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En el instante 23 de junio de 2026, 16:00:55 UTC,
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Modificado el valor del campo
spatial_coverage
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en Factors influencing vertebrate carcasses retention time on roads: a preliminary study on Mediterranean context.
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| 77 | "notes": "Monitoring vertebrate roadkills is a task increasingly | 77 | "notes": "Monitoring vertebrate roadkills is a task increasingly | ||
| 78 | done in the last decades in order to better evaluate the impact of | 78 | done in the last decades in order to better evaluate the impact of | ||
| 79 | roads on wildlife. However, these studies usually underestimate the | 79 | roads on wildlife. However, these studies usually underestimate the | ||
| 80 | real number of road kills counts, due to the sampling strategy and | 80 | real number of road kills counts, due to the sampling strategy and | ||
| 81 | because large time intervals (frequently weekly monitoring) are used | 81 | because large time intervals (frequently weekly monitoring) are used | ||
| 82 | between surveys. On summer of 2005 in central of Portugal, we carried | 82 | between surveys. On summer of 2005 in central of Portugal, we carried | ||
| 83 | out in a 26 km stretch of a main national road, a trial survey | 83 | out in a 26 km stretch of a main national road, a trial survey | ||
| 84 | consisting in 31 consecutive day\u2019s road kill monitoring. The | 84 | consisting in 31 consecutive day\u2019s road kill monitoring. The | ||
| 85 | initial position of the corpse on road and spatial geographic location | 85 | initial position of the corpse on road and spatial geographic location | ||
| 86 | were registered. Species biomass, daily temperatures, precipitation | 86 | were registered. Species biomass, daily temperatures, precipitation | ||
| 87 | and traffic load were also considered as possible factors affecting | 87 | and traffic load were also considered as possible factors affecting | ||
| 88 | the number of days the carcass remain on the road after animals have | 88 | the number of days the carcass remain on the road after animals have | ||
| 89 | been hit by a vehicle. We used the Cox regression to model the | 89 | been hit by a vehicle. We used the Cox regression to model the | ||
| 90 | survival time that road killed vertebrates remain on the road. A total | 90 | survival time that road killed vertebrates remain on the road. A total | ||
| 91 | of 188 corpses belonging to 40 vertebrate species were recorded. The | 91 | of 188 corpses belonging to 40 vertebrate species were recorded. The | ||
| 92 | biomass was the only significant factor influencing the maintenance of | 92 | biomass was the only significant factor influencing the maintenance of | ||
| 93 | a corpse on the road. Larger individuals (>500g) have 0.65 probability | 93 | a corpse on the road. Larger individuals (>500g) have 0.65 probability | ||
| 94 | of remaining on the road after three days, comparing to 0.35 for | 94 | of remaining on the road after three days, comparing to 0.35 for | ||
| 95 | medium ( ]50g-500g]) and 0.2 for small individuals (<50g). By the end | 95 | medium ( ]50g-500g]) and 0.2 for small individuals (<50g). By the end | ||
| 96 | of the trial survey, the majority (more than 95%) of the medium and | 96 | of the trial survey, the majority (more than 95%) of the medium and | ||
| 97 | small animals have already disappeared, while 20% of the larger | 97 | small animals have already disappeared, while 20% of the larger | ||
| 98 | animals may persist. Moreover, we would have lost almost 70% of the | 98 | animals may persist. Moreover, we would have lost almost 70% of the | ||
| 99 | corpses if road kills were monitored twice a month and almost 55% | 99 | corpses if road kills were monitored twice a month and almost 55% | ||
| 100 | under a weekly survey. Our results may have important conservation | 100 | under a weekly survey. Our results may have important conservation | ||
| 101 | implications when planning road kills monitoring, because small | 101 | implications when planning road kills monitoring, because small | ||
| 102 | species with a high conservation concern (e.g. bats) may not be | 102 | species with a high conservation concern (e.g. bats) may not be | ||
| 103 | counted on twice a month or weekly surveys.", | 103 | counted on twice a month or weekly surveys.", | ||
| 104 | "notes_translated": { | 104 | "notes_translated": { | ||
| 105 | "en": "Monitoring vertebrate roadkills is a task increasingly done | 105 | "en": "Monitoring vertebrate roadkills is a task increasingly done | ||
| 106 | in the last decades in order to better evaluate the impact of roads on | 106 | in the last decades in order to better evaluate the impact of roads on | ||
| 107 | wildlife. However, these studies usually underestimate the real number | 107 | wildlife. However, these studies usually underestimate the real number | ||
| 108 | of road kills counts, due to the sampling strategy and because large | 108 | of road kills counts, due to the sampling strategy and because large | ||
| 109 | time intervals (frequently weekly monitoring) are used between | 109 | time intervals (frequently weekly monitoring) are used between | ||
| 110 | surveys. On summer of 2005 in central of Portugal, we carried out in a | 110 | surveys. On summer of 2005 in central of Portugal, we carried out in a | ||
| 111 | 26 km stretch of a main national road, a trial survey consisting in 31 | 111 | 26 km stretch of a main national road, a trial survey consisting in 31 | ||
| 112 | consecutive day\u2019s road kill monitoring. The initial position of | 112 | consecutive day\u2019s road kill monitoring. The initial position of | ||
| 113 | the corpse on road and spatial geographic location were registered. | 113 | the corpse on road and spatial geographic location were registered. | ||
| 114 | Species biomass, daily temperatures, precipitation and traffic load | 114 | Species biomass, daily temperatures, precipitation and traffic load | ||
| 115 | were also considered as possible factors affecting the number of days | 115 | were also considered as possible factors affecting the number of days | ||
| 116 | the carcass remain on the road after animals have been hit by a | 116 | the carcass remain on the road after animals have been hit by a | ||
| 117 | vehicle. We used the Cox regression to model the survival time that | 117 | vehicle. We used the Cox regression to model the survival time that | ||
| 118 | road killed vertebrates remain on the road. A total of 188 corpses | 118 | road killed vertebrates remain on the road. A total of 188 corpses | ||
| 119 | belonging to 40 vertebrate species were recorded. The biomass was the | 119 | belonging to 40 vertebrate species were recorded. The biomass was the | ||
| 120 | only significant factor influencing the maintenance of a corpse on the | 120 | only significant factor influencing the maintenance of a corpse on the | ||
| 121 | road. Larger individuals (>500g) have 0.65 probability of remaining on | 121 | road. Larger individuals (>500g) have 0.65 probability of remaining on | ||
| 122 | the road after three days, comparing to 0.35 for medium ( ]50g-500g]) | 122 | the road after three days, comparing to 0.35 for medium ( ]50g-500g]) | ||
| 123 | and 0.2 for small individuals (<50g). By the end of the trial survey, | 123 | and 0.2 for small individuals (<50g). By the end of the trial survey, | ||
| 124 | the majority (more than 95%) of the medium and small animals have | 124 | the majority (more than 95%) of the medium and small animals have | ||
| 125 | already disappeared, while 20% of the larger animals may persist. | 125 | already disappeared, while 20% of the larger animals may persist. | ||
| 126 | Moreover, we would have lost almost 70% of the corpses if road kills | 126 | Moreover, we would have lost almost 70% of the corpses if road kills | ||
| 127 | were monitored twice a month and almost 55% under a weekly survey. Our | 127 | were monitored twice a month and almost 55% under a weekly survey. Our | ||
| 128 | results may have important conservation implications when planning | 128 | results may have important conservation implications when planning | ||
| 129 | road kills monitoring, because small species with a high conservation | 129 | road kills monitoring, because small species with a high conservation | ||
| 130 | concern (e.g. bats) may not be counted on twice a month or weekly | 130 | concern (e.g. bats) may not be counted on twice a month or weekly | ||
| 131 | surveys.", | 131 | surveys.", | ||
| 132 | "es": "Monitoring vertebrate roadkills is a task increasingly done | 132 | "es": "Monitoring vertebrate roadkills is a task increasingly done | ||
| 133 | in the last decades in order to better evaluate the impact of roads on | 133 | in the last decades in order to better evaluate the impact of roads on | ||
| 134 | wildlife. However, these studies usually underestimate the real number | 134 | wildlife. However, these studies usually underestimate the real number | ||
| 135 | of road kills counts, due to the sampling strategy and because large | 135 | of road kills counts, due to the sampling strategy and because large | ||
| 136 | time intervals (frequently weekly monitoring) are used between | 136 | time intervals (frequently weekly monitoring) are used between | ||
| 137 | surveys. On summer of 2005 in central of Portugal, we carried out in a | 137 | surveys. On summer of 2005 in central of Portugal, we carried out in a | ||
| 138 | 26 km stretch of a main national road, a trial survey consisting in 31 | 138 | 26 km stretch of a main national road, a trial survey consisting in 31 | ||
| 139 | consecutive day\u2019s road kill monitoring. The initial position of | 139 | consecutive day\u2019s road kill monitoring. The initial position of | ||
| 140 | the corpse on road and spatial geographic location were registered. | 140 | the corpse on road and spatial geographic location were registered. | ||
| 141 | Species biomass, daily temperatures, precipitation and traffic load | 141 | Species biomass, daily temperatures, precipitation and traffic load | ||
| 142 | were also considered as possible factors affecting the number of days | 142 | were also considered as possible factors affecting the number of days | ||
| 143 | the carcass remain on the road after animals have been hit by a | 143 | the carcass remain on the road after animals have been hit by a | ||
| 144 | vehicle. We used the Cox regression to model the survival time that | 144 | vehicle. We used the Cox regression to model the survival time that | ||
| 145 | road killed vertebrates remain on the road. A total of 188 corpses | 145 | road killed vertebrates remain on the road. A total of 188 corpses | ||
| 146 | belonging to 40 vertebrate species were recorded. The biomass was the | 146 | belonging to 40 vertebrate species were recorded. The biomass was the | ||
| 147 | only significant factor influencing the maintenance of a corpse on the | 147 | only significant factor influencing the maintenance of a corpse on the | ||
| 148 | road. Larger individuals (>500g) have 0.65 probability of remaining on | 148 | road. Larger individuals (>500g) have 0.65 probability of remaining on | ||
| 149 | the road after three days, comparing to 0.35 for medium ( ]50g-500g]) | 149 | the road after three days, comparing to 0.35 for medium ( ]50g-500g]) | ||
| 150 | and 0.2 for small individuals (<50g). By the end of the trial survey, | 150 | and 0.2 for small individuals (<50g). By the end of the trial survey, | ||
| 151 | the majority (more than 95%) of the medium and small animals have | 151 | the majority (more than 95%) of the medium and small animals have | ||
| 152 | already disappeared, while 20% of the larger animals may persist. | 152 | already disappeared, while 20% of the larger animals may persist. | ||
| 153 | Moreover, we would have lost almost 70% of the corpses if road kills | 153 | Moreover, we would have lost almost 70% of the corpses if road kills | ||
| 154 | were monitored twice a month and almost 55% under a weekly survey. Our | 154 | were monitored twice a month and almost 55% under a weekly survey. Our | ||
| 155 | results may have important conservation implications when planning | 155 | results may have important conservation implications when planning | ||
| 156 | road kills monitoring, because small species with a high conservation | 156 | road kills monitoring, because small species with a high conservation | ||
| 157 | concern (e.g. bats) may not be counted on twice a month or weekly | 157 | concern (e.g. bats) may not be counted on twice a month or weekly | ||
| 158 | surveys." | 158 | surveys." | ||
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