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| 79 | "notes": "The connectivity of protected area networks depends on key | 79 | "notes": "The connectivity of protected area networks depends on key | ||
| 80 | elements located in strategic positions within the landscape, which | 80 | elements located in strategic positions within the landscape, which | ||
| 81 | uphold the ecological fluxes and sustain the diversity and longterm | 81 | uphold the ecological fluxes and sustain the diversity and longterm | ||
| 82 | viability of native biota. Landscape planning requires objective and | 82 | viability of native biota. Landscape planning requires objective and | ||
| 83 | quantitative approaches to identify those key elements and reinforce | 83 | quantitative approaches to identify those key elements and reinforce | ||
| 84 | the spatial coherence of protected area designs and related | 84 | the spatial coherence of protected area designs and related | ||
| 85 | conservation schemes. With this objective, we apply for the first time | 85 | conservation schemes. With this objective, we apply for the first time | ||
| 86 | recent methodological developments that, deriving from the probability | 86 | recent methodological developments that, deriving from the probability | ||
| 87 | of connectivity index, allow evaluating the role of both individual | 87 | of connectivity index, allow evaluating the role of both individual | ||
| 88 | protected areas and links in the intermediate landscape matrix as | 88 | protected areas and links in the intermediate landscape matrix as | ||
| 89 | providers of connectivity between the rest of the sites in the | 89 | providers of connectivity between the rest of the sites in the | ||
| 90 | network. We focus on a case study covering the forest protected areas | 90 | 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 | 91 | from the Cantabrian Range to the Western Alps (N Spain, S France and | ||
| 92 | NW Italy), considering different dispersal distances and the impact of | 92 | NW Italy), considering different dispersal distances and the impact of | ||
| 93 | highways. We show how the proposed approach is useful to identify | 93 | highways. We show how the proposed approach is useful to identify | ||
| 94 | those protected areas and links that most contribute to uphold | 94 | those protected areas and links that most contribute to uphold | ||
| 95 | functional connectivity in this transnational network, as well as | 95 | functional connectivity in this transnational network, as well as | ||
| 96 | those road sectors where the defragmentation and barrier effect | 96 | those road sectors where the defragmentation and barrier effect | ||
| 97 | mitigation measures should be prioritized. We compare our results with | 97 | mitigation measures should be prioritized. We compare our results with | ||
| 98 | other more qualitative and expert-based approaches that have been | 98 | other more qualitative and expert-based approaches that have been | ||
| 99 | reported in the same area. The methodological approach could be easily | 99 | reported in the same area. The methodological approach could be easily | ||
| 100 | adopted in a variety of other related landscape planning applications | 100 | adopted in a variety of other related landscape planning applications | ||
| 101 | at different scales, with the required quantitative tools being | 101 | at different scales, with the required quantitative tools being | ||
| 102 | available as free and open source software packages.", | 102 | available as free and open source software packages.", | ||
| 103 | "notes_translated": { | 103 | "notes_translated": { | ||
| 104 | "en": "The connectivity of protected area networks depends on key | 104 | "en": "The connectivity of protected area networks depends on key | ||
| 105 | elements located in strategic positions within the landscape, which | 105 | elements located in strategic positions within the landscape, which | ||
| 106 | uphold the ecological fluxes and sustain the diversity and longterm | 106 | uphold the ecological fluxes and sustain the diversity and longterm | ||
| 107 | viability of native biota. Landscape planning requires objective and | 107 | viability of native biota. Landscape planning requires objective and | ||
| 108 | quantitative approaches to identify those key elements and reinforce | 108 | quantitative approaches to identify those key elements and reinforce | ||
| 109 | the spatial coherence of protected area designs and related | 109 | the spatial coherence of protected area designs and related | ||
| 110 | conservation schemes. With this objective, we apply for the first time | 110 | conservation schemes. With this objective, we apply for the first time | ||
| 111 | recent methodological developments that, deriving from the probability | 111 | recent methodological developments that, deriving from the probability | ||
| 112 | of connectivity index, allow evaluating the role of both individual | 112 | of connectivity index, allow evaluating the role of both individual | ||
| 113 | protected areas and links in the intermediate landscape matrix as | 113 | protected areas and links in the intermediate landscape matrix as | ||
| 114 | providers of connectivity between the rest of the sites in the | 114 | providers of connectivity between the rest of the sites in the | ||
| 115 | network. We focus on a case study covering the forest protected areas | 115 | 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 | 116 | from the Cantabrian Range to the Western Alps (N Spain, S France and | ||
| 117 | NW Italy), considering different dispersal distances and the impact of | 117 | NW Italy), considering different dispersal distances and the impact of | ||
| 118 | highways. We show how the proposed approach is useful to identify | 118 | highways. We show how the proposed approach is useful to identify | ||
| 119 | those protected areas and links that most contribute to uphold | 119 | those protected areas and links that most contribute to uphold | ||
| 120 | functional connectivity in this transnational network, as well as | 120 | functional connectivity in this transnational network, as well as | ||
| 121 | those road sectors where the defragmentation and barrier | 121 | those road sectors where the defragmentation and barrier | ||
| 122 | effect\u00a0mitigation measures\u00a0should be prioritized. We compare | 122 | effect\u00a0mitigation measures\u00a0should be prioritized. We compare | ||
| 123 | our results with other more qualitative and expert-based approaches | 123 | our results with other more qualitative and expert-based approaches | ||
| 124 | that have been reported in the same area. The methodological approach | 124 | that have been reported in the same area. The methodological approach | ||
| 125 | could be easily adopted in a variety of other related landscape | 125 | could be easily adopted in a variety of other related landscape | ||
| 126 | planning applications at different scales, with the required | 126 | planning applications at different scales, with the required | ||
| 127 | quantitative tools being available as\u00a0free and open source | 127 | quantitative tools being available as\u00a0free and open source | ||
| 128 | software\u00a0packages.", | 128 | software\u00a0packages.", | ||
| 129 | "es": "The connectivity of protected area networks depends on key | 129 | "es": "The connectivity of protected area networks depends on key | ||
| 130 | elements located in strategic positions within the landscape, which | 130 | elements located in strategic positions within the landscape, which | ||
| 131 | uphold the ecological fluxes and sustain the diversity and longterm | 131 | uphold the ecological fluxes and sustain the diversity and longterm | ||
| 132 | viability of native biota. Landscape planning requires objective and | 132 | viability of native biota. Landscape planning requires objective and | ||
| 133 | quantitative approaches to identify those key elements and reinforce | 133 | quantitative approaches to identify those key elements and reinforce | ||
| 134 | the spatial coherence of protected area designs and related | 134 | the spatial coherence of protected area designs and related | ||
| 135 | conservation schemes. With this objective, we apply for the first time | 135 | conservation schemes. With this objective, we apply for the first time | ||
| 136 | recent methodological developments that, deriving from the probability | 136 | recent methodological developments that, deriving from the probability | ||
| 137 | of connectivity index, allow evaluating the role of both individual | 137 | of connectivity index, allow evaluating the role of both individual | ||
| 138 | protected areas and links in the intermediate landscape matrix as | 138 | protected areas and links in the intermediate landscape matrix as | ||
| 139 | providers of connectivity between the rest of the sites in the | 139 | providers of connectivity between the rest of the sites in the | ||
| 140 | network. We focus on a case study covering the forest protected areas | 140 | 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 | 141 | from the Cantabrian Range to the Western Alps (N Spain, S France and | ||
| 142 | NW Italy), considering different dispersal distances and the impact of | 142 | NW Italy), considering different dispersal distances and the impact of | ||
| 143 | highways. We show how the proposed approach is useful to identify | 143 | highways. We show how the proposed approach is useful to identify | ||
| 144 | those protected areas and links that most contribute to uphold | 144 | those protected areas and links that most contribute to uphold | ||
| 145 | functional connectivity in this transnational network, as well as | 145 | functional connectivity in this transnational network, as well as | ||
| 146 | those road sectors where the defragmentation and barrier effect | 146 | those road sectors where the defragmentation and barrier effect | ||
| 147 | mitigation measures should be prioritized. We compare our results with | 147 | mitigation measures should be prioritized. We compare our results with | ||
| 148 | other more qualitative and expert-based approaches that have been | 148 | other more qualitative and expert-based approaches that have been | ||
| 149 | reported in the same area. The methodological approach could be easily | 149 | reported in the same area. The methodological approach could be easily | ||
| 150 | adopted in a variety of other related landscape planning applications | 150 | adopted in a variety of other related landscape planning applications | ||
| 151 | at different scales, with the required quantitative tools being | 151 | at different scales, with the required quantitative tools being | ||
| 152 | available as free and open source software packages." | 152 | available as free and open source software packages." | ||
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| 243 | ps://www.sciencedirect.com/science/article/abs/pii/S0169204611001022", | 243 | ps://www.sciencedirect.com/science/article/abs/pii/S0169204611001022", | ||
| 244 | "url_type": null | 244 | "url_type": null | ||
| 245 | } | 245 | } | ||
| 246 | ], | 246 | ], | ||
| 247 | "schemingdcat_xls_metadata_template": false, | 247 | "schemingdcat_xls_metadata_template": false, | ||
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| 251 | 27.64]]]}", | 251 | 27.64]]]}", | ||
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| 260 | "uri": | 260 | "uri": | ||
| 261 | ttp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a" | 261 | ttp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a" | ||
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| 267 | "state": "active", | 267 | "state": "active", | ||
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| 269 | "es": "" | 269 | "es": "" | ||
| 270 | }, | 270 | }, | ||
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| 272 | 272 | ||||
| 273 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | 273 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | ||
| 274 | ], | 274 | ], | ||
| 275 | "tags": [ | 275 | "tags": [ | ||
| 276 | { | 276 | { | ||
| 277 | "display_name": "aspectos-globales-sobre-fragmentacion-de", | 277 | "display_name": "aspectos-globales-sobre-fragmentacion-de", | ||
| 278 | "id": "2379c860-0540-450a-9a23-72454ee80469", | 278 | "id": "2379c860-0540-450a-9a23-72454ee80469", | ||
| 279 | "name": "aspectos-globales-sobre-fragmentacion-de", | 279 | "name": "aspectos-globales-sobre-fragmentacion-de", | ||
| 280 | "state": "active", | 280 | "state": "active", | ||
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| 285 | "id": "627f9c0a-a199-4c69-b563-0c8d626e3194", | 285 | "id": "627f9c0a-a199-4c69-b563-0c8d626e3194", | ||
| 286 | "name": "fragmentacion", | 286 | "name": "fragmentacion", | ||
| 287 | "state": "active", | 287 | "state": "active", | ||
| 288 | "vocabulary_id": null | 288 | "vocabulary_id": null | ||
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| 293 | ], | 293 | ], | ||
| 294 | "theme_es": [ | 294 | "theme_es": [ | ||
| 295 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | 295 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | ||
| 296 | ], | 296 | ], | ||
| 297 | "title": "Key connectors in protected forest area networks and the | 297 | "title": "Key connectors in protected forest area networks and the | ||
| 298 | impact of highways: a transnational case study from the Cantabrian | 298 | impact of highways: a transnational case study from the Cantabrian | ||
| 299 | Range to the Western Alps (SW Europe).", | 299 | Range to the Western Alps (SW Europe).", | ||
| 300 | "title_translated": { | 300 | "title_translated": { | ||
| 301 | "en": "", | 301 | "en": "", | ||
| 302 | "es": "Key connectors in protected forest area networks and the | 302 | "es": "Key connectors in protected forest area networks and the | ||
| 303 | impact of highways: a transnational case study from the Cantabrian | 303 | impact of highways: a transnational case study from the Cantabrian | ||
| 304 | Range to the Western Alps (SW Europe)." | 304 | Range to the Western Alps (SW Europe)." | ||
| 305 | }, | 305 | }, | ||
| 306 | "topic": | 306 | "topic": | ||
| 307 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | 307 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | ||
| 308 | "type": "dataset", | 308 | "type": "dataset", | ||
| 309 | "url": | 309 | "url": | ||
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| 313 | "en": "", | 313 | "en": "", | ||
| 314 | "es": "" | 314 | "es": "" | ||
| 315 | } | 315 | } | ||
| 316 | } | 316 | } |