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Modificado el valor del campo
spatial_coverage
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en The risk of being hungry: influence of prey availability in verges on predator skills.
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| 77 | "notes": "Road verges may provide important refuges for small fauna, | 77 | "notes": "Road verges may provide important refuges for small fauna, | ||
| 78 | particularly when roads cross intensive agricultural or grazed | 78 | particularly when roads cross intensive agricultural or grazed | ||
| 79 | landscapes. In these circumstances, the increasing use of verges by | 79 | landscapes. In these circumstances, the increasing use of verges by | ||
| 80 | important prey species may attract predators to road surroundings | 80 | important prey species may attract predators to road surroundings | ||
| 81 | increasing the likelihood of their roadkill. The main goal of this | 81 | increasing the likelihood of their roadkill. The main goal of this | ||
| 82 | study is to evaluate the importance of prey abundance (rabbits and | 82 | study is to evaluate the importance of prey abundance (rabbits and | ||
| 83 | small mammals) in verges on predator road fatalities. We analyzed this | 83 | small mammals) in verges on predator road fatalities. We analyzed this | ||
| 84 | effect on different kinds of predators including snakes, owls and | 84 | effect on different kinds of predators including snakes, owls and | ||
| 85 | mammal carnivores. The study took place on a 10km stretch of a main | 85 | mammal carnivores. The study took place on a 10km stretch of a main | ||
| 86 | National Road (EN4) in southern Portugal. Small mammal abundance was | 86 | National Road (EN4) in southern Portugal. Small mammal abundance was | ||
| 87 | evaluated as the number of animals caught at 200 Sherman live traps, | 87 | evaluated as the number of animals caught at 200 Sherman live traps, | ||
| 88 | located at 50 m interval along the road. Rabbit counts were assessed | 88 | located at 50 m interval along the road. Rabbit counts were assessed | ||
| 89 | in ten morning car cruises, moving at a constant speed of about | 89 | in ten morning car cruises, moving at a constant speed of about | ||
| 90 | 20km/h. Landscape and road characteristics were also considered in the | 90 | 20km/h. Landscape and road characteristics were also considered in the | ||
| 91 | analysis. Relationships between predator mortality and explanatory | 91 | analysis. Relationships between predator mortality and explanatory | ||
| 92 | variables (prey abundance, landscape and road features) were evaluated | 92 | variables (prey abundance, landscape and road features) were evaluated | ||
| 93 | by means of Generalized Linear Models (GLM) and multivariate | 93 | by means of Generalized Linear Models (GLM) and multivariate | ||
| 94 | Redundancy Analysis (RDA). Explained variance of each group of | 94 | Redundancy Analysis (RDA). Explained variance of each group of | ||
| 95 | explanatory variables was accounted through a Variance Partitioning | 95 | explanatory variables was accounted through a Variance Partitioning | ||
| 96 | procedure. Our results show that prey abundance on verges enhances the | 96 | procedure. Our results show that prey abundance on verges enhances the | ||
| 97 | likelihood of predator mortality, even though landscape attributes | 97 | likelihood of predator mortality, even though landscape attributes | ||
| 98 | explain the main variation in predator road-kills. Among preys, Wood | 98 | explain the main variation in predator road-kills. Among preys, Wood | ||
| 99 | Mouse and Rabbits were the species that most contributed to this | 99 | Mouse and Rabbits were the species that most contributed to this | ||
| 100 | outcome. In contrast, road features were the group of variables with | 100 | outcome. In contrast, road features were the group of variables with | ||
| 101 | lower power in explaining predator fatalities. Therefore, actions | 101 | lower power in explaining predator fatalities. Therefore, actions | ||
| 102 | aiming to mitigate predator roadkills must consider the management of | 102 | aiming to mitigate predator roadkills must consider the management of | ||
| 103 | vegetation on verges in order to diminish prey abundance in these | 103 | vegetation on verges in order to diminish prey abundance in these | ||
| 104 | areas, thus reducing predator attractiveness. On the other hand, such | 104 | areas, thus reducing predator attractiveness. On the other hand, such | ||
| 105 | treatments may jeopardize one of the most important refuges for small | 105 | treatments may jeopardize one of the most important refuges for small | ||
| 106 | fauna when roads cross intensively grazed and agricultural areas.", | 106 | fauna when roads cross intensively grazed and agricultural areas.", | ||
| 107 | "notes_translated": { | 107 | "notes_translated": { | ||
| 108 | "en": "Road verges may provide important refuges for small fauna, | 108 | "en": "Road verges may provide important refuges for small fauna, | ||
| 109 | particularly when roads cross intensive agricultural or grazed | 109 | particularly when roads cross intensive agricultural or grazed | ||
| 110 | landscapes. In these circumstances, the increasing use of verges by | 110 | landscapes. In these circumstances, the increasing use of verges by | ||
| 111 | important prey species may attract predators to road surroundings | 111 | important prey species may attract predators to road surroundings | ||
| 112 | increasing the likelihood of their roadkill. The main goal of this | 112 | increasing the likelihood of their roadkill. The main goal of this | ||
| 113 | study is to evaluate the importance of prey abundance (rabbits and | 113 | study is to evaluate the importance of prey abundance (rabbits and | ||
| 114 | small mammals) in verges on predator road fatalities. We analyzed this | 114 | small mammals) in verges on predator road fatalities. We analyzed this | ||
| 115 | effect on different kinds of predators including snakes, owls and | 115 | effect on different kinds of predators including snakes, owls and | ||
| 116 | mammal carnivores. The study took place on a 10km stretch of a main | 116 | mammal carnivores. The study took place on a 10km stretch of a main | ||
| 117 | National Road (EN4) in southern Portugal. Small mammal abundance was | 117 | National Road (EN4) in southern Portugal. Small mammal abundance was | ||
| 118 | evaluated as the number of animals caught at 200 Sherman live traps, | 118 | evaluated as the number of animals caught at 200 Sherman live traps, | ||
| 119 | located at 50 m interval along the road. Rabbit counts were assessed | 119 | located at 50 m interval along the road. Rabbit counts were assessed | ||
| 120 | in ten morning car cruises, moving at a constant speed of about | 120 | in ten morning car cruises, moving at a constant speed of about | ||
| 121 | 20km/h. Landscape and road characteristics were also considered in the | 121 | 20km/h. Landscape and road characteristics were also considered in the | ||
| 122 | analysis. Relationships between predator mortality and explanatory | 122 | analysis. Relationships between predator mortality and explanatory | ||
| 123 | variables (prey abundance, landscape and road features) were evaluated | 123 | variables (prey abundance, landscape and road features) were evaluated | ||
| 124 | by means of Generalized Linear Models (GLM) and multivariate | 124 | by means of Generalized Linear Models (GLM) and multivariate | ||
| 125 | Redundancy Analysis (RDA). Explained variance of each group of | 125 | Redundancy Analysis (RDA). Explained variance of each group of | ||
| 126 | explanatory variables was accounted through a Variance Partitioning | 126 | explanatory variables was accounted through a Variance Partitioning | ||
| 127 | procedure. Our results show that prey abundance on\nverges enhances | 127 | procedure. Our results show that prey abundance on\nverges enhances | ||
| 128 | the likelihood of predator mortality, even though landscape attributes | 128 | the likelihood of predator mortality, even though landscape attributes | ||
| 129 | explain the main variation in predator road-kills. Among preys, Wood | 129 | explain the main variation in predator road-kills. Among preys, Wood | ||
| 130 | Mouse and Rabbits were the species that most contributed to this | 130 | Mouse and Rabbits were the species that most contributed to this | ||
| 131 | outcome. In contrast, road features were the group of variables with | 131 | outcome. In contrast, road features were the group of variables with | ||
| 132 | lower power in explaining predator fatalities. Therefore, actions | 132 | lower power in explaining predator fatalities. Therefore, actions | ||
| 133 | aiming to mitigate predator roadkills must consider the management of | 133 | aiming to mitigate predator roadkills must consider the management of | ||
| 134 | vegetation on verges in order to diminish prey abundance in these | 134 | vegetation on verges in order to diminish prey abundance in these | ||
| 135 | areas, thus reducing predator attractiveness. On the other hand, such | 135 | areas, thus reducing predator attractiveness. On the other hand, such | ||
| 136 | treatments may jeopardize one of the most important refuges for small | 136 | treatments may jeopardize one of the most important refuges for small | ||
| 137 | fauna when roads cross intensively grazed and agricultural areas.", | 137 | fauna when roads cross intensively grazed and agricultural areas.", | ||
| 138 | "es": "Road verges may provide important refuges for small fauna, | 138 | "es": "Road verges may provide important refuges for small fauna, | ||
| 139 | particularly when roads cross intensive agricultural or grazed | 139 | particularly when roads cross intensive agricultural or grazed | ||
| 140 | landscapes. In these circumstances, the increasing use of verges by | 140 | landscapes. In these circumstances, the increasing use of verges by | ||
| 141 | important prey species may attract predators to road surroundings | 141 | important prey species may attract predators to road surroundings | ||
| 142 | increasing the likelihood of their roadkill. The main goal of this | 142 | increasing the likelihood of their roadkill. The main goal of this | ||
| 143 | study is to evaluate the importance of prey abundance (rabbits and | 143 | study is to evaluate the importance of prey abundance (rabbits and | ||
| 144 | small mammals) in verges on predator road fatalities. We analyzed this | 144 | small mammals) in verges on predator road fatalities. We analyzed this | ||
| 145 | effect on different kinds of predators including snakes, owls and | 145 | effect on different kinds of predators including snakes, owls and | ||
| 146 | mammal carnivores. The study took place on a 10km stretch of a main | 146 | mammal carnivores. The study took place on a 10km stretch of a main | ||
| 147 | National Road (EN4) in southern Portugal. Small mammal abundance was | 147 | National Road (EN4) in southern Portugal. Small mammal abundance was | ||
| 148 | evaluated as the number of animals caught at 200 Sherman live traps, | 148 | evaluated as the number of animals caught at 200 Sherman live traps, | ||
| 149 | located at 50 m interval along the road. Rabbit counts were assessed | 149 | located at 50 m interval along the road. Rabbit counts were assessed | ||
| 150 | in ten morning car cruises, moving at a constant speed of about | 150 | in ten morning car cruises, moving at a constant speed of about | ||
| 151 | 20km/h. Landscape and road characteristics were also considered in the | 151 | 20km/h. Landscape and road characteristics were also considered in the | ||
| 152 | analysis. Relationships between predator mortality and explanatory | 152 | analysis. Relationships between predator mortality and explanatory | ||
| 153 | variables (prey abundance, landscape and road features) were evaluated | 153 | variables (prey abundance, landscape and road features) were evaluated | ||
| 154 | by means of Generalized Linear Models (GLM) and multivariate | 154 | by means of Generalized Linear Models (GLM) and multivariate | ||
| 155 | Redundancy Analysis (RDA). Explained variance of each group of | 155 | Redundancy Analysis (RDA). Explained variance of each group of | ||
| 156 | explanatory variables was accounted through a Variance Partitioning | 156 | explanatory variables was accounted through a Variance Partitioning | ||
| 157 | procedure. Our results show that prey abundance on verges enhances the | 157 | procedure. Our results show that prey abundance on verges enhances the | ||
| 158 | likelihood of predator mortality, even though landscape attributes | 158 | likelihood of predator mortality, even though landscape attributes | ||
| 159 | explain the main variation in predator road-kills. Among preys, Wood | 159 | explain the main variation in predator road-kills. Among preys, Wood | ||
| 160 | Mouse and Rabbits were the species that most contributed to this | 160 | Mouse and Rabbits were the species that most contributed to this | ||
| 161 | outcome. In contrast, road features were the group of variables with | 161 | outcome. In contrast, road features were the group of variables with | ||
| 162 | lower power in explaining predator fatalities. Therefore, actions | 162 | lower power in explaining predator fatalities. Therefore, actions | ||
| 163 | aiming to mitigate predator roadkills must consider the management of | 163 | aiming to mitigate predator roadkills must consider the management of | ||
| 164 | vegetation on verges in order to diminish prey abundance in these | 164 | vegetation on verges in order to diminish prey abundance in these | ||
| 165 | areas, thus reducing predator attractiveness. On the other hand, such | 165 | areas, thus reducing predator attractiveness. On the other hand, such | ||
| 166 | treatments may jeopardize one of the most important refuges for small | 166 | treatments may jeopardize one of the most important refuges for small | ||
| 167 | fauna when roads cross intensively grazed and agricultural areas." | 167 | fauna when roads cross intensively grazed and agricultural areas." | ||
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