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En el instante 23 de junio de 2026, 16:03:01 UTC,
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Modificado el valor del campo
spatial_coverage
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en Vegetation structure and prey abundance requirements of the iberian lynx: implications for the design of reserves and corridors.
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| 57 | "Journal of Applied Ecology. Vol. 38", | 57 | "Journal of Applied Ecology. Vol. 38", | ||
| 58 | "Num. 1", | 58 | "Num. 1", | ||
| 59 | "pags. 9-18" | 59 | "pags. 9-18" | ||
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| 79 | "notes": "1. Habitat alteration and fragmentation are two of the | 79 | "notes": "1. Habitat alteration and fragmentation are two of the | ||
| 80 | greatest threats to biodiversity. The conservation of most species in | 80 | greatest threats to biodiversity. The conservation of most species in | ||
| 81 | highly encroached areas requires reserves that are connected by | 81 | highly encroached areas requires reserves that are connected by | ||
| 82 | suitable habitat corridors to increase the effectiveness of the area | 82 | suitable habitat corridors to increase the effectiveness of the area | ||
| 83 | under protection. However, the quality required for such corridors is | 83 | under protection. However, the quality required for such corridors is | ||
| 84 | still debated. This study investigated the habitat characteristic | 84 | still debated. This study investigated the habitat characteristic | ||
| 85 | (vegetation structure and prey abundance) of sites used by resident | 85 | (vegetation structure and prey abundance) of sites used by resident | ||
| 86 | and dispersing Iberian lynx in south-western Spain. 2. Vegetation | 86 | and dispersing Iberian lynx in south-western Spain. 2. Vegetation | ||
| 87 | structure and an index of rabbit abundance (the staple prey of lynx) | 87 | structure and an index of rabbit abundance (the staple prey of lynx) | ||
| 88 | were measured at sites used by radio-collared lynx in 1996 and 1997. | 88 | were measured at sites used by radio-collared lynx in 1996 and 1997. | ||
| 89 | Data from 128 plots used by resident lynx and 310 plots used by | 89 | Data from 128 plots used by resident lynx and 310 plots used by | ||
| 90 | dispersing individuals were compared with data from 162 randomly | 90 | dispersing individuals were compared with data from 162 randomly | ||
| 91 | located plots in sites considered to be unused by lynx. 3. Resident | 91 | located plots in sites considered to be unused by lynx. 3. Resident | ||
| 92 | sites had a lower percentage of tree cover, shorter tree height, | 92 | sites had a lower percentage of tree cover, shorter tree height, | ||
| 93 | higher percentage of tall shrub cover, higher percentage of overall | 93 | higher percentage of tall shrub cover, higher percentage of overall | ||
| 94 | understorey and higher number of rabbit pellets than both dispersal | 94 | understorey and higher number of rabbit pellets than both dispersal | ||
| 95 | and unused sites. The height of the short shrub layer was taller and | 95 | and unused sites. The height of the short shrub layer was taller and | ||
| 96 | the rabbit abundance index was higher in dispersing sites than in | 96 | the rabbit abundance index was higher in dispersing sites than in | ||
| 97 | unused sites. 4. Gender did not affect habitat selection by lynx. | 97 | unused sites. 4. Gender did not affect habitat selection by lynx. | ||
| 98 | During dispersal, lynx frequently (50% of cases) used vegetation | 98 | During dispersal, lynx frequently (50% of cases) used vegetation | ||
| 99 | patches narrower than 300 m. In these cases, sites used by lynx had | 99 | patches narrower than 300 m. In these cases, sites used by lynx had | ||
| 100 | higher understorey cover and taller shrub height than adjacent unused | 100 | higher understorey cover and taller shrub height than adjacent unused | ||
| 101 | sites. The percentage of short shrub cover used by lynx increased with | 101 | sites. The percentage of short shrub cover used by lynx increased with | ||
| 102 | the length of time taken to disperse; this was the only variable that | 102 | the length of time taken to disperse; this was the only variable that | ||
| 103 | changed over time. 5. Range size of resident individuals declined | 103 | changed over time. 5. Range size of resident individuals declined | ||
| 104 | significantly with the index of rabbit abundance but increased with | 104 | significantly with the index of rabbit abundance but increased with | ||
| 105 | the percentage of short shrub cover. Both variables were good | 105 | the percentage of short shrub cover. Both variables were good | ||
| 106 | predictors of range size. 6. The study shows that corridors connecting | 106 | predictors of range size. 6. The study shows that corridors connecting | ||
| 107 | reserves do not have to be prime habitats; they can even support | 107 | reserves do not have to be prime habitats; they can even support | ||
| 108 | moderate habitat degradation due to human activity. This result has | 108 | moderate habitat degradation due to human activity. This result has | ||
| 109 | implications both for the conservation of existing corridors, and for | 109 | implications both for the conservation of existing corridors, and for | ||
| 110 | the restoration of the many corridors between reserves that have been | 110 | the restoration of the many corridors between reserves that have been | ||
| 111 | lost.\n Palabras clave: Connectivity, Corridor, Dispersal, Habitat, | 111 | lost.\n Palabras clave: Connectivity, Corridor, Dispersal, Habitat, | ||
| 112 | Habitat fragmentation, Lynx", | 112 | Habitat fragmentation, Lynx", | ||
| 113 | "notes_translated": { | 113 | "notes_translated": { | ||
| 114 | "en": "1. Habitat alteration and fragmentation are two of the | 114 | "en": "1. Habitat alteration and fragmentation are two of the | ||
| 115 | greatest threats to biodiversity. The conservation of most species in | 115 | greatest threats to biodiversity. The conservation of most species in | ||
| 116 | highly encroached areas requires reserves that are connected by | 116 | highly encroached areas requires reserves that are connected by | ||
| 117 | suitable habitat corridors to increase the effectiveness of the area | 117 | suitable habitat corridors to increase the effectiveness of the area | ||
| 118 | under protection. However, the quality required for such corridors is | 118 | under protection. However, the quality required for such corridors is | ||
| 119 | still debated. This study investigated the habitat characteristic | 119 | still debated. This study investigated the habitat characteristic | ||
| 120 | (vegetation structure and prey abundance) of sites used by resident | 120 | (vegetation structure and prey abundance) of sites used by resident | ||
| 121 | and dispersing Iberian lynx in south-western Spain. 2. Vegetation | 121 | and dispersing Iberian lynx in south-western Spain. 2. Vegetation | ||
| 122 | structure and an index of rabbit abundance (the staple prey of lynx) | 122 | structure and an index of rabbit abundance (the staple prey of lynx) | ||
| 123 | were measured at sites used by radio-collared lynx in 1996 and 1997. | 123 | were measured at sites used by radio-collared lynx in 1996 and 1997. | ||
| 124 | Data from 128 plots used by resident lynx and 310 plots used by | 124 | Data from 128 plots used by resident lynx and 310 plots used by | ||
| 125 | dispersing individuals were compared with data from 162 randomly | 125 | dispersing individuals were compared with data from 162 randomly | ||
| 126 | located plots in sites considered to be unused by lynx. 3. Resident | 126 | located plots in sites considered to be unused by lynx. 3. Resident | ||
| 127 | sites had a lower percentage of tree cover, shorter tree height, | 127 | sites had a lower percentage of tree cover, shorter tree height, | ||
| 128 | higher percentage of tall shrub cover, higher percentage of overall | 128 | higher percentage of tall shrub cover, higher percentage of overall | ||
| 129 | understorey and higher number of rabbit pellets than both dispersal | 129 | understorey and higher number of rabbit pellets than both dispersal | ||
| 130 | and unused sites. The height of the short shrub layer was taller and | 130 | and unused sites. The height of the short shrub layer was taller and | ||
| 131 | the rabbit abundance index was higher in dispersing sites than in | 131 | the rabbit abundance index was higher in dispersing sites than in | ||
| 132 | unused sites. 4. Gender did not affect habitat selection by lynx. | 132 | unused sites. 4. Gender did not affect habitat selection by lynx. | ||
| 133 | During dispersal, lynx frequently (50% of cases) used vegetation | 133 | During dispersal, lynx frequently (50% of cases) used vegetation | ||
| 134 | patches narrower than 300 m. In these cases, sites used by lynx had | 134 | patches narrower than 300 m. In these cases, sites used by lynx had | ||
| 135 | higher understorey cover and taller shrub height than adjacent unused | 135 | higher understorey cover and taller shrub height than adjacent unused | ||
| 136 | sites. The percentage of short shrub cover used by lynx increased with | 136 | sites. The percentage of short shrub cover used by lynx increased with | ||
| 137 | the length of time taken to disperse; this was the only variable that | 137 | the length of time taken to disperse; this was the only variable that | ||
| 138 | changed over time. 5. Range size of resident individuals declined | 138 | changed over time. 5. Range size of resident individuals declined | ||
| 139 | significantly with the index of rabbit abundance but increased with | 139 | significantly with the index of rabbit abundance but increased with | ||
| 140 | the percentage of short shrub cover. Both variables were good | 140 | the percentage of short shrub cover. Both variables were good | ||
| 141 | predictors of range size. 6. The study shows that corridors connecting | 141 | predictors of range size. 6. The study shows that corridors connecting | ||
| 142 | reserves do not have to be prime habitats; they can even support | 142 | reserves do not have to be prime habitats; they can even support | ||
| 143 | moderate habitat degradation due to human activity. This result has | 143 | moderate habitat degradation due to human activity. This result has | ||
| 144 | implications both for the conservation of existing corridors, and for | 144 | implications both for the conservation of existing corridors, and for | ||
| 145 | the restoration of the many corridors between reserves that have been | 145 | the restoration of the many corridors between reserves that have been | ||
| 146 | lost.", | 146 | lost.", | ||
| 147 | "es": "1. Habitat alteration and fragmentation are two of the | 147 | "es": "1. Habitat alteration and fragmentation are two of the | ||
| 148 | greatest threats to biodiversity. The conservation of most species in | 148 | greatest threats to biodiversity. The conservation of most species in | ||
| 149 | highly encroached areas requires reserves that are connected by | 149 | highly encroached areas requires reserves that are connected by | ||
| 150 | suitable habitat corridors to increase the effectiveness of the area | 150 | suitable habitat corridors to increase the effectiveness of the area | ||
| 151 | under protection. However, the quality required for such corridors is | 151 | under protection. However, the quality required for such corridors is | ||
| 152 | still debated. This study investigated the habitat characteristic | 152 | still debated. This study investigated the habitat characteristic | ||
| 153 | (vegetation structure and prey abundance) of sites used by resident | 153 | (vegetation structure and prey abundance) of sites used by resident | ||
| 154 | and dispersing Iberian lynx in south-western Spain. 2. Vegetation | 154 | and dispersing Iberian lynx in south-western Spain. 2. Vegetation | ||
| 155 | structure and an index of rabbit abundance (the staple prey of lynx) | 155 | structure and an index of rabbit abundance (the staple prey of lynx) | ||
| 156 | were measured at sites used by radio-collared lynx in 1996 and 1997. | 156 | were measured at sites used by radio-collared lynx in 1996 and 1997. | ||
| 157 | Data from 128 plots used by resident lynx and 310 plots used by | 157 | Data from 128 plots used by resident lynx and 310 plots used by | ||
| 158 | dispersing individuals were compared with data from 162 randomly | 158 | dispersing individuals were compared with data from 162 randomly | ||
| 159 | located plots in sites considered to be unused by lynx. 3. Resident | 159 | located plots in sites considered to be unused by lynx. 3. Resident | ||
| 160 | sites had a lower percentage of tree cover, shorter tree height, | 160 | sites had a lower percentage of tree cover, shorter tree height, | ||
| 161 | higher percentage of tall shrub cover, higher percentage of overall | 161 | higher percentage of tall shrub cover, higher percentage of overall | ||
| 162 | understorey and higher number of rabbit pellets than both dispersal | 162 | understorey and higher number of rabbit pellets than both dispersal | ||
| 163 | and unused sites. The height of the short shrub layer was taller and | 163 | and unused sites. The height of the short shrub layer was taller and | ||
| 164 | the rabbit abundance index was higher in dispersing sites than in | 164 | the rabbit abundance index was higher in dispersing sites than in | ||
| 165 | unused sites. 4. Gender did not affect habitat selection by lynx. | 165 | unused sites. 4. Gender did not affect habitat selection by lynx. | ||
| 166 | During dispersal, lynx frequently (50% of cases) used vegetation | 166 | During dispersal, lynx frequently (50% of cases) used vegetation | ||
| 167 | patches narrower than 300 m. In these cases, sites used by lynx had | 167 | patches narrower than 300 m. In these cases, sites used by lynx had | ||
| 168 | higher understorey cover and taller shrub height than adjacent unused | 168 | higher understorey cover and taller shrub height than adjacent unused | ||
| 169 | sites. The percentage of short shrub cover used by lynx increased with | 169 | sites. The percentage of short shrub cover used by lynx increased with | ||
| 170 | the length of time taken to disperse; this was the only variable that | 170 | the length of time taken to disperse; this was the only variable that | ||
| 171 | changed over time. 5. Range size of resident individuals declined | 171 | changed over time. 5. Range size of resident individuals declined | ||
| 172 | significantly with the index of rabbit abundance but increased with | 172 | significantly with the index of rabbit abundance but increased with | ||
| 173 | the percentage of short shrub cover. Both variables were good | 173 | the percentage of short shrub cover. Both variables were good | ||
| 174 | predictors of range size. 6. The study shows that corridors connecting | 174 | predictors of range size. 6. The study shows that corridors connecting | ||
| 175 | reserves do not have to be prime habitats; they can even support | 175 | reserves do not have to be prime habitats; they can even support | ||
| 176 | moderate habitat degradation due to human activity. This result has | 176 | moderate habitat degradation due to human activity. This result has | ||
| 177 | implications both for the conservation of existing corridors, and for | 177 | implications both for the conservation of existing corridors, and for | ||
| 178 | the restoration of the many corridors between reserves that have been | 178 | the restoration of the many corridors between reserves that have been | ||
| 179 | lost.\n Palabras clave: Connectivity, Corridor, Dispersal, Habitat, | 179 | lost.\n Palabras clave: Connectivity, Corridor, Dispersal, Habitat, | ||
| 180 | Habitat fragmentation, Lynx" | 180 | Habitat fragmentation, Lynx" | ||
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