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En el instante 25 de junio de 2026, 12:33:25 UTC,
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Modificado el valor del campo
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a2026-06-25
en Community response of mammalian predators and their prey to motorways: implications for predator–prey dynamics. -
Modificado el valor del campo
modified
del recurso Acceso al recurso a2026-06-25
(anteriormente2026-06-23
) en Community response of mammalian predators and their prey to motorways: implications for predator–prey dynamics.
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| 79 | "notes": "Understanding the interactions between predators and prey | 93 | "notes": "Understanding the interactions between predators and prey | ||
| 80 | is essential for predicting the effects of disturbances to ecosystems. | 94 | is essential for predicting the effects of disturbances to ecosystems. | ||
| 81 | Motorways produce changes in the surrounding biotic and abiotic | 95 | Motorways produce changes in the surrounding biotic and abiotic | ||
| 82 | environment and hence have multiple impacts on wildlife. Some species | 96 | environment and hence have multiple impacts on wildlife. Some species | ||
| 83 | are known to change their activity patterns in the proximity of | 97 | are known to change their activity patterns in the proximity of | ||
| 84 | motorways but the implications for the structure of food webs are | 98 | motorways but the implications for the structure of food webs are | ||
| 85 | unknown. This study analyzes the activity patterns of both mammalian | 99 | unknown. This study analyzes the activity patterns of both mammalian | ||
| 86 | predators and their prey species near nine motorways in attempt to | 100 | predators and their prey species near nine motorways in attempt to | ||
| 87 | clarify how motorways affect the mammalian community. Habitat | 101 | clarify how motorways affect the mammalian community. Habitat | ||
| 88 | structural variables were also sampled to control the effects of | 102 | structural variables were also sampled to control the effects of | ||
| 89 | microhabitat on relative prey abundance. Our results revealed | 103 | microhabitat on relative prey abundance. Our results revealed | ||
| 90 | different activity patterns of both predators and prey near motorways | 104 | different activity patterns of both predators and prey near motorways | ||
| 91 | that are independent of structural differences in microhabitat. Both | 105 | that are independent of structural differences in microhabitat. Both | ||
| 92 | the red fox and small mammals were found to use the zone close to the | 106 | the red fox and small mammals were found to use the zone close to the | ||
| 93 | motorways more frequently, whereas lagomorphs and mustelids were less | 107 | motorways more frequently, whereas lagomorphs and mustelids were less | ||
| 94 | active there. These differences suggest that motorways favor the | 108 | active there. These differences suggest that motorways favor the | ||
| 95 | population of the predator that is most tolerant of human activity, | 109 | population of the predator that is most tolerant of human activity, | ||
| 96 | the red fox, whose activity could have both direct and indirect | 110 | the red fox, whose activity could have both direct and indirect | ||
| 97 | effects on that of other members of the predator and prey community. | 111 | effects on that of other members of the predator and prey community. | ||
| 98 | On the one hand, the red fox seems to act as \u201ctop predator\u201d | 112 | On the one hand, the red fox seems to act as \u201ctop predator\u201d | ||
| 99 | and mustelids to follow a \u201csafety match\u201d strategy avoiding | 113 | and mustelids to follow a \u201csafety match\u201d strategy avoiding | ||
| 100 | the area close to the motorway where fox is more active. On the other | 114 | the area close to the motorway where fox is more active. On the other | ||
| 101 | hand, abundances of prey species are negatively associated with the | 115 | hand, abundances of prey species are negatively associated with the | ||
| 102 | activity of their most frequent predators. This study is the first to | 116 | activity of their most frequent predators. This study is the first to | ||
| 103 | assess how the proximity to motorways affects the activity of mammals | 117 | assess how the proximity to motorways affects the activity of mammals | ||
| 104 | in two levels of the food web and opens the field for research to | 118 | in two levels of the food web and opens the field for research to | ||
| 105 | understand the processes driving the detected patterns. Moreover, such | 119 | understand the processes driving the detected patterns. Moreover, such | ||
| 106 | effects at the community scale should be taken into account when | 120 | effects at the community scale should be taken into account when | ||
| 107 | evaluating the impacts of motorways on the surrounding ecosystems.\n | 121 | evaluating the impacts of motorways on the surrounding ecosystems.\n | ||
| 108 | Palabras clave: Mammal, Motorway", | 122 | Palabras clave: Mammal, Motorway", | ||
| 109 | "notes_translated": { | 123 | "notes_translated": { | ||
| 110 | "en": "Understanding the interactions between predators and prey | 124 | "en": "Understanding the interactions between predators and prey | ||
| 111 | is essential for predicting the effects of disturbances to ecosystems. | 125 | is essential for predicting the effects of disturbances to ecosystems. | ||
| 112 | Motorways produce changes in the surrounding biotic and abiotic | 126 | Motorways produce changes in the surrounding biotic and abiotic | ||
| 113 | environment and hence have multiple impacts on wildlife. Some species | 127 | environment and hence have multiple impacts on wildlife. Some species | ||
| 114 | are known to change their activity patterns in the proximity of | 128 | are known to change their activity patterns in the proximity of | ||
| 115 | motorways but the implications for the structure of food webs are | 129 | motorways but the implications for the structure of food webs are | ||
| 116 | unknown. This study analyzes the activity patterns of both mammalian | 130 | unknown. This study analyzes the activity patterns of both mammalian | ||
| 117 | predators and their prey species near nine motorways in attempt to | 131 | predators and their prey species near nine motorways in attempt to | ||
| 118 | clarify how motorways affect the mammalian community. Habitat | 132 | clarify how motorways affect the mammalian community. Habitat | ||
| 119 | structural variables were also sampled to control the effects of | 133 | structural variables were also sampled to control the effects of | ||
| 120 | microhabitat on relative prey abundance. Our results revealed | 134 | microhabitat on relative prey abundance. Our results revealed | ||
| 121 | different activity patterns of both predators and prey near motorways | 135 | different activity patterns of both predators and prey near motorways | ||
| 122 | that are independent of structural differences in microhabitat. Both | 136 | that are independent of structural differences in microhabitat. Both | ||
| 123 | the red fox and small mammals were found to use the zone close to the | 137 | the red fox and small mammals were found to use the zone close to the | ||
| 124 | motorways more frequently, whereas lagomorphs and mustelids were less | 138 | motorways more frequently, whereas lagomorphs and mustelids were less | ||
| 125 | active there. These differences suggest that motorways favor the | 139 | active there. These differences suggest that motorways favor the | ||
| 126 | population of the predator that is most tolerant of human activity, | 140 | population of the predator that is most tolerant of human activity, | ||
| 127 | the red fox, whose activity could have both direct and indirect | 141 | the red fox, whose activity could have both direct and indirect | ||
| 128 | effects on that of other members of the predator and prey community. | 142 | effects on that of other members of the predator and prey community. | ||
| 129 | On the one hand, the red fox seems to act as \u201ctop predator\u201d | 143 | On the one hand, the red fox seems to act as \u201ctop predator\u201d | ||
| 130 | and mustelids to follow a \u201csafety match\u201d strategy avoiding | 144 | and mustelids to follow a \u201csafety match\u201d strategy avoiding | ||
| 131 | the area close to the motorway where fox is more active. On the other | 145 | the area close to the motorway where fox is more active. On the other | ||
| 132 | hand, abundances of prey species are negatively associated with the | 146 | hand, abundances of prey species are negatively associated with the | ||
| 133 | activity of their most frequent predators. This study is the first to | 147 | activity of their most frequent predators. This study is the first to | ||
| 134 | assess how the proximity to motorways affects the activity of mammals | 148 | assess how the proximity to motorways affects the activity of mammals | ||
| 135 | in two levels of the food web and opens the field for research to | 149 | in two levels of the food web and opens the field for research to | ||
| 136 | understand the processes driving the detected patterns. Moreover, such | 150 | understand the processes driving the detected patterns. Moreover, such | ||
| 137 | effects at the community scale should be taken into account when | 151 | effects at the community scale should be taken into account when | ||
| 138 | evaluating the impacts of motorways on the surrounding ecosystems.", | 152 | evaluating the impacts of motorways on the surrounding ecosystems.", | ||
| 139 | "es": "Understanding the interactions between predators and prey | 153 | "es": "Understanding the interactions between predators and prey | ||
| 140 | is essential for predicting the effects of disturbances to ecosystems. | 154 | is essential for predicting the effects of disturbances to ecosystems. | ||
| 141 | Motorways produce changes in the surrounding biotic and abiotic | 155 | Motorways produce changes in the surrounding biotic and abiotic | ||
| 142 | environment and hence have multiple impacts on wildlife. Some species | 156 | environment and hence have multiple impacts on wildlife. Some species | ||
| 143 | are known to change their activity patterns in the proximity of | 157 | are known to change their activity patterns in the proximity of | ||
| 144 | motorways but the implications for the structure of food webs are | 158 | motorways but the implications for the structure of food webs are | ||
| 145 | unknown. This study analyzes the activity patterns of both mammalian | 159 | unknown. This study analyzes the activity patterns of both mammalian | ||
| 146 | predators and their prey species near nine motorways in attempt to | 160 | predators and their prey species near nine motorways in attempt to | ||
| 147 | clarify how motorways affect the mammalian community. Habitat | 161 | clarify how motorways affect the mammalian community. Habitat | ||
| 148 | structural variables were also sampled to control the effects of | 162 | structural variables were also sampled to control the effects of | ||
| 149 | microhabitat on relative prey abundance. Our results revealed | 163 | microhabitat on relative prey abundance. Our results revealed | ||
| 150 | different activity patterns of both predators and prey near motorways | 164 | different activity patterns of both predators and prey near motorways | ||
| 151 | that are independent of structural differences in microhabitat. Both | 165 | that are independent of structural differences in microhabitat. Both | ||
| 152 | the red fox and small mammals were found to use the zone close to the | 166 | the red fox and small mammals were found to use the zone close to the | ||
| 153 | motorways more frequently, whereas lagomorphs and mustelids were less | 167 | motorways more frequently, whereas lagomorphs and mustelids were less | ||
| 154 | active there. These differences suggest that motorways favor the | 168 | active there. These differences suggest that motorways favor the | ||
| 155 | population of the predator that is most tolerant of human activity, | 169 | population of the predator that is most tolerant of human activity, | ||
| 156 | the red fox, whose activity could have both direct and indirect | 170 | the red fox, whose activity could have both direct and indirect | ||
| 157 | effects on that of other members of the predator and prey community. | 171 | effects on that of other members of the predator and prey community. | ||
| 158 | On the one hand, the red fox seems to act as \u201ctop predator\u201d | 172 | On the one hand, the red fox seems to act as \u201ctop predator\u201d | ||
| 159 | and mustelids to follow a \u201csafety match\u201d strategy avoiding | 173 | and mustelids to follow a \u201csafety match\u201d strategy avoiding | ||
| 160 | the area close to the motorway where fox is more active. On the other | 174 | the area close to the motorway where fox is more active. On the other | ||
| 161 | hand, abundances of prey species are negatively associated with the | 175 | hand, abundances of prey species are negatively associated with the | ||
| 162 | activity of their most frequent predators. This study is the first to | 176 | activity of their most frequent predators. This study is the first to | ||
| 163 | assess how the proximity to motorways affects the activity of mammals | 177 | assess how the proximity to motorways affects the activity of mammals | ||
| 164 | in two levels of the food web and opens the field for research to | 178 | in two levels of the food web and opens the field for research to | ||
| 165 | understand the processes driving the detected patterns. Moreover, such | 179 | understand the processes driving the detected patterns. Moreover, such | ||
| 166 | effects at the community scale should be taken into account when | 180 | effects at the community scale should be taken into account when | ||
| 167 | evaluating the impacts of motorways on the surrounding ecosystems.\n | 181 | evaluating the impacts of motorways on the surrounding ecosystems.\n | ||
| 168 | Palabras clave: Mammal, Motorway" | 182 | Palabras clave: Mammal, Motorway" | ||
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