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en Magnitude, composition and spatiotemporal patterns of vertebrate roadkill at regional scales: a study in southern Spain. -
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del recurso Acceso al recurso a2026-06-25
(anteriormente2026-06-23
) en Magnitude, composition and spatiotemporal patterns of vertebrate roadkill at regional scales: a study in southern Spain.
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| 82 | "notes": "Although roadkill studies on a large scale are | 96 | "notes": "Although roadkill studies on a large scale are | ||
| 83 | challenging, they can provide valuable information to assess the | 97 | challenging, they can provide valuable information to assess the | ||
| 84 | impact of road traffic on animal populations. Over 22 months (between | 98 | impact of road traffic on animal populations. Over 22 months (between | ||
| 85 | July 2009\u2013June 2010, and April 2011\u2013March 2012) we surveyed | 99 | July 2009\u2013June 2010, and April 2011\u2013March 2012) we surveyed | ||
| 86 | 45 road sections of 10 km within a global biodiversity hotspot in | 100 | 45 road sections of 10 km within a global biodiversity hotspot in | ||
| 87 | Andalusia (87,000 km2), in southern Spain. We divided the region into | 101 | Andalusia (87,000 km2), in southern Spain. We divided the region into | ||
| 88 | five ecoregions differing in environmental conditions and landscape | 102 | five ecoregions differing in environmental conditions and landscape | ||
| 89 | characteristics and recorded the relative magnitude, composition and | 103 | characteristics and recorded the relative magnitude, composition and | ||
| 90 | spatiotemporal patterns of vertebrate (birds, mammal, amphibians, and | 104 | spatiotemporal patterns of vertebrate (birds, mammal, amphibians, and | ||
| 91 | reptiles) mortality. We used roadkill data from monthly surveys of | 105 | reptiles) mortality. We used roadkill data from monthly surveys of | ||
| 92 | road stretches with different speed limits, traffic volume, road | 106 | road stretches with different speed limits, traffic volume, road | ||
| 93 | design, and adjacent landscape composition. Roadkills varied over time | 107 | design, and adjacent landscape composition. Roadkills varied over time | ||
| 94 | and were not randomly distributed across ecoregions and road types. | 108 | and were not randomly distributed across ecoregions and road types. | ||
| 95 | Overall, the groups most frequently encountered were mammals (54.4 % | 109 | Overall, the groups most frequently encountered were mammals (54.4 % | ||
| 96 | of total roadkills) and birds (36.2 %). Mortality rates in these two | 110 | of total roadkills) and birds (36.2 %). Mortality rates in these two | ||
| 97 | groups were higher on highways than on national or local roads, | 111 | groups were higher on highways than on national or local roads, | ||
| 98 | whereas those of amphibians (4.6 %) and reptiles (4.3 %) did not | 112 | whereas those of amphibians (4.6 %) and reptiles (4.3 %) did not | ||
| 99 | differ between road types. Except for mammals, the observed variation | 113 | differ between road types. Except for mammals, the observed variation | ||
| 100 | in vertebrate roadkills across ecoregions reflects the patterns of | 114 | in vertebrate roadkills across ecoregions reflects the patterns of | ||
| 101 | species richness previously described in the literature. Roadkills | 115 | species richness previously described in the literature. Roadkills | ||
| 102 | were concentrated over relatively short periods and this pattern was | 116 | were concentrated over relatively short periods and this pattern was | ||
| 103 | repeated over study periods and for all vertebrate classes. Our | 117 | repeated over study periods and for all vertebrate classes. Our | ||
| 104 | findings provide baseline information about road types, time periods | 118 | findings provide baseline information about road types, time periods | ||
| 105 | and taxa with a higher probability of roadkills across an extensive | 119 | and taxa with a higher probability of roadkills across an extensive | ||
| 106 | region. These data represent an essential step towards the future | 120 | region. These data represent an essential step towards the future | ||
| 107 | implementation of broad\u2013scale mitigation measures.", | 121 | implementation of broad\u2013scale mitigation measures.", | ||
| 108 | "notes_translated": { | 122 | "notes_translated": { | ||
| 109 | "en": "Although roadkill studies on a large scale are challenging, | 123 | "en": "Although roadkill studies on a large scale are challenging, | ||
| 110 | they can provide valuable information to assess the impact of road | 124 | they can provide valuable information to assess the impact of road | ||
| 111 | traffic on animal populations. Over 22 months (between July | 125 | traffic on animal populations. Over 22 months (between July | ||
| 112 | 2009\u2013June 2010, and April 2011\u2013March 2012) we surveyed 45 | 126 | 2009\u2013June 2010, and April 2011\u2013March 2012) we surveyed 45 | ||
| 113 | road sections of 10 km within a global biodiversity hotspot in | 127 | road sections of 10 km within a global biodiversity hotspot in | ||
| 114 | Andalusia (87,000 km2), in southern Spain. We divided the region into | 128 | Andalusia (87,000 km2), in southern Spain. We divided the region into | ||
| 115 | five ecoregions differing in environmental conditions and landscape | 129 | five ecoregions differing in environmental conditions and landscape | ||
| 116 | characteristics and recorded the relative magnitude, composition and | 130 | characteristics and recorded the relative magnitude, composition and | ||
| 117 | spatiotemporal patterns of vertebrate (birds, mammal, amphibians, and | 131 | spatiotemporal patterns of vertebrate (birds, mammal, amphibians, and | ||
| 118 | reptiles) mortality. We used roadkill data from monthly surveys of | 132 | reptiles) mortality. We used roadkill data from monthly surveys of | ||
| 119 | road stretches with different speed limits, traffic volume, road | 133 | road stretches with different speed limits, traffic volume, road | ||
| 120 | design, and adjacent landscape composition. Roadkills varied over time | 134 | design, and adjacent landscape composition. Roadkills varied over time | ||
| 121 | and were not randomly distributed across ecoregions and road types. | 135 | and were not randomly distributed across ecoregions and road types. | ||
| 122 | Overall, the groups most frequently encountered were mammals (54.4 % | 136 | Overall, the groups most frequently encountered were mammals (54.4 % | ||
| 123 | of total roadkills) and birds (36.2 %). Mortality rates in these two | 137 | of total roadkills) and birds (36.2 %). Mortality rates in these two | ||
| 124 | groups were higher on highways than on national or local roads, | 138 | groups were higher on highways than on national or local roads, | ||
| 125 | whereas those of amphibians (4.6 %) and reptiles (4.3 %) did not | 139 | whereas those of amphibians (4.6 %) and reptiles (4.3 %) did not | ||
| 126 | differ between road types. Except for mammals, the observed variation | 140 | differ between road types. Except for mammals, the observed variation | ||
| 127 | in vertebrate roadkills across ecoregions reflects the patterns of | 141 | in vertebrate roadkills across ecoregions reflects the patterns of | ||
| 128 | species richness previously described in the literature. Roadkills | 142 | species richness previously described in the literature. Roadkills | ||
| 129 | were concentrated over relatively short periods and this pattern was | 143 | were concentrated over relatively short periods and this pattern was | ||
| 130 | repeated over study periods and for all vertebrate classes. Our | 144 | repeated over study periods and for all vertebrate classes. Our | ||
| 131 | findings provide baseline information about road types, time periods | 145 | findings provide baseline information about road types, time periods | ||
| 132 | and taxa with a higher probability of roadkills across an extensive | 146 | and taxa with a higher probability of roadkills across an extensive | ||
| 133 | region. These data represent an essential step towards the future | 147 | region. These data represent an essential step towards the future | ||
| 134 | implementation of broad\u2013scale mitigation measures.", | 148 | implementation of broad\u2013scale mitigation measures.", | ||
| 135 | "es": "Although roadkill studies on a large scale are challenging, | 149 | "es": "Although roadkill studies on a large scale are challenging, | ||
| 136 | they can provide valuable information to assess the impact of road | 150 | they can provide valuable information to assess the impact of road | ||
| 137 | traffic on animal populations. Over 22 months (between July | 151 | traffic on animal populations. Over 22 months (between July | ||
| 138 | 2009\u2013June 2010, and April 2011\u2013March 2012) we surveyed 45 | 152 | 2009\u2013June 2010, and April 2011\u2013March 2012) we surveyed 45 | ||
| 139 | road sections of 10 km within a global biodiversity hotspot in | 153 | road sections of 10 km within a global biodiversity hotspot in | ||
| 140 | Andalusia (87,000 km2), in southern Spain. We divided the region into | 154 | Andalusia (87,000 km2), in southern Spain. We divided the region into | ||
| 141 | five ecoregions differing in environmental conditions and landscape | 155 | five ecoregions differing in environmental conditions and landscape | ||
| 142 | characteristics and recorded the relative magnitude, composition and | 156 | characteristics and recorded the relative magnitude, composition and | ||
| 143 | spatiotemporal patterns of vertebrate (birds, mammal, amphibians, and | 157 | spatiotemporal patterns of vertebrate (birds, mammal, amphibians, and | ||
| 144 | reptiles) mortality. We used roadkill data from monthly surveys of | 158 | reptiles) mortality. We used roadkill data from monthly surveys of | ||
| 145 | road stretches with different speed limits, traffic volume, road | 159 | road stretches with different speed limits, traffic volume, road | ||
| 146 | design, and adjacent landscape composition. Roadkills varied over time | 160 | design, and adjacent landscape composition. Roadkills varied over time | ||
| 147 | and were not randomly distributed across ecoregions and road types. | 161 | and were not randomly distributed across ecoregions and road types. | ||
| 148 | Overall, the groups most frequently encountered were mammals (54.4 % | 162 | Overall, the groups most frequently encountered were mammals (54.4 % | ||
| 149 | of total roadkills) and birds (36.2 %). Mortality rates in these two | 163 | of total roadkills) and birds (36.2 %). Mortality rates in these two | ||
| 150 | groups were higher on highways than on national or local roads, | 164 | groups were higher on highways than on national or local roads, | ||
| 151 | whereas those of amphibians (4.6 %) and reptiles (4.3 %) did not | 165 | whereas those of amphibians (4.6 %) and reptiles (4.3 %) did not | ||
| 152 | differ between road types. Except for mammals, the observed variation | 166 | differ between road types. Except for mammals, the observed variation | ||
| 153 | in vertebrate roadkills across ecoregions reflects the patterns of | 167 | in vertebrate roadkills across ecoregions reflects the patterns of | ||
| 154 | species richness previously described in the literature. Roadkills | 168 | species richness previously described in the literature. Roadkills | ||
| 155 | were concentrated over relatively short periods and this pattern was | 169 | were concentrated over relatively short periods and this pattern was | ||
| 156 | repeated over study periods and for all vertebrate classes. Our | 170 | repeated over study periods and for all vertebrate classes. Our | ||
| 157 | findings provide baseline information about road types, time periods | 171 | findings provide baseline information about road types, time periods | ||
| 158 | and taxa with a higher probability of roadkills across an extensive | 172 | and taxa with a higher probability of roadkills across an extensive | ||
| 159 | region. These data represent an essential step towards the future | 173 | region. These data represent an essential step towards the future | ||
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