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en Key connectors in protected forest area networks and the impact of highways: a transnational case study from the Cantabrian Range to the Western Alps (SW Europe). -
Modificado el valor del campo
modified
del recurso Acceso al recurso a2026-06-25
(anteriormente2026-06-23
) en Key connectors in protected forest area networks and the impact of highways: a transnational case study from the Cantabrian Range to the Western Alps (SW Europe).
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| 79 | "notes": "The connectivity of protected area networks depends on key | 93 | "notes": "The connectivity of protected area networks depends on key | ||
| 80 | elements located in strategic positions within the landscape, which | 94 | elements located in strategic positions within the landscape, which | ||
| 81 | uphold the ecological fluxes and sustain the diversity and longterm | 95 | uphold the ecological fluxes and sustain the diversity and longterm | ||
| 82 | viability of native biota. Landscape planning requires objective and | 96 | viability of native biota. Landscape planning requires objective and | ||
| 83 | quantitative approaches to identify those key elements and reinforce | 97 | quantitative approaches to identify those key elements and reinforce | ||
| 84 | the spatial coherence of protected area designs and related | 98 | the spatial coherence of protected area designs and related | ||
| 85 | conservation schemes. With this objective, we apply for the first time | 99 | conservation schemes. With this objective, we apply for the first time | ||
| 86 | recent methodological developments that, deriving from the probability | 100 | recent methodological developments that, deriving from the probability | ||
| 87 | of connectivity index, allow evaluating the role of both individual | 101 | of connectivity index, allow evaluating the role of both individual | ||
| 88 | protected areas and links in the intermediate landscape matrix as | 102 | protected areas and links in the intermediate landscape matrix as | ||
| 89 | providers of connectivity between the rest of the sites in the | 103 | providers of connectivity between the rest of the sites in the | ||
| 90 | network. We focus on a case study covering the forest protected areas | 104 | network. We focus on a case study covering the forest protected areas | ||
| 91 | from the Cantabrian Range to the Western Alps (N Spain, S France and | 105 | from the Cantabrian Range to the Western Alps (N Spain, S France and | ||
| 92 | NW Italy), considering different dispersal distances and the impact of | 106 | NW Italy), considering different dispersal distances and the impact of | ||
| 93 | highways. We show how the proposed approach is useful to identify | 107 | highways. We show how the proposed approach is useful to identify | ||
| 94 | those protected areas and links that most contribute to uphold | 108 | those protected areas and links that most contribute to uphold | ||
| 95 | functional connectivity in this transnational network, as well as | 109 | functional connectivity in this transnational network, as well as | ||
| 96 | those road sectors where the defragmentation and barrier effect | 110 | those road sectors where the defragmentation and barrier effect | ||
| 97 | mitigation measures should be prioritized. We compare our results with | 111 | mitigation measures should be prioritized. We compare our results with | ||
| 98 | other more qualitative and expert-based approaches that have been | 112 | other more qualitative and expert-based approaches that have been | ||
| 99 | reported in the same area. The methodological approach could be easily | 113 | reported in the same area. The methodological approach could be easily | ||
| 100 | adopted in a variety of other related landscape planning applications | 114 | adopted in a variety of other related landscape planning applications | ||
| 101 | at different scales, with the required quantitative tools being | 115 | at different scales, with the required quantitative tools being | ||
| 102 | available as free and open source software packages.", | 116 | available as free and open source software packages.", | ||
| 103 | "notes_translated": { | 117 | "notes_translated": { | ||
| 104 | "en": "The connectivity of protected area networks depends on key | 118 | "en": "The connectivity of protected area networks depends on key | ||
| 105 | elements located in strategic positions within the landscape, which | 119 | elements located in strategic positions within the landscape, which | ||
| 106 | uphold the ecological fluxes and sustain the diversity and longterm | 120 | uphold the ecological fluxes and sustain the diversity and longterm | ||
| 107 | viability of native biota. Landscape planning requires objective and | 121 | viability of native biota. Landscape planning requires objective and | ||
| 108 | quantitative approaches to identify those key elements and reinforce | 122 | quantitative approaches to identify those key elements and reinforce | ||
| 109 | the spatial coherence of protected area designs and related | 123 | the spatial coherence of protected area designs and related | ||
| 110 | conservation schemes. With this objective, we apply for the first time | 124 | conservation schemes. With this objective, we apply for the first time | ||
| 111 | recent methodological developments that, deriving from the probability | 125 | recent methodological developments that, deriving from the probability | ||
| 112 | of connectivity index, allow evaluating the role of both individual | 126 | of connectivity index, allow evaluating the role of both individual | ||
| 113 | protected areas and links in the intermediate landscape matrix as | 127 | protected areas and links in the intermediate landscape matrix as | ||
| 114 | providers of connectivity between the rest of the sites in the | 128 | providers of connectivity between the rest of the sites in the | ||
| 115 | network. We focus on a case study covering the forest protected areas | 129 | network. We focus on a case study covering the forest protected areas | ||
| 116 | from the Cantabrian Range to the Western Alps (N Spain, S France and | 130 | from the Cantabrian Range to the Western Alps (N Spain, S France and | ||
| 117 | NW Italy), considering different dispersal distances and the impact of | 131 | NW Italy), considering different dispersal distances and the impact of | ||
| 118 | highways. We show how the proposed approach is useful to identify | 132 | highways. We show how the proposed approach is useful to identify | ||
| 119 | those protected areas and links that most contribute to uphold | 133 | those protected areas and links that most contribute to uphold | ||
| 120 | functional connectivity in this transnational network, as well as | 134 | functional connectivity in this transnational network, as well as | ||
| 121 | those road sectors where the defragmentation and barrier | 135 | those road sectors where the defragmentation and barrier | ||
| 122 | effect\u00a0mitigation measures\u00a0should be prioritized. We compare | 136 | effect\u00a0mitigation measures\u00a0should be prioritized. We compare | ||
| 123 | our results with other more qualitative and expert-based approaches | 137 | our results with other more qualitative and expert-based approaches | ||
| 124 | that have been reported in the same area. The methodological approach | 138 | that have been reported in the same area. The methodological approach | ||
| 125 | could be easily adopted in a variety of other related landscape | 139 | could be easily adopted in a variety of other related landscape | ||
| 126 | planning applications at different scales, with the required | 140 | planning applications at different scales, with the required | ||
| 127 | quantitative tools being available as\u00a0free and open source | 141 | quantitative tools being available as\u00a0free and open source | ||
| 128 | software\u00a0packages.", | 142 | software\u00a0packages.", | ||
| 129 | "es": "The connectivity of protected area networks depends on key | 143 | "es": "The connectivity of protected area networks depends on key | ||
| 130 | elements located in strategic positions within the landscape, which | 144 | elements located in strategic positions within the landscape, which | ||
| 131 | uphold the ecological fluxes and sustain the diversity and longterm | 145 | uphold the ecological fluxes and sustain the diversity and longterm | ||
| 132 | viability of native biota. Landscape planning requires objective and | 146 | viability of native biota. Landscape planning requires objective and | ||
| 133 | quantitative approaches to identify those key elements and reinforce | 147 | quantitative approaches to identify those key elements and reinforce | ||
| 134 | the spatial coherence of protected area designs and related | 148 | the spatial coherence of protected area designs and related | ||
| 135 | conservation schemes. With this objective, we apply for the first time | 149 | conservation schemes. With this objective, we apply for the first time | ||
| 136 | recent methodological developments that, deriving from the probability | 150 | recent methodological developments that, deriving from the probability | ||
| 137 | of connectivity index, allow evaluating the role of both individual | 151 | of connectivity index, allow evaluating the role of both individual | ||
| 138 | protected areas and links in the intermediate landscape matrix as | 152 | protected areas and links in the intermediate landscape matrix as | ||
| 139 | providers of connectivity between the rest of the sites in the | 153 | providers of connectivity between the rest of the sites in the | ||
| 140 | network. We focus on a case study covering the forest protected areas | 154 | network. We focus on a case study covering the forest protected areas | ||
| 141 | from the Cantabrian Range to the Western Alps (N Spain, S France and | 155 | from the Cantabrian Range to the Western Alps (N Spain, S France and | ||
| 142 | NW Italy), considering different dispersal distances and the impact of | 156 | NW Italy), considering different dispersal distances and the impact of | ||
| 143 | highways. We show how the proposed approach is useful to identify | 157 | highways. We show how the proposed approach is useful to identify | ||
| 144 | those protected areas and links that most contribute to uphold | 158 | those protected areas and links that most contribute to uphold | ||
| 145 | functional connectivity in this transnational network, as well as | 159 | functional connectivity in this transnational network, as well as | ||
| 146 | those road sectors where the defragmentation and barrier effect | 160 | those road sectors where the defragmentation and barrier effect | ||
| 147 | mitigation measures should be prioritized. We compare our results with | 161 | mitigation measures should be prioritized. We compare our results with | ||
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