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en The responses of leaf litter invertebrates to environmental gradients along road edges in subtropical island forests. -
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del recurso Acceso al recurso a2026-06-25
(anteriormente2026-06-23
) en The responses of leaf litter invertebrates to environmental gradients along road edges in subtropical island forests.
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| 82 | "notes": "Knowledge of how roads affect forest biodiversity can be | 96 | "notes": "Knowledge of how roads affect forest biodiversity can be | ||
| 83 | improved by measuring the responses of indicator species to complex | 97 | improved by measuring the responses of indicator species to complex | ||
| 84 | environmental gradients caused by these infrastructures. We studied | 98 | environmental gradients caused by these infrastructures. We studied | ||
| 85 | litter invertebrate species responses to road edges in laurel and pine | 99 | litter invertebrate species responses to road edges in laurel and pine | ||
| 86 | forests in Tenerife, Canary Islands. We sampled invertebrates from | 100 | forests in Tenerife, Canary Islands. We sampled invertebrates from | ||
| 87 | litter and assessed the environmental variation related to road | 101 | litter and assessed the environmental variation related to road | ||
| 88 | proximity. We also assessed the effect of relevant environmental | 102 | proximity. We also assessed the effect of relevant environmental | ||
| 89 | predictors on a diverse array of potential indicator species. We | 103 | predictors on a diverse array of potential indicator species. We | ||
| 90 | applied canonical ordination and non-parametric regression (Lowess) to | 104 | applied canonical ordination and non-parametric regression (Lowess) to | ||
| 91 | classify invertebrate species responses to roads and their associated | 105 | classify invertebrate species responses to roads and their associated | ||
| 92 | gradients. Three types of responses to road edge proximity were | 106 | gradients. Three types of responses to road edge proximity were | ||
| 93 | defined for the most common invertebrate taxa: edge-preferring or edge | 107 | defined for the most common invertebrate taxa: edge-preferring or edge | ||
| 94 | specialists, interior-preferring or edge-avoiders, and | 108 | specialists, interior-preferring or edge-avoiders, and | ||
| 95 | edge-indifferent or neutral species. Those species appearing most | 109 | edge-indifferent or neutral species. Those species appearing most | ||
| 96 | frequently and with higher population density between 1 and 20 m from | 110 | frequently and with higher population density between 1 and 20 m from | ||
| 97 | the edge (commonly peaking at 10 m from the road) were categorized as | 111 | the edge (commonly peaking at 10 m from the road) were categorized as | ||
| 98 | edge-preferring. We classified taxa attaining peak population | 112 | edge-preferring. We classified taxa attaining peak population | ||
| 99 | densities at or beyond 60 m from the edge (and most commonly 100 m) as | 113 | densities at or beyond 60 m from the edge (and most commonly 100 m) as | ||
| 100 | interior species. Edge-neutral species were those without an evident | 114 | interior species. Edge-neutral species were those without an evident | ||
| 101 | pattern of stabilization in abundance along the gradient and with | 115 | pattern of stabilization in abundance along the gradient and with | ||
| 102 | peaks in abundance at varying distance intervals. These edge litter | 116 | peaks in abundance at varying distance intervals. These edge litter | ||
| 103 | communities contain a high native and endemic diversity but also a | 117 | communities contain a high native and endemic diversity but also a | ||
| 104 | significant density of alien fauna. The specific patterns of | 118 | significant density of alien fauna. The specific patterns of | ||
| 105 | penetration of road edge effects on invertebrate species should be | 119 | penetration of road edge effects on invertebrate species should be | ||
| 106 | seen as having a pervasive and cumulative impact considering the | 120 | seen as having a pervasive and cumulative impact considering the | ||
| 107 | exceptionally large number of roads in these forests and the high | 121 | exceptionally large number of roads in these forests and the high | ||
| 108 | population densities of alien invertebrates. Future management plans | 122 | population densities of alien invertebrates. Future management plans | ||
| 109 | for forest conservation on the Canary Islands should include the | 123 | for forest conservation on the Canary Islands should include the | ||
| 110 | highly altered but valuable litter communities along road edges.", | 124 | highly altered but valuable litter communities along road edges.", | ||
| 111 | "notes_translated": { | 125 | "notes_translated": { | ||
| 112 | "en": "Knowledge of how roads affect forest biodiversity can be | 126 | "en": "Knowledge of how roads affect forest biodiversity can be | ||
| 113 | improved by measuring the responses of indicator species to complex | 127 | improved by measuring the responses of indicator species to complex | ||
| 114 | environmental gradients caused by these infrastructures. We studied | 128 | environmental gradients caused by these infrastructures. We studied | ||
| 115 | litter invertebrate species responses to road edges in laurel and pine | 129 | litter invertebrate species responses to road edges in laurel and pine | ||
| 116 | forests in Tenerife, Canary Islands. We sampled invertebrates from | 130 | forests in Tenerife, Canary Islands. We sampled invertebrates from | ||
| 117 | litter and assessed the environmental variation related to road | 131 | litter and assessed the environmental variation related to road | ||
| 118 | proximity. We also assessed the effect of relevant environmental | 132 | proximity. We also assessed the effect of relevant environmental | ||
| 119 | predictors on a diverse array of potential indicator species. We | 133 | predictors on a diverse array of potential indicator species. We | ||
| 120 | applied canonical ordination and non-parametric regression (Lowess) to | 134 | applied canonical ordination and non-parametric regression (Lowess) to | ||
| 121 | classify invertebrate species responses to roads and their associated | 135 | classify invertebrate species responses to roads and their associated | ||
| 122 | gradients. Three types of responses to road edge proximity were | 136 | gradients. Three types of responses to road edge proximity were | ||
| 123 | defined for the most common invertebrate taxa: edge-preferring or edge | 137 | defined for the most common invertebrate taxa: edge-preferring or edge | ||
| 124 | specialists, interior-preferring or edge-avoiders, and | 138 | specialists, interior-preferring or edge-avoiders, and | ||
| 125 | edge-indifferent or neutral species. Those species appearing most | 139 | edge-indifferent or neutral species. Those species appearing most | ||
| 126 | frequently and with higher population density between 1 and 20 m from | 140 | frequently and with higher population density between 1 and 20 m from | ||
| 127 | the edge (commonly peaking at 10 m from the road) were categorized as | 141 | the edge (commonly peaking at 10 m from the road) were categorized as | ||
| 128 | edge-preferring. We classified taxa attaining peak population | 142 | edge-preferring. We classified taxa attaining peak population | ||
| 129 | densities at or beyond 60 m from the edge (and most commonly 100 m) as | 143 | densities at or beyond 60 m from the edge (and most commonly 100 m) as | ||
| 130 | interior species. Edge-neutral species were those without an evident | 144 | interior species. Edge-neutral species were those without an evident | ||
| 131 | pattern of stabilization in abundance along the gradient and with | 145 | pattern of stabilization in abundance along the gradient and with | ||
| 132 | peaks in abundance at varying distance intervals. These edge litter | 146 | peaks in abundance at varying distance intervals. These edge litter | ||
| 133 | communities contain a high native and endemic diversity but also a | 147 | communities contain a high native and endemic diversity but also a | ||
| 134 | significant density of alien fauna. The specific patterns of | 148 | significant density of alien fauna. The specific patterns of | ||
| 135 | penetration of road edge effects on invertebrate species should be | 149 | penetration of road edge effects on invertebrate species should be | ||
| 136 | seen as having a pervasive and cumulative impact considering the | 150 | seen as having a pervasive and cumulative impact considering the | ||
| 137 | exceptionally large number of roads in these forests and the high | 151 | exceptionally large number of roads in these forests and the high | ||
| 138 | population densities of alien invertebrates. Future management plans | 152 | population densities of alien invertebrates. Future management plans | ||
| 139 | for forest conservation on the Canary Islands should include the | 153 | for forest conservation on the Canary Islands should include the | ||
| 140 | highly altered but valuable litter communities along road edges.", | 154 | highly altered but valuable litter communities along road edges.", | ||
| 141 | "es": "Knowledge of how roads affect forest biodiversity can be | 155 | "es": "Knowledge of how roads affect forest biodiversity can be | ||
| 142 | improved by measuring the responses of indicator species to complex | 156 | improved by measuring the responses of indicator species to complex | ||
| 143 | environmental gradients caused by these infrastructures. We studied | 157 | environmental gradients caused by these infrastructures. We studied | ||
| 144 | litter invertebrate species responses to road edges in laurel and pine | 158 | litter invertebrate species responses to road edges in laurel and pine | ||
| 145 | forests in Tenerife, Canary Islands. We sampled invertebrates from | 159 | forests in Tenerife, Canary Islands. We sampled invertebrates from | ||
| 146 | litter and assessed the environmental variation related to road | 160 | litter and assessed the environmental variation related to road | ||
| 147 | proximity. We also assessed the effect of relevant environmental | 161 | proximity. We also assessed the effect of relevant environmental | ||
| 148 | predictors on a diverse array of potential indicator species. We | 162 | predictors on a diverse array of potential indicator species. We | ||
| 149 | applied canonical ordination and non-parametric regression (Lowess) to | 163 | applied canonical ordination and non-parametric regression (Lowess) to | ||
| 150 | classify invertebrate species responses to roads and their associated | 164 | classify invertebrate species responses to roads and their associated | ||
| 151 | gradients. Three types of responses to road edge proximity were | 165 | gradients. Three types of responses to road edge proximity were | ||
| 152 | defined for the most common invertebrate taxa: edge-preferring or edge | 166 | defined for the most common invertebrate taxa: edge-preferring or edge | ||
| 153 | specialists, interior-preferring or edge-avoiders, and | 167 | specialists, interior-preferring or edge-avoiders, and | ||
| 154 | edge-indifferent or neutral species. Those species appearing most | 168 | edge-indifferent or neutral species. Those species appearing most | ||
| 155 | frequently and with higher population density between 1 and 20 m from | 169 | frequently and with higher population density between 1 and 20 m from | ||
| 156 | the edge (commonly peaking at 10 m from the road) were categorized as | 170 | the edge (commonly peaking at 10 m from the road) were categorized as | ||
| 157 | edge-preferring. We classified taxa attaining peak population | 171 | edge-preferring. We classified taxa attaining peak population | ||
| 158 | densities at or beyond 60 m from the edge (and most commonly 100 m) as | 172 | densities at or beyond 60 m from the edge (and most commonly 100 m) as | ||
| 159 | interior species. Edge-neutral species were those without an evident | 173 | interior species. Edge-neutral species were those without an evident | ||
| 160 | pattern of stabilization in abundance along the gradient and with | 174 | pattern of stabilization in abundance along the gradient and with | ||
| 161 | peaks in abundance at varying distance intervals. These edge litter | 175 | peaks in abundance at varying distance intervals. These edge litter | ||
| 162 | communities contain a high native and endemic diversity but also a | 176 | communities contain a high native and endemic diversity but also a | ||
| 163 | significant density of alien fauna. The specific patterns of | 177 | significant density of alien fauna. The specific patterns of | ||
| 164 | penetration of road edge effects on invertebrate species should be | 178 | penetration of road edge effects on invertebrate species should be | ||
| 165 | seen as having a pervasive and cumulative impact considering the | 179 | seen as having a pervasive and cumulative impact considering the | ||
| 166 | exceptionally large number of roads in these forests and the high | 180 | exceptionally large number of roads in these forests and the high | ||
| 167 | population densities of alien invertebrates. Future management plans | 181 | population densities of alien invertebrates. Future management plans | ||
| 168 | for forest conservation on the Canary Islands should include the | 182 | for forest conservation on the Canary Islands should include the | ||
| 169 | highly altered but valuable litter communities along road edges." | 183 | highly altered but valuable litter communities along road edges." | ||
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