||
| 95 | road crossing, avoidance, or mortality due to a collision with a | 109 | road crossing, avoidance, or mortality due to a collision with a | ||
| 96 | vehicle. We also forecasted where in Brazil these impacts might be | 110 | vehicle. We also forecasted where in Brazil these impacts might be | ||
| 97 | most significant. Our model incorporated species demographic and | 111 | most significant. Our model incorporated species demographic and | ||
| 98 | movement parameters, plus habitat quality and a map of the road | 112 | movement parameters, plus habitat quality and a map of the road | ||
| 99 | network. We found that even moderate rates of road mortality led to | 113 | network. We found that even moderate rates of road mortality led to | ||
| 100 | severe declines in population size, and that four specific locations | 114 | severe declines in population size, and that four specific locations | ||
| 101 | accounted for a disproportionate fraction of roadkill events. Our | 115 | accounted for a disproportionate fraction of roadkill events. Our | ||
| 102 | approach will be generally useful for evaluating the relative | 116 | approach will be generally useful for evaluating the relative | ||
| 103 | importance of road effects on species conservation in many ecological | 117 | importance of road effects on species conservation in many ecological | ||
| 104 | systems, for prioritizing data collection efforts, and for informing | 118 | systems, for prioritizing data collection efforts, and for informing | ||
| 105 | conservation policies and mitigation strategies.", | 119 | conservation policies and mitigation strategies.", | ||
| 106 | "notes_translated": { | 120 | "notes_translated": { | ||
| 107 | "en": "Rapidly expanding road networks have been a key driver of | 121 | "en": "Rapidly expanding road networks have been a key driver of | ||
| 108 | the fragmentation and isolation of many wildlife species, and are a | 122 | the fragmentation and isolation of many wildlife species, and are a | ||
| 109 | source of significant mortality due to collisions with vehicles. But | 123 | source of significant mortality due to collisions with vehicles. But | ||
| 110 | not all animals are affected equally by transportation infrastructure, | 124 | not all animals are affected equally by transportation infrastructure, | ||
| 111 | and in most cases little is known about the population-scale | 125 | and in most cases little is known about the population-scale | ||
| 112 | consequences of roads for wildlife. Even less information is available | 126 | consequences of roads for wildlife. Even less information is available | ||
| 113 | to characterize species\u2019 behavioral responses to roads. Although | 127 | to characterize species\u2019 behavioral responses to roads. Although | ||
| 114 | research shows that maned wolves (Chrysocyon brachyurus) in Brazil are | 128 | research shows that maned wolves (Chrysocyon brachyurus) in Brazil are | ||
| 115 | experiencing considerable fragmentation and road mortality, the degree | 129 | experiencing considerable fragmentation and road mortality, the degree | ||
| 116 | to which these disturbances are impacting the species\u2019 viability | 130 | to which these disturbances are impacting the species\u2019 viability | ||
| 117 | is unknown. The goal of this study was to analyze the potential | 131 | is unknown. The goal of this study was to analyze the potential | ||
| 118 | effects of roads on maned wolf population size and structure. We used | 132 | effects of roads on maned wolf population size and structure. We used | ||
| 119 | a simulation model to evaluate the population-scale consequences of | 133 | a simulation model to evaluate the population-scale consequences of | ||
| 120 | individual maned wolf interactions with roads, which can result in | 134 | individual maned wolf interactions with roads, which can result in | ||
| 121 | road crossing, avoidance, or mortality due to a collision with a | 135 | road crossing, avoidance, or mortality due to a collision with a | ||
| 122 | vehicle. We also forecasted where in Brazil these impacts might be | 136 | vehicle. We also forecasted where in Brazil these impacts might be | ||
| 123 | most significant. Our model incorporated species demographic and | 137 | most significant. Our model incorporated species demographic and | ||
| 124 | movement parameters, plus habitat quality and a map of the road | 138 | movement parameters, plus habitat quality and a map of the road | ||
| 125 | network. We found that even moderate rates of road mortality led to | 139 | network. We found that even moderate rates of road mortality led to | ||
| 126 | severe declines in population size, and that four specific locations | 140 | severe declines in population size, and that four specific locations | ||
| 127 | accounted for a disproportionate fraction | 141 | accounted for a disproportionate fraction | ||
| 128 | of\u00a0roadkill\u00a0events. Our approach will be generally useful | 142 | of\u00a0roadkill\u00a0events. Our approach will be generally useful | ||
| 129 | for evaluating the relative importance of road effects on species | 143 | for evaluating the relative importance of road effects on species | ||
| 130 | conservation in many ecological systems, for prioritizing data | 144 | conservation in many ecological systems, for prioritizing data | ||
| 131 | collection efforts, and for informing conservation policies and | 145 | collection efforts, and for informing conservation policies and | ||
| 132 | mitigation strategies.", | 146 | mitigation strategies.", | ||
| 133 | "es": "Rapidly expanding road networks have been a key driver of | 147 | "es": "Rapidly expanding road networks have been a key driver of | ||
| 134 | the fragmentation and isolation of many wildlife species, and are a | 148 | the fragmentation and isolation of many wildlife species, and are a | ||
| 135 | source of significant mortality due to collisions with vehicles. But | 149 | source of significant mortality due to collisions with vehicles. But | ||
| 136 | not all animals are affected equally by transportation infrastructure, | 150 | not all animals are affected equally by transportation infrastructure, | ||
| 137 | and in most cases little is known about the population-scale | 151 | and in most cases little is known about the population-scale | ||
| 138 | consequences of roads for wildlife. Even less information is available | 152 | consequences of roads for wildlife. Even less information is available | ||
| 139 | to characterize species\u2019 behavioral responses to roads. Although | 153 | to characterize species\u2019 behavioral responses to roads. Although | ||
| 140 | research shows that maned wolves (Chrysocyon brachyurus) in Brazil are | 154 | research shows that maned wolves (Chrysocyon brachyurus) in Brazil are | ||
| 141 | experiencing considerable fragmentation and road mortality, the degree | 155 | experiencing considerable fragmentation and road mortality, the degree | ||
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| 143 | is unknown. The goal of this study was to analyze the potential | 157 | is unknown. The goal of this study was to analyze the potential | ||
| 144 | effects of roads on maned wolf population size and structure. We used | 158 | effects of roads on maned wolf population size and structure. We used | ||
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| 146 | individual maned wolf interactions with roads, which can result in | 160 | individual maned wolf interactions with roads, which can result in | ||
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| 148 | vehicle. We also forecasted where in Brazil these impacts might be | 162 | vehicle. We also forecasted where in Brazil these impacts might be | ||
| 149 | most significant. Our model incorporated species demographic and | 163 | most significant. Our model incorporated species demographic and | ||
| 150 | movement parameters, plus habitat quality and a map of the road | 164 | movement parameters, plus habitat quality and a map of the road | ||
| 151 | network. We found that even moderate rates of road mortality led to | 165 | network. We found that even moderate rates of road mortality led to | ||
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| 153 | accounted for a disproportionate fraction of roadkill events. Our | 167 | accounted for a disproportionate fraction of roadkill events. Our | ||
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| 155 | importance of road effects on species conservation in many ecological | 169 | importance of road effects on species conservation in many ecological | ||
| 156 | systems, for prioritizing data collection efforts, and for informing | 170 | systems, for prioritizing data collection efforts, and for informing | ||
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