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en Spatial analysis of amphibian road mortality levels in northern Portugal country roads. -
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del recurso Acceso al recurso a2026-06-25
(anteriormente2026-06-23
) en Spatial analysis of amphibian road mortality levels in northern Portugal country roads.
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| 79 | "notes": "Animal mortality caused by vehicle collisions is one of | 93 | "notes": "Animal mortality caused by vehicle collisions is one of | ||
| 80 | the main ecological impacts of roads. Amphibians are the most affected | 94 | the main ecological impacts of roads. Amphibians are the most affected | ||
| 81 | group and road fatalities have a significant impact on population | 95 | group and road fatalities have a significant impact on population | ||
| 82 | dynamics and viability. Several studies on Iberian amphibians have | 96 | dynamics and viability. Several studies on Iberian amphibians have | ||
| 83 | shown the importance of country roads on amphibian road mortality, but | 97 | shown the importance of country roads on amphibian road mortality, but | ||
| 84 | still, little is known about the situation in northern Portugal. By | 98 | still, little is known about the situation in northern Portugal. By | ||
| 85 | being more permeable to amphibian passage, country roads represent a | 99 | being more permeable to amphibian passage, country roads represent a | ||
| 86 | greater source of mortality than highways, which act as barriers. | 100 | greater source of mortality than highways, which act as barriers. | ||
| 87 | Thus, mitigation measures should be applied, but due to the extensive | 101 | Thus, mitigation measures should be applied, but due to the extensive | ||
| 88 | road network, the identification of precise locations (hotspots) and | 102 | road network, the identification of precise locations (hotspots) and | ||
| 89 | variables related to animal-vehicle collision is needed to plan these | 103 | variables related to animal-vehicle collision is needed to plan these | ||
| 90 | measures successfully. The aim of the study was to analyse the spatial | 104 | measures successfully. The aim of the study was to analyse the spatial | ||
| 91 | occurrence and related factors linked to amphibian mortality on a | 105 | occurrence and related factors linked to amphibian mortality on a | ||
| 92 | number of country roads in northern Portugal, using spatial statistics | 106 | number of country roads in northern Portugal, using spatial statistics | ||
| 93 | implemented in GIS and applying a binary logistical regression. We | 107 | implemented in GIS and applying a binary logistical regression. We | ||
| 94 | surveyed 631 km of road corresponding to seven transects, and observed | 108 | surveyed 631 km of road corresponding to seven transects, and observed | ||
| 95 | 404 individual amphibians: 74 (18.3%) alive and 330 (81.7%) | 109 | 404 individual amphibians: 74 (18.3%) alive and 330 (81.7%) | ||
| 96 | road-killed. Bufo bufo represented 80% of the mortality records. Three | 110 | road-killed. Bufo bufo represented 80% of the mortality records. Three | ||
| 97 | transects showed clustered distribution of road-kills, and broadleaved | 111 | transects showed clustered distribution of road-kills, and broadleaved | ||
| 98 | forests and road ditches were the most important factors associated | 112 | forests and road ditches were the most important factors associated | ||
| 99 | with hotspots of road-kill. Logistic regression models showed that | 113 | with hotspots of road-kill. Logistic regression models showed that | ||
| 100 | habitat quality, Bufo bufo\u2019s habitat preferences, and road | 114 | habitat quality, Bufo bufo\u2019s habitat preferences, and road | ||
| 101 | ditches are positively associated with amphibians\u2019 road mortality | 115 | ditches are positively associated with amphibians\u2019 road mortality | ||
| 102 | in northern Portugal, whereas average altitude and length of walls | 116 | in northern Portugal, whereas average altitude and length of walls | ||
| 103 | were negatively associated. This study is a useful tool to understand | 117 | were negatively associated. This study is a useful tool to understand | ||
| 104 | spatial occurrence of amphibian road-kills in the face of applying | 118 | spatial occurrence of amphibian road-kills in the face of applying | ||
| 105 | mitigation measures on country roads from northern Portugal. This | 119 | mitigation measures on country roads from northern Portugal. This | ||
| 106 | study also considers the necessity of assessing the condition of | 120 | study also considers the necessity of assessing the condition of | ||
| 107 | amphibian local populations to understand their road-kills spatial | 121 | amphibian local populations to understand their road-kills spatial | ||
| 108 | patterns and the urgency to apply mitigation measures on country | 122 | patterns and the urgency to apply mitigation measures on country | ||
| 109 | roads.\n Palabras clave: Amphibian, Mortality", | 123 | roads.\n Palabras clave: Amphibian, Mortality", | ||
| 110 | "notes_translated": { | 124 | "notes_translated": { | ||
| 111 | "en": "Animal mortality caused by vehicle collisions is one of the | 125 | "en": "Animal mortality caused by vehicle collisions is one of the | ||
| 112 | main ecological impacts of roads. Amphibians are the most affected | 126 | main ecological impacts of roads. Amphibians are the most affected | ||
| 113 | group and road fatalities have a significant impact on population | 127 | group and road fatalities have a significant impact on population | ||
| 114 | dynamics and viability. Several studies on Iberian amphibians have | 128 | dynamics and viability. Several studies on Iberian amphibians have | ||
| 115 | shown the importance of country roads on amphibian road mortality, but | 129 | shown the importance of country roads on amphibian road mortality, but | ||
| 116 | still, little is known about the situation in northern Portugal. By | 130 | still, little is known about the situation in northern Portugal. By | ||
| 117 | being more permeable to amphibian passage, country roads represent a | 131 | being more permeable to amphibian passage, country roads represent a | ||
| 118 | greater source of mortality than highways, which act as barriers. | 132 | greater source of mortality than highways, which act as barriers. | ||
| 119 | Thus, mitigation measures should be applied, but due to the extensive | 133 | Thus, mitigation measures should be applied, but due to the extensive | ||
| 120 | road network, the identification of precise locations (hotspots) and | 134 | road network, the identification of precise locations (hotspots) and | ||
| 121 | variables related to animal-vehicle collision is needed to plan these | 135 | variables related to animal-vehicle collision is needed to plan these | ||
| 122 | measures successfully. The aim of the study was to analyse the spatial | 136 | measures successfully. The aim of the study was to analyse the spatial | ||
| 123 | occurrence and related factors linked to amphibian mortality on a | 137 | occurrence and related factors linked to amphibian mortality on a | ||
| 124 | number of country roads in northern Portugal \u2026", | 138 | number of country roads in northern Portugal \u2026", | ||
| 125 | "es": "Animal mortality caused by vehicle collisions is one of the | 139 | "es": "Animal mortality caused by vehicle collisions is one of the | ||
| 126 | main ecological impacts of roads. Amphibians are the most affected | 140 | main ecological impacts of roads. Amphibians are the most affected | ||
| 127 | group and road fatalities have a significant impact on population | 141 | group and road fatalities have a significant impact on population | ||
| 128 | dynamics and viability. Several studies on Iberian amphibians have | 142 | dynamics and viability. Several studies on Iberian amphibians have | ||
| 129 | shown the importance of country roads on amphibian road mortality, but | 143 | shown the importance of country roads on amphibian road mortality, but | ||
| 130 | still, little is known about the situation in northern Portugal. By | 144 | still, little is known about the situation in northern Portugal. By | ||
| 131 | being more permeable to amphibian passage, country roads represent a | 145 | being more permeable to amphibian passage, country roads represent a | ||
| 132 | greater source of mortality than highways, which act as barriers. | 146 | greater source of mortality than highways, which act as barriers. | ||
| 133 | Thus, mitigation measures should be applied, but due to the extensive | 147 | Thus, mitigation measures should be applied, but due to the extensive | ||
| 134 | road network, the identification of precise locations (hotspots) and | 148 | road network, the identification of precise locations (hotspots) and | ||
| 135 | variables related to animal-vehicle collision is needed to plan these | 149 | variables related to animal-vehicle collision is needed to plan these | ||
| 136 | measures successfully. The aim of the study was to analyse the spatial | 150 | measures successfully. The aim of the study was to analyse the spatial | ||
| 137 | occurrence and related factors linked to amphibian mortality on a | 151 | occurrence and related factors linked to amphibian mortality on a | ||
| 138 | number of country roads in northern Portugal, using spatial statistics | 152 | number of country roads in northern Portugal, using spatial statistics | ||
| 139 | implemented in GIS and applying a binary logistical regression. We | 153 | implemented in GIS and applying a binary logistical regression. We | ||
| 140 | surveyed 631 km of road corresponding to seven transects, and observed | 154 | surveyed 631 km of road corresponding to seven transects, and observed | ||
| 141 | 404 individual amphibians: 74 (18.3%) alive and 330 (81.7%) | 155 | 404 individual amphibians: 74 (18.3%) alive and 330 (81.7%) | ||
| 142 | road-killed. Bufo bufo represented 80% of the mortality records. Three | 156 | road-killed. Bufo bufo represented 80% of the mortality records. Three | ||
| 143 | transects showed clustered distribution of road-kills, and broadleaved | 157 | transects showed clustered distribution of road-kills, and broadleaved | ||
| 144 | forests and road ditches were the most important factors associated | 158 | forests and road ditches were the most important factors associated | ||
| 145 | with hotspots of road-kill. Logistic regression models showed that | 159 | with hotspots of road-kill. Logistic regression models showed that | ||
| 146 | habitat quality, Bufo bufo\u2019s habitat preferences, and road | 160 | habitat quality, Bufo bufo\u2019s habitat preferences, and road | ||
| 147 | ditches are positively associated with amphibians\u2019 road mortality | 161 | ditches are positively associated with amphibians\u2019 road mortality | ||
| 148 | in northern Portugal, whereas average altitude and length of walls | 162 | in northern Portugal, whereas average altitude and length of walls | ||
| 149 | were negatively associated. This study is a useful tool to understand | 163 | were negatively associated. This study is a useful tool to understand | ||
| 150 | spatial occurrence of amphibian road-kills in the face of applying | 164 | spatial occurrence of amphibian road-kills in the face of applying | ||
| 151 | mitigation measures on country roads from northern Portugal. This | 165 | mitigation measures on country roads from northern Portugal. This | ||
| 152 | study also considers the necessity of assessing the condition of | 166 | study also considers the necessity of assessing the condition of | ||
| 153 | amphibian local populations to understand their road-kills spatial | 167 | amphibian local populations to understand their road-kills spatial | ||
| 154 | patterns and the urgency to apply mitigation measures on country | 168 | patterns and the urgency to apply mitigation measures on country | ||
| 155 | roads.\n Palabras clave: Amphibian, Mortality" | 169 | roads.\n Palabras clave: Amphibian, Mortality" | ||
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