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En el instante 25 de junio de 2026, 12:33:22 UTC,
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a2026-06-25
en Multispecies landscape functional connectivity enhances local bird species’ diversity in a highly fragmented landscape. -
Modificado el valor del campo
modified
del recurso Acceso al recurso a2026-06-25
(anteriormente2026-06-23
) en Multispecies landscape functional connectivity enhances local bird species’ diversity in a highly fragmented landscape.
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| 80 | "name": "93b1c5b0-9631-5f52-9d9e-5186446429ff", | 94 | "name": "93b1c5b0-9631-5f52-9d9e-5186446429ff", | ||
| 81 | "notes": "Local species assemblages are likely the result of habitat | 95 | "notes": "Local species assemblages are likely the result of habitat | ||
| 82 | and landscape filtering. However, there is still limited knowledge on | 96 | and landscape filtering. However, there is still limited knowledge on | ||
| 83 | how landscape functional connectivity complements habitat attributes | 97 | how landscape functional connectivity complements habitat attributes | ||
| 84 | in mediating local species assemblages in real-world fragmented | 98 | in mediating local species assemblages in real-world fragmented | ||
| 85 | landscapes. In this study, we set up a non-manipulative experimental | 99 | landscapes. In this study, we set up a non-manipulative experimental | ||
| 86 | design in a standard production forest to demonstrate how functional | 100 | design in a standard production forest to demonstrate how functional | ||
| 87 | connectivity determines the spatial distribution of a bird community. | 101 | connectivity determines the spatial distribution of a bird community. | ||
| 88 | We test single- and multispecies spatially explicit, landscape | 102 | We test single- and multispecies spatially explicit, landscape | ||
| 89 | functional connectivity models framed within the circuit theory, | 103 | functional connectivity models framed within the circuit theory, | ||
| 90 | considering also patch attributes describing habitat size and quality, | 104 | considering also patch attributes describing habitat size and quality, | ||
| 91 | to weight their effects on species occurrence and community | 105 | to weight their effects on species occurrence and community | ||
| 92 | assemblage. We found that single-species functional connectivity | 106 | assemblage. We found that single-species functional connectivity | ||
| 93 | effects contributed positively for occurrence of each species. | 107 | effects contributed positively for occurrence of each species. | ||
| 94 | However, they rarely provided competing alternatives in predicting | 108 | However, they rarely provided competing alternatives in predicting | ||
| 95 | community parameters when compared to multispecies connectivity | 109 | community parameters when compared to multispecies connectivity | ||
| 96 | models. Incorporating multispecies connectivity showed more consistent | 110 | models. Incorporating multispecies connectivity showed more consistent | ||
| 97 | effects for all community parameters, than single-species models, | 111 | effects for all community parameters, than single-species models, | ||
| 98 | since the overlap between species\u2019 dispersal abilities in the | 112 | since the overlap between species\u2019 dispersal abilities in the | ||
| 99 | landscape shows poor agreement. Habitat size and quality, though less | 113 | landscape shows poor agreement. Habitat size and quality, though less | ||
| 100 | important, were also determinant in explaining community parameters | 114 | important, were also determinant in explaining community parameters | ||
| 101 | while possibly relating to the provision of suitable nesting and | 115 | while possibly relating to the provision of suitable nesting and | ||
| 102 | foraging conditions. Both habitat and landscape filters concur to | 116 | foraging conditions. Both habitat and landscape filters concur to | ||
| 103 | govern community assembly, though likely influencing different | 117 | govern community assembly, though likely influencing different | ||
| 104 | processes: while landscape connectivity determines which species can | 118 | processes: while landscape connectivity determines which species can | ||
| 105 | reach a patch, habitat quality determines which species settle in the | 119 | reach a patch, habitat quality determines which species settle in the | ||
| 106 | patch. Our results also suggest that surrogating multispecies | 120 | patch. Our results also suggest that surrogating multispecies | ||
| 107 | connectivity from single species has potential to source bias by | 121 | connectivity from single species has potential to source bias by | ||
| 108 | assuming species perceive landscape and its barriers similarly. | 122 | assuming species perceive landscape and its barriers similarly. | ||
| 109 | Inference on this issue must be gathered from as much species as | 123 | Inference on this issue must be gathered from as much species as | ||
| 110 | possible.", | 124 | possible.", | ||
| 111 | "notes_translated": { | 125 | "notes_translated": { | ||
| 112 | "en": "Local species assemblages are likely the result of habitat | 126 | "en": "Local species assemblages are likely the result of habitat | ||
| 113 | and landscape filtering. However, there is still limited knowledge on | 127 | and landscape filtering. However, there is still limited knowledge on | ||
| 114 | how landscape functional connectivity complements habitat attributes | 128 | how landscape functional connectivity complements habitat attributes | ||
| 115 | in mediating local species assemblages in real-world fragmented | 129 | in mediating local species assemblages in real-world fragmented | ||
| 116 | landscapes. In this study, we set up a | 130 | landscapes. In this study, we set up a | ||
| 117 | non-manipulative\u00a0experimental design\u00a0in a standard | 131 | non-manipulative\u00a0experimental design\u00a0in a standard | ||
| 118 | production forest to demonstrate how functional connectivity | 132 | production forest to demonstrate how functional connectivity | ||
| 119 | determines the spatial distribution of a bird\u00a0community. We test | 133 | determines the spatial distribution of a bird\u00a0community. We test | ||
| 120 | single- and multispecies spatially explicit, landscape functional | 134 | single- and multispecies spatially explicit, landscape functional | ||
| 121 | connectivity models framed within the circuit theory, considering also | 135 | connectivity models framed within the circuit theory, considering also | ||
| 122 | patch attributes describing habitat size and quality, to weight their | 136 | patch attributes describing habitat size and quality, to weight their | ||
| 123 | effects on species occurrence and\u00a0community\u00a0assemblage. We | 137 | effects on species occurrence and\u00a0community\u00a0assemblage. We | ||
| 124 | found that single-species functional connectivity effects contributed | 138 | found that single-species functional connectivity effects contributed | ||
| 125 | positively for occurrence of each species. However, they rarely | 139 | positively for occurrence of each species. However, they rarely | ||
| 126 | provided competing alternatives in predicting community parameters | 140 | provided competing alternatives in predicting community parameters | ||
| 127 | when compared to multispecies connectivity models. Incorporating | 141 | when compared to multispecies connectivity models. Incorporating | ||
| 128 | multispecies connectivity showed more consistent effects for all | 142 | multispecies connectivity showed more consistent effects for all | ||
| 129 | community parameters, than single-species models, since the overlap | 143 | community parameters, than single-species models, since the overlap | ||
| 130 | between species\u2019 dispersal abilities in the landscape shows poor | 144 | between species\u2019 dispersal abilities in the landscape shows poor | ||
| 131 | agreement. Habitat size and quality, though less important, were also | 145 | agreement. Habitat size and quality, though less important, were also | ||
| 132 | determinant in explaining community parameters while possibly relating | 146 | determinant in explaining community parameters while possibly relating | ||
| 133 | to the provision of suitable nesting and foraging conditions. Both | 147 | to the provision of suitable nesting and foraging conditions. Both | ||
| 134 | habitat and landscape filters concur to govern community assembly, | 148 | habitat and landscape filters concur to govern community assembly, | ||
| 135 | though likely influencing different processes: while landscape | 149 | though likely influencing different processes: while landscape | ||
| 136 | connectivity determines which species can reach a patch, habitat | 150 | connectivity determines which species can reach a patch, habitat | ||
| 137 | quality determines which species settle in the patch. Our results also | 151 | quality determines which species settle in the patch. Our results also | ||
| 138 | suggest that surrogating multispecies connectivity from single species | 152 | suggest that surrogating multispecies connectivity from single species | ||
| 139 | has potential to source bias by assuming species perceive landscape | 153 | has potential to source bias by assuming species perceive landscape | ||
| 140 | and its barriers similarly. Inference on this issue must be gathered | 154 | and its barriers similarly. Inference on this issue must be gathered | ||
| 141 | from as much species as possible.", | 155 | from as much species as possible.", | ||
| 142 | "es": "Local species assemblages are likely the result of habitat | 156 | "es": "Local species assemblages are likely the result of habitat | ||
| 143 | and landscape filtering. However, there is still limited knowledge on | 157 | and landscape filtering. However, there is still limited knowledge on | ||
| 144 | how landscape functional connectivity complements habitat attributes | 158 | how landscape functional connectivity complements habitat attributes | ||
| 145 | in mediating local species assemblages in real-world fragmented | 159 | in mediating local species assemblages in real-world fragmented | ||
| 146 | landscapes. In this study, we set up a non-manipulative experimental | 160 | landscapes. In this study, we set up a non-manipulative experimental | ||
| 147 | design in a standard production forest to demonstrate how functional | 161 | design in a standard production forest to demonstrate how functional | ||
| 148 | connectivity determines the spatial distribution of a bird community. | 162 | connectivity determines the spatial distribution of a bird community. | ||
| 149 | We test single- and multispecies spatially explicit, landscape | 163 | We test single- and multispecies spatially explicit, landscape | ||
| 150 | functional connectivity models framed within the circuit theory, | 164 | functional connectivity models framed within the circuit theory, | ||
| 151 | considering also patch attributes describing habitat size and quality, | 165 | considering also patch attributes describing habitat size and quality, | ||
| 152 | to weight their effects on species occurrence and community | 166 | to weight their effects on species occurrence and community | ||
| 153 | assemblage. We found that single-species functional connectivity | 167 | assemblage. We found that single-species functional connectivity | ||
| 154 | effects contributed positively for occurrence of each species. | 168 | effects contributed positively for occurrence of each species. | ||
| 155 | However, they rarely provided competing alternatives in predicting | 169 | However, they rarely provided competing alternatives in predicting | ||
| 156 | community parameters when compared to multispecies connectivity | 170 | community parameters when compared to multispecies connectivity | ||
| 157 | models. Incorporating multispecies connectivity showed more consistent | 171 | models. Incorporating multispecies connectivity showed more consistent | ||
| 158 | effects for all community parameters, than single-species models, | 172 | effects for all community parameters, than single-species models, | ||
| 159 | since the overlap between species\u2019 dispersal abilities in the | 173 | since the overlap between species\u2019 dispersal abilities in the | ||
| 160 | landscape shows poor agreement. Habitat size and quality, though less | 174 | landscape shows poor agreement. Habitat size and quality, though less | ||
| 161 | important, were also determinant in explaining community parameters | 175 | important, were also determinant in explaining community parameters | ||
| 162 | while possibly relating to the provision of suitable nesting and | 176 | while possibly relating to the provision of suitable nesting and | ||
| 163 | foraging conditions. Both habitat and landscape filters concur to | 177 | foraging conditions. Both habitat and landscape filters concur to | ||
| 164 | govern community assembly, though likely influencing different | 178 | govern community assembly, though likely influencing different | ||
| 165 | processes: while landscape connectivity determines which species can | 179 | processes: while landscape connectivity determines which species can | ||
| 166 | reach a patch, habitat quality determines which species settle in the | 180 | reach a patch, habitat quality determines which species settle in the | ||
| 167 | patch. Our results also suggest that surrogating multispecies | 181 | patch. Our results also suggest that surrogating multispecies | ||
| 168 | connectivity from single species has potential to source bias by | 182 | connectivity from single species has potential to source bias by | ||
| 169 | assuming species perceive landscape and its barriers similarly. | 183 | assuming species perceive landscape and its barriers similarly. | ||
| 170 | Inference on this issue must be gathered from as much species as | 184 | Inference on this issue must be gathered from as much species as | ||
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