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en Habitat quality predicts the distribution of a lizard in fragmented woodlands better than habitat fragmentation. -
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) en Habitat quality predicts the distribution of a lizard in fragmented woodlands better than habitat fragmentation.
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| 81 | "name": "df606bdf-af74-51ce-a057-bc8a3edf88f8", | 95 | "name": "df606bdf-af74-51ce-a057-bc8a3edf88f8", | ||
| 82 | "notes": "Organisms often face a higher risk of local extinction in | 96 | "notes": "Organisms often face a higher risk of local extinction in | ||
| 83 | fragmented than in continuous habitat. However, whether populations | 97 | fragmented than in continuous habitat. However, whether populations | ||
| 84 | are affected by reduced size and connectivity of the habitat or by | 98 | are affected by reduced size and connectivity of the habitat or by | ||
| 85 | changes in habitat quality in fragmented landscapes remains poorly | 99 | changes in habitat quality in fragmented landscapes remains poorly | ||
| 86 | investigated. We studied the regional distribution and microhabitat | 100 | investigated. We studied the regional distribution and microhabitat | ||
| 87 | selection of the lacertid lizard Psammodromus algirus in a fragmented | 101 | selection of the lacertid lizard Psammodromus algirus in a fragmented | ||
| 88 | landscape where the existence of deciduous and evergreen woodlands | 102 | landscape where the existence of deciduous and evergreen woodlands | ||
| 89 | brought about variation in habitat quality. Lizards never occupied any | 103 | brought about variation in habitat quality. Lizards never occupied any | ||
| 90 | fragment smaller than 0.5 ha. However, above that limit fragment size | 104 | fragment smaller than 0.5 ha. However, above that limit fragment size | ||
| 91 | no longer predicted lizard occurrence, which was explained by woodland | 105 | no longer predicted lizard occurrence, which was explained by woodland | ||
| 92 | type instead, with lizards being more frequently found in deciduous | 106 | type instead, with lizards being more frequently found in deciduous | ||
| 93 | than in evergreen woodlands. Lizards selected microhabitats that had | 107 | than in evergreen woodlands. Lizards selected microhabitats that had | ||
| 94 | structural features favouring thermoregulation, foraging and predator | 108 | structural features favouring thermoregulation, foraging and predator | ||
| 95 | avoidance, and we identified better conditions for thermoregulation | 109 | avoidance, and we identified better conditions for thermoregulation | ||
| 96 | and food acquisition in deciduous than in evergreen woodlands. Our | 110 | and food acquisition in deciduous than in evergreen woodlands. Our | ||
| 97 | results support the idea that variation in habitat quality can | 111 | results support the idea that variation in habitat quality can | ||
| 98 | sometimes override the effect of habitat fragmentation on animal | 112 | sometimes override the effect of habitat fragmentation on animal | ||
| 99 | populations. We consider the implications of our study for the | 113 | populations. We consider the implications of our study for the | ||
| 100 | conservation of Mediterranean lizards, discussing our results in a | 114 | conservation of Mediterranean lizards, discussing our results in a | ||
| 101 | broader context framed by previous studies conducted in nearby | 115 | broader context framed by previous studies conducted in nearby | ||
| 102 | areas.", | 116 | areas.", | ||
| 103 | "notes_translated": { | 117 | "notes_translated": { | ||
| 104 | "en": "Organisms often face a higher risk of local extinction in | 118 | "en": "Organisms often face a higher risk of local extinction in | ||
| 105 | fragmented than in continuous habitat. However, whether populations | 119 | fragmented than in continuous habitat. However, whether populations | ||
| 106 | are affected by reduced size and connectivity of the habitat or by | 120 | are affected by reduced size and connectivity of the habitat or by | ||
| 107 | changes in habitat quality in fragmented landscapes remains poorly | 121 | changes in habitat quality in fragmented landscapes remains poorly | ||
| 108 | investigated. We studied the regional distribution and microhabitat | 122 | investigated. We studied the regional distribution and microhabitat | ||
| 109 | selection of the lacertid lizard\u00a0Psammodromus algirus\u00a0in a | 123 | selection of the lacertid lizard\u00a0Psammodromus algirus\u00a0in a | ||
| 110 | fragmented landscape where the existence of deciduous and evergreen | 124 | fragmented landscape where the existence of deciduous and evergreen | ||
| 111 | woodlands brought about variation in habitat quality. Lizards never | 125 | woodlands brought about variation in habitat quality. Lizards never | ||
| 112 | occupied any fragment smaller than 0.5\u2003ha. However, above that | 126 | occupied any fragment smaller than 0.5\u2003ha. However, above that | ||
| 113 | limit fragment size no longer predicted lizard occurrence, which was | 127 | limit fragment size no longer predicted lizard occurrence, which was | ||
| 114 | explained by woodland type instead, with lizards being more frequently | 128 | explained by woodland type instead, with lizards being more frequently | ||
| 115 | found in deciduous than in evergreen woodlands. Lizards selected | 129 | found in deciduous than in evergreen woodlands. Lizards selected | ||
| 116 | microhabitats that had structural features favouring thermoregulation, | 130 | microhabitats that had structural features favouring thermoregulation, | ||
| 117 | foraging and predator avoidance, and we identified better conditions | 131 | foraging and predator avoidance, and we identified better conditions | ||
| 118 | for thermoregulation and food acquisition in deciduous than in | 132 | for thermoregulation and food acquisition in deciduous than in | ||
| 119 | evergreen woodlands. Our results support the idea that variation in | 133 | evergreen woodlands. Our results support the idea that variation in | ||
| 120 | habitat quality can sometimes override the effect of habitat | 134 | habitat quality can sometimes override the effect of habitat | ||
| 121 | fragmentation on animal populations. We consider the implications of | 135 | fragmentation on animal populations. We consider the implications of | ||
| 122 | our study for the conservation of Mediterranean lizards, discussing | 136 | our study for the conservation of Mediterranean lizards, discussing | ||
| 123 | our results in a broader context framed by previous studies conducted | 137 | our results in a broader context framed by previous studies conducted | ||
| 124 | in nearby areas.", | 138 | in nearby areas.", | ||
| 125 | "es": "Organisms often face a higher risk of local extinction in | 139 | "es": "Organisms often face a higher risk of local extinction in | ||
| 126 | fragmented than in continuous habitat. However, whether populations | 140 | fragmented than in continuous habitat. However, whether populations | ||
| 127 | are affected by reduced size and connectivity of the habitat or by | 141 | are affected by reduced size and connectivity of the habitat or by | ||
| 128 | changes in habitat quality in fragmented landscapes remains poorly | 142 | changes in habitat quality in fragmented landscapes remains poorly | ||
| 129 | investigated. We studied the regional distribution and microhabitat | 143 | investigated. We studied the regional distribution and microhabitat | ||
| 130 | selection of the lacertid lizard Psammodromus algirus in a fragmented | 144 | selection of the lacertid lizard Psammodromus algirus in a fragmented | ||
| 131 | landscape where the existence of deciduous and evergreen woodlands | 145 | landscape where the existence of deciduous and evergreen woodlands | ||
| 132 | brought about variation in habitat quality. Lizards never occupied any | 146 | brought about variation in habitat quality. Lizards never occupied any | ||
| 133 | fragment smaller than 0.5 ha. However, above that limit fragment size | 147 | fragment smaller than 0.5 ha. However, above that limit fragment size | ||
| 134 | no longer predicted lizard occurrence, which was explained by woodland | 148 | no longer predicted lizard occurrence, which was explained by woodland | ||
| 135 | type instead, with lizards being more frequently found in deciduous | 149 | type instead, with lizards being more frequently found in deciduous | ||
| 136 | than in evergreen woodlands. Lizards selected microhabitats that had | 150 | than in evergreen woodlands. Lizards selected microhabitats that had | ||
| 137 | structural features favouring thermoregulation, foraging and predator | 151 | structural features favouring thermoregulation, foraging and predator | ||
| 138 | avoidance, and we identified better conditions for thermoregulation | 152 | avoidance, and we identified better conditions for thermoregulation | ||
| 139 | and food acquisition in deciduous than in evergreen woodlands. Our | 153 | and food acquisition in deciduous than in evergreen woodlands. Our | ||
| 140 | results support the idea that variation in habitat quality can | 154 | results support the idea that variation in habitat quality can | ||
| 141 | sometimes override the effect of habitat fragmentation on animal | 155 | sometimes override the effect of habitat fragmentation on animal | ||
| 142 | populations. We consider the implications of our study for the | 156 | populations. We consider the implications of our study for the | ||
| 143 | conservation of Mediterranean lizards, discussing our results in a | 157 | conservation of Mediterranean lizards, discussing our results in a | ||
| 144 | broader context framed by previous studies conducted in nearby areas." | 158 | broader context framed by previous studies conducted in nearby areas." | ||
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| 289 | "title": "Habitat quality predicts the distribution of a lizard in | 303 | "title": "Habitat quality predicts the distribution of a lizard in | ||
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