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a2026-06-25
en Effects of habitat encroachment by roads on space use and movement patterns of an endangered vole. -
Modificado el valor del campo
modified
del recurso Acceso al recurso a2026-06-25
(anteriormente2026-06-23
) en Effects of habitat encroachment by roads on space use and movement patterns of an endangered vole.
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| 6 | Santos, S.M.", | 6 | Santos, S.M.", | ||
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| 36 | "name": "Horta Fernandes, N., Ferreira, E., Pita, R., Mira, A. y | 36 | "name": "Horta Fernandes, N., Ferreira, E., Pita, R., Mira, A. y | ||
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| 51 | h\u00e1bitat se transforma en una serie de parches m\u00e1s | ||||
| 52 | peque\u00f1os de menor superficie total aislados entre s\u00ed por una | ||||
| 53 | matriz de h\u00e1bitats distinta de la original", | ||||
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| 60 | "2018 IENE International Conference. Abstract book", | 74 | "2018 IENE International Conference. Abstract book", | ||
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| 70 | "miteco_data_population": { | 84 | "miteco_data_population": { | ||
| 71 | "es": "" | 85 | "es": "" | ||
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| 73 | "miteco_data_territory": { | 87 | "miteco_data_territory": { | ||
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| 80 | "name": "4e2f816a-bddb-5a36-be4f-105756c9660f", | 94 | "name": "4e2f816a-bddb-5a36-be4f-105756c9660f", | ||
| 81 | "notes": "Roads are a significant cause of habitat fragmentation and | 95 | "notes": "Roads are a significant cause of habitat fragmentation and | ||
| 82 | a barrier to movement of several species across the world. Terrestrial | 96 | a barrier to movement of several species across the world. Terrestrial | ||
| 83 | species with low mobility, low abundance and specific habitat | 97 | species with low mobility, low abundance and specific habitat | ||
| 84 | requirements could be particularly affected by this kind of barriers | 98 | requirements could be particularly affected by this kind of barriers | ||
| 85 | concerning their movements. In the present study, we aimed to assess | 99 | concerning their movements. In the present study, we aimed to assess | ||
| 86 | the influence of habitat invasion by roads on space use and movements | 100 | the influence of habitat invasion by roads on space use and movements | ||
| 87 | of Cabrera voles (Microtus cabrerae), an Iberian endemism, classified | 101 | of Cabrera voles (Microtus cabrerae), an Iberian endemism, classified | ||
| 88 | as \u2018near threatened\u2019 and with small and fragmented | 102 | as \u2018near threatened\u2019 and with small and fragmented | ||
| 89 | populations. We hypothesise that: (1) individuals occupying areas more | 103 | populations. We hypothesise that: (1) individuals occupying areas more | ||
| 90 | densely encroached by roads have smaller home ranges and higher | 104 | densely encroached by roads have smaller home ranges and higher | ||
| 91 | intrasexual spatial overlap; (2) movement paths are i) shorter; ii) | 105 | intrasexual spatial overlap; (2) movement paths are i) shorter; ii) | ||
| 92 | more linear; and iii) more frequent along the road in areas with more | 106 | more linear; and iii) more frequent along the road in areas with more | ||
| 93 | encroachment; (3) movements are shorter during higher traffic periods | 107 | encroachment; (3) movements are shorter during higher traffic periods | ||
| 94 | of the day (daylight) in those areas. We radio-tracked 16 Cabrera | 108 | of the day (daylight) in those areas. We radio-tracked 16 Cabrera | ||
| 95 | voles (Wildlife Materials; SOM-2018) in two habitat patches along a | 109 | voles (Wildlife Materials; SOM-2018) in two habitat patches along a | ||
| 96 | National road in Southern Portugal (\u00c9vora district). The patches | 110 | National road in Southern Portugal (\u00c9vora district). The patches | ||
| 97 | are separated by 1.4 km, with one being highly encroached by roads | 111 | are separated by 1.4 km, with one being highly encroached by roads | ||
| 98 | (\u201cverge\u201d patch) and the other much less impacted by these | 112 | (\u201cverge\u201d patch) and the other much less impacted by these | ||
| 99 | structures (\u201cmeadow\u201d patch), with high habitat availability | 113 | structures (\u201cmeadow\u201d patch), with high habitat availability | ||
| 100 | despite the proximity of roads. Eight voles were radio-tracked in each | 114 | despite the proximity of roads. Eight voles were radio-tracked in each | ||
| 101 | patch (1 male and 7 females in \u201cMeadow\u201d; 5 males and 3 | 115 | patch (1 male and 7 females in \u201cMeadow\u201d; 5 males and 3 | ||
| 102 | females in \u201cVerge\u201d), between 7th April and 14th June 2017. | 116 | females in \u201cVerge\u201d), between 7th April and 14th June 2017. | ||
| 103 | Fixes were registered at 15 min-intervals in rounds of 4 hours which | 117 | Fixes were registered at 15 min-intervals in rounds of 4 hours which | ||
| 104 | covered the 24h cycle. We measured home range size (biased random | 118 | covered the 24h cycle. We measured home range size (biased random | ||
| 105 | bridge kernel) for all individuals, the percentage of home range | 119 | bridge kernel) for all individuals, the percentage of home range | ||
| 106 | overlap between females (UDOI index), path length, path linearity, and | 120 | overlap between females (UDOI index), path length, path linearity, and | ||
| 107 | path and step direction to assess space use and movement patterns in | 121 | path and step direction to assess space use and movement patterns in | ||
| 108 | the two habitat patches. According to our predictions, animals | 122 | the two habitat patches. According to our predictions, animals | ||
| 109 | occupying the \u201cverge\u201d patch showed significantly smaller | 123 | occupying the \u201cverge\u201d patch showed significantly smaller | ||
| 110 | home ranges when compared with animals sampled in the | 124 | home ranges when compared with animals sampled in the | ||
| 111 | \u201cmeadow\u201d patch, although female spatial overlap was not | 125 | \u201cmeadow\u201d patch, although female spatial overlap was not | ||
| 112 | statistically different between patches. Some of the remaining | 126 | statistically different between patches. Some of the remaining | ||
| 113 | predictions were not satisfied, as there were no significant | 127 | predictions were not satisfied, as there were no significant | ||
| 114 | differences in path length, path linearity or step direction between | 128 | differences in path length, path linearity or step direction between | ||
| 115 | patches. Nevertheless, there were differences in path length between | 129 | patches. Nevertheless, there were differences in path length between | ||
| 116 | day periods but only for the \u201cverge\u201d patch. The paths were | 130 | day periods but only for the \u201cverge\u201d patch. The paths were | ||
| 117 | shorter for the period 09-21h when compared with 05-09h in verge patch | 131 | shorter for the period 09-21h when compared with 05-09h in verge patch | ||
| 118 | (but not in meadow patch). No events of road crossing were detected in | 132 | (but not in meadow patch). No events of road crossing were detected in | ||
| 119 | any of the radio-tracked animals. Overall, these results provide | 133 | any of the radio-tracked animals. Overall, these results provide | ||
| 120 | empirical support for the idea that habitat invasion by roads may | 134 | empirical support for the idea that habitat invasion by roads may | ||
| 121 | significantly impact species behavioural traits related to space use | 135 | significantly impact species behavioural traits related to space use | ||
| 122 | and movement patterns.", | 136 | and movement patterns.", | ||
| 123 | "notes_translated": { | 137 | "notes_translated": { | ||
| 124 | "en": "Roads are a significant cause of habitat fragmentation and | 138 | "en": "Roads are a significant cause of habitat fragmentation and | ||
| 125 | a barrier to movement of several species across the world. Terrestrial | 139 | a barrier to movement of several species across the world. Terrestrial | ||
| 126 | species with low mobility, low abundance and specific habitat | 140 | species with low mobility, low abundance and specific habitat | ||
| 127 | requirements could be particularly affected by this kind of barriers | 141 | requirements could be particularly affected by this kind of barriers | ||
| 128 | concerning their movements. In the present study, we aimed to assess | 142 | concerning their movements. In the present study, we aimed to assess | ||
| 129 | the influence of habitat invasion by roads on space use and movements | 143 | the influence of habitat invasion by roads on space use and movements | ||
| 130 | of Cabrera voles (Microtus cabrerae), an Iberian endemism, classified | 144 | of Cabrera voles (Microtus cabrerae), an Iberian endemism, classified | ||
| 131 | as \u2018near threatened\u2019 and with small and fragmented | 145 | as \u2018near threatened\u2019 and with small and fragmented | ||
| 132 | populations. We hypothesise that: (1) individuals occupying areas more | 146 | populations. We hypothesise that: (1) individuals occupying areas more | ||
| 133 | densely encroached by roads have smaller home ranges and higher | 147 | densely encroached by roads have smaller home ranges and higher | ||
| 134 | intrasexual spatial overlap; (2) movement paths are i) shorter; ii) | 148 | intrasexual spatial overlap; (2) movement paths are i) shorter; ii) | ||
| 135 | more linear; and iii) more frequent along the road in areas with more | 149 | more linear; and iii) more frequent along the road in areas with more | ||
| 136 | encroachment; (3) movements are shorter during higher traffic periods | 150 | encroachment; (3) movements are shorter during higher traffic periods | ||
| 137 | of the day (daylight) in those areas. We radio-tracked 16 Cabrera | 151 | of the day (daylight) in those areas. We radio-tracked 16 Cabrera | ||
| 138 | voles (Wildlife Materials; SOM-2018) in two habitat patches along a | 152 | voles (Wildlife Materials; SOM-2018) in two habitat patches along a | ||
| 139 | National road in Southern Portugal (\u00c9vora district). The patches | 153 | National road in Southern Portugal (\u00c9vora district). The patches | ||
| 140 | are separated by 1.4 km, with one being highly encroached by roads | 154 | are separated by 1.4 km, with one being highly encroached by roads | ||
| 141 | (\u201cverge\u201d patch) and the other much less impacted by these | 155 | (\u201cverge\u201d patch) and the other much less impacted by these | ||
| 142 | structures (\u201cmeadow\u201d patch), with high habitat availability | 156 | structures (\u201cmeadow\u201d patch), with high habitat availability | ||
| 143 | despite the proximity of roads. Eight voles were radio-tracked in each | 157 | despite the proximity of roads. Eight voles were radio-tracked in each | ||
| 144 | patch (1 male and 7 females in \u201cMeadow\u201d; 5 males and 3 | 158 | patch (1 male and 7 females in \u201cMeadow\u201d; 5 males and 3 | ||
| 145 | females in \u201cVerge\u201d), between 7th April and 14th June 2017. | 159 | females in \u201cVerge\u201d), between 7th April and 14th June 2017. | ||
| 146 | Fixes were registered at 15 min-intervals in rounds of 4 hours which | 160 | Fixes were registered at 15 min-intervals in rounds of 4 hours which | ||
| 147 | covered the 24h cycle. We measured home range size (biased random | 161 | covered the 24h cycle. We measured home range size (biased random | ||
| 148 | bridge kernel) for all individuals, the percentage of home range | 162 | bridge kernel) for all individuals, the percentage of home range | ||
| 149 | overlap between females (UDOI index), path length, path linearity, and | 163 | overlap between females (UDOI index), path length, path linearity, and | ||
| 150 | path and step direction to assess space use and movement patterns in | 164 | path and step direction to assess space use and movement patterns in | ||
| 151 | the two habitat patches. According to our predictions, animals | 165 | the two habitat patches. According to our predictions, animals | ||
| 152 | occupying the \u201cverge\u201d patch showed significantly smaller | 166 | occupying the \u201cverge\u201d patch showed significantly smaller | ||
| 153 | home ranges when compared with animals sampled in the | 167 | home ranges when compared with animals sampled in the | ||
| 154 | \u201cmeadow\u201d patch, although female spatial overlap was not | 168 | \u201cmeadow\u201d patch, although female spatial overlap was not | ||
| 155 | statistically different between patches. Some of the remaining | 169 | statistically different between patches. Some of the remaining | ||
| 156 | predictions were not satisfied, as there were no significant | 170 | predictions were not satisfied, as there were no significant | ||
| 157 | differences in path length, path linearity or step direction between | 171 | differences in path length, path linearity or step direction between | ||
| 158 | patches. Nevertheless, there were differences in path length between | 172 | patches. Nevertheless, there were differences in path length between | ||
| 159 | day periods but only for the \u201cverge\u201d patch. The paths were | 173 | day periods but only for the \u201cverge\u201d patch. The paths were | ||
| 160 | shorter for the period 09-21h when compared with 05-09h in verge patch | 174 | shorter for the period 09-21h when compared with 05-09h in verge patch | ||
| 161 | (but not in meadow patch). No events of road crossing were detected in | 175 | (but not in meadow patch). No events of road crossing were detected in | ||
| 162 | any of the radio-tracked animals. Overall, these results provide | 176 | any of the radio-tracked animals. Overall, these results provide | ||
| 163 | empirical support for the idea that habitat invasion by roads may | 177 | empirical support for the idea that habitat invasion by roads may | ||
| 164 | significantly impact species behavioural traits related to space use | 178 | significantly impact species behavioural traits related to space use | ||
| 165 | and movement patterns.", | 179 | and movement patterns.", | ||
| 166 | "es": "Roads are a significant cause of habitat fragmentation and | 180 | "es": "Roads are a significant cause of habitat fragmentation and | ||
| 167 | a barrier to movement of several species across the world. Terrestrial | 181 | a barrier to movement of several species across the world. Terrestrial | ||
| 168 | species with low mobility, low abundance and specific habitat | 182 | species with low mobility, low abundance and specific habitat | ||
| 169 | requirements could be particularly affected by this kind of barriers | 183 | requirements could be particularly affected by this kind of barriers | ||
| 170 | concerning their movements. In the present study, we aimed to assess | 184 | concerning their movements. In the present study, we aimed to assess | ||
| 171 | the influence of habitat invasion by roads on space use and movements | 185 | the influence of habitat invasion by roads on space use and movements | ||
| 172 | of Cabrera voles (Microtus cabrerae), an Iberian endemism, classified | 186 | of Cabrera voles (Microtus cabrerae), an Iberian endemism, classified | ||
| 173 | as \u2018near threatened\u2019 and with small and fragmented | 187 | as \u2018near threatened\u2019 and with small and fragmented | ||
| 174 | populations. We hypothesise that: (1) individuals occupying areas more | 188 | populations. We hypothesise that: (1) individuals occupying areas more | ||
| 175 | densely encroached by roads have smaller home ranges and higher | 189 | densely encroached by roads have smaller home ranges and higher | ||
| 176 | intrasexual spatial overlap; (2) movement paths are i) shorter; ii) | 190 | intrasexual spatial overlap; (2) movement paths are i) shorter; ii) | ||
| 177 | more linear; and iii) more frequent along the road in areas with more | 191 | more linear; and iii) more frequent along the road in areas with more | ||
| 178 | encroachment; (3) movements are shorter during higher traffic periods | 192 | encroachment; (3) movements are shorter during higher traffic periods | ||
| 179 | of the day (daylight) in those areas. We radio-tracked 16 Cabrera | 193 | of the day (daylight) in those areas. We radio-tracked 16 Cabrera | ||
| 180 | voles (Wildlife Materials; SOM-2018) in two habitat patches along a | 194 | voles (Wildlife Materials; SOM-2018) in two habitat patches along a | ||
| 181 | National road in Southern Portugal (\u00c9vora district). The patches | 195 | National road in Southern Portugal (\u00c9vora district). The patches | ||
| 182 | are separated by 1.4 km, with one being highly encroached by roads | 196 | are separated by 1.4 km, with one being highly encroached by roads | ||
| 183 | (\u201cverge\u201d patch) and the other much less impacted by these | 197 | (\u201cverge\u201d patch) and the other much less impacted by these | ||
| 184 | structures (\u201cmeadow\u201d patch), with high habitat availability | 198 | structures (\u201cmeadow\u201d patch), with high habitat availability | ||
| 185 | despite the proximity of roads. Eight voles were radio-tracked in each | 199 | despite the proximity of roads. Eight voles were radio-tracked in each | ||
| 186 | patch (1 male and 7 females in \u201cMeadow\u201d; 5 males and 3 | 200 | patch (1 male and 7 females in \u201cMeadow\u201d; 5 males and 3 | ||
| 187 | females in \u201cVerge\u201d), between 7th April and 14th June 2017. | 201 | females in \u201cVerge\u201d), between 7th April and 14th June 2017. | ||
| 188 | Fixes were registered at 15 min-intervals in rounds of 4 hours which | 202 | Fixes were registered at 15 min-intervals in rounds of 4 hours which | ||
| 189 | covered the 24h cycle. We measured home range size (biased random | 203 | covered the 24h cycle. We measured home range size (biased random | ||
| 190 | bridge kernel) for all individuals, the percentage of home range | 204 | bridge kernel) for all individuals, the percentage of home range | ||
| 191 | overlap between females (UDOI index), path length, path linearity, and | 205 | overlap between females (UDOI index), path length, path linearity, and | ||
| 192 | path and step direction to assess space use and movement patterns in | 206 | path and step direction to assess space use and movement patterns in | ||
| 193 | the two habitat patches. According to our predictions, animals | 207 | the two habitat patches. According to our predictions, animals | ||
| 194 | occupying the \u201cverge\u201d patch showed significantly smaller | 208 | occupying the \u201cverge\u201d patch showed significantly smaller | ||
| 195 | home ranges when compared with animals sampled in the | 209 | home ranges when compared with animals sampled in the | ||
| 196 | \u201cmeadow\u201d patch, although female spatial overlap was not | 210 | \u201cmeadow\u201d patch, although female spatial overlap was not | ||
| 197 | statistically different between patches. Some of the remaining | 211 | statistically different between patches. Some of the remaining | ||
| 198 | predictions were not satisfied, as there were no significant | 212 | predictions were not satisfied, as there were no significant | ||
| 199 | differences in path length, path linearity or step direction between | 213 | differences in path length, path linearity or step direction between | ||
| 200 | patches. Nevertheless, there were differences in path length between | 214 | patches. Nevertheless, there were differences in path length between | ||
| 201 | day periods but only for the \u201cverge\u201d patch. The paths were | 215 | day periods but only for the \u201cverge\u201d patch. The paths were | ||
| 202 | shorter for the period 09-21h when compared with 05-09h in verge patch | 216 | shorter for the period 09-21h when compared with 05-09h in verge patch | ||
| 203 | (but not in meadow patch). No events of road crossing were detected in | 217 | (but not in meadow patch). No events of road crossing were detected in | ||
| 204 | any of the radio-tracked animals. Overall, these results provide | 218 | any of the radio-tracked animals. Overall, these results provide | ||
| 205 | empirical support for the idea that habitat invasion by roads may | 219 | empirical support for the idea that habitat invasion by roads may | ||
| 206 | significantly impact species behavioural traits related to space use | 220 | significantly impact species behavioural traits related to space use | ||
| 207 | and movement patterns." | 221 | and movement patterns." | ||
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