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En el instante 23 de junio de 2026, 16:04:14 UTC,
-
Modificado el valor del campo
spatial_coverage
a[{'bbox': '{"type": "Polygon", "coordinates": [[[-18.16, 27.64], [4.32, 27.64], [4.32, 43.79], [-18.16, 43.79], [-18.16, 27.64]]]}', 'centroid': '{"type": "Point", "coordinates": [-6.92, 35.715]}', 'text': 'España', 'uri': 'http://datos.gob.es/recurso/sector-publico/territorio/Pais/España'}]
en Validation data is needed to support modelling in road ecology.
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| 78 | "notes": "Roads and other linear transportation infrastructures are | 78 | "notes": "Roads and other linear transportation infrastructures are | ||
| 79 | among the most ubiquitous human-made features on the globe, causing | 79 | among the most ubiquitous human-made features on the globe, causing | ||
| 80 | several pernicious negative effects on biodiversity including | 80 | several pernicious negative effects on biodiversity including | ||
| 81 | mortality due to collisions and acting as barriers to animal movement | 81 | mortality due to collisions and acting as barriers to animal movement | ||
| 82 | and gene flow. While there are several studies describing such | 82 | and gene flow. While there are several studies describing such | ||
| 83 | negative effects in a large collection of species, very few attempted | 83 | negative effects in a large collection of species, very few attempted | ||
| 84 | to quantify the consequences of such impacts on the biodiversity, in | 84 | to quantify the consequences of such impacts on the biodiversity, in | ||
| 85 | particular in population persistence. Recently, BC published an | 85 | particular in population persistence. Recently, BC published an | ||
| 86 | interesting exercise by Pinto et al.(2018) aiming to assess the | 86 | interesting exercise by Pinto et al.(2018) aiming to assess the | ||
| 87 | relative role of habitat fragmentation and additional mortality due to | 87 | relative role of habitat fragmentation and additional mortality due to | ||
| 88 | collisions with vehicles on population viability of giant anteater | 88 | collisions with vehicles on population viability of giant anteater | ||
| 89 | (Myrmecophaga tridactyla) in Brazil. The work is based on the | 89 | (Myrmecophaga tridactyla) in Brazil. The work is based on the | ||
| 90 | theoretical models developed by Bordade-\u00c1gua et al.(2011), which | 90 | theoretical models developed by Bordade-\u00c1gua et al.(2011), which | ||
| 91 | aim to provide minimum patch size (Pmin) and critical road density | 91 | aim to provide minimum patch size (Pmin) and critical road density | ||
| 92 | (Dmax) threshold values for species persistence. This is a value | 92 | (Dmax) threshold values for species persistence. This is a value | ||
| 93 | information for assisting on planning ecologically sustainable road | 93 | information for assisting on planning ecologically sustainable road | ||
| 94 | networks, particularly in times when a massive expansion of | 94 | networks, particularly in times when a massive expansion of | ||
| 95 | transportation infrastructures is foreseen (Meijer et al., 2018), with | 95 | transportation infrastructures is foreseen (Meijer et al., 2018), with | ||
| 96 | potential dramatic consequences for biodiversity. However, and this is | 96 | potential dramatic consequences for biodiversity. However, and this is | ||
| 97 | our main point, such a modeling exercise lacks a validation procedure | 97 | our main point, such a modeling exercise lacks a validation procedure | ||
| 98 | to inform the accuracy and robustness of the transferability of the | 98 | to inform the accuracy and robustness of the transferability of the | ||
| 99 | theoretical models developed by Borda-de-\u00c1gua et al.(2011) when | 99 | theoretical models developed by Borda-de-\u00c1gua et al.(2011) when | ||
| 100 | applied to this specific system. Recently, Ceia-Hasse et al.(2017) | 100 | applied to this specific system. Recently, Ceia-Hasse et al.(2017) | ||
| 101 | presented a modelling study aimed to assess the effects of | 101 | presented a modelling study aimed to assess the effects of | ||
| 102 | transportation infrastructures on carnivore population persistence at | 102 | transportation infrastructures on carnivore population persistence at | ||
| 103 | the global scale. Although \u2026", | 103 | the global scale. Although \u2026", | ||
| 104 | "notes_translated": { | 104 | "notes_translated": { | ||
| 105 | "en": "Roads and other linear transportation infrastructures are | 105 | "en": "Roads and other linear transportation infrastructures are | ||
| 106 | among the most ubiquitous human-made features on the globe, causing | 106 | among the most ubiquitous human-made features on the globe, causing | ||
| 107 | several pernicious negative effects on biodiversity including | 107 | several pernicious negative effects on biodiversity including | ||
| 108 | mortality due to collisions and acting as barriers to animal movement | 108 | mortality due to collisions and acting as barriers to animal movement | ||
| 109 | and gene flow. While there are several studies describing such | 109 | and gene flow. While there are several studies describing such | ||
| 110 | negative effects in a large collection of species, very few attempted | 110 | negative effects in a large collection of species, very few attempted | ||
| 111 | to quantify the consequences of such impacts on the biodiversity, in | 111 | to quantify the consequences of such impacts on the biodiversity, in | ||
| 112 | particular in population persistence. Recently, BC published an | 112 | particular in population persistence. Recently, BC published an | ||
| 113 | interesting exercise by Pinto et al.(2018) aiming to assess the | 113 | interesting exercise by Pinto et al.(2018) aiming to assess the | ||
| 114 | relative role of habitat fragmentation and additional mortality due to | 114 | relative role of habitat fragmentation and additional mortality due to | ||
| 115 | collisions with vehicles on population viability of giant anteater | 115 | collisions with vehicles on population viability of giant anteater | ||
| 116 | (Myrmecophaga tridactyla) in Brazil. The work is based on the | 116 | (Myrmecophaga tridactyla) in Brazil. The work is based on the | ||
| 117 | theoretical models developed by Bordade-\u00c1gua et al.(2011), which | 117 | theoretical models developed by Bordade-\u00c1gua et al.(2011), which | ||
| 118 | aim to provide minimum patch size (Pmin) and critical road density | 118 | aim to provide minimum patch size (Pmin) and critical road density | ||
| 119 | (Dmax) threshold values for species persistence. This is a value | 119 | (Dmax) threshold values for species persistence. This is a value | ||
| 120 | information for assisting on planning ecologically sustainable road | 120 | information for assisting on planning ecologically sustainable road | ||
| 121 | networks, particularly in times when a massive expansion of | 121 | networks, particularly in times when a massive expansion of | ||
| 122 | transportation infrastructures is foreseen (Meijer et al., 2018), with | 122 | transportation infrastructures is foreseen (Meijer et al., 2018), with | ||
| 123 | potential dramatic consequences for biodiversity. However, and this is | 123 | potential dramatic consequences for biodiversity. However, and this is | ||
| 124 | our main point, such a modeling exercise lacks a validation procedure | 124 | our main point, such a modeling exercise lacks a validation procedure | ||
| 125 | to inform the accuracy and robustness of the transferability of the | 125 | to inform the accuracy and robustness of the transferability of the | ||
| 126 | theoretical models developed by Borda-de-\u00c1gua et al.(2011) when | 126 | theoretical models developed by Borda-de-\u00c1gua et al.(2011) when | ||
| 127 | applied to this specific system. Recently, Ceia-Hasse et al.(2017) | 127 | applied to this specific system. Recently, Ceia-Hasse et al.(2017) | ||
| 128 | presented a modelling study aimed to assess the effects of | 128 | presented a modelling study aimed to assess the effects of | ||
| 129 | transportation infrastructures on carnivore population persistence at | 129 | transportation infrastructures on carnivore population persistence at | ||
| 130 | the global scale. Although \u2026", | 130 | the global scale. Although \u2026", | ||
| 131 | "es": "Roads and other linear transportation infrastructures are | 131 | "es": "Roads and other linear transportation infrastructures are | ||
| 132 | among the most ubiquitous human-made features on the globe, causing | 132 | among the most ubiquitous human-made features on the globe, causing | ||
| 133 | several pernicious negative effects on biodiversity including | 133 | several pernicious negative effects on biodiversity including | ||
| 134 | mortality due to collisions and acting as barriers to animal movement | 134 | mortality due to collisions and acting as barriers to animal movement | ||
| 135 | and gene flow. While there are several studies describing such | 135 | and gene flow. While there are several studies describing such | ||
| 136 | negative effects in a large collection of species, very few attempted | 136 | negative effects in a large collection of species, very few attempted | ||
| 137 | to quantify the consequences of such impacts on the biodiversity, in | 137 | to quantify the consequences of such impacts on the biodiversity, in | ||
| 138 | particular in population persistence. Recently, BC published an | 138 | particular in population persistence. Recently, BC published an | ||
| 139 | interesting exercise by Pinto et al.(2018) aiming to assess the | 139 | interesting exercise by Pinto et al.(2018) aiming to assess the | ||
| 140 | relative role of habitat fragmentation and additional mortality due to | 140 | relative role of habitat fragmentation and additional mortality due to | ||
| 141 | collisions with vehicles on population viability of giant anteater | 141 | collisions with vehicles on population viability of giant anteater | ||
| 142 | (Myrmecophaga tridactyla) in Brazil. The work is based on the | 142 | (Myrmecophaga tridactyla) in Brazil. The work is based on the | ||
| 143 | theoretical models developed by Bordade-\u00c1gua et al.(2011), which | 143 | theoretical models developed by Bordade-\u00c1gua et al.(2011), which | ||
| 144 | aim to provide minimum patch size (Pmin) and critical road density | 144 | aim to provide minimum patch size (Pmin) and critical road density | ||
| 145 | (Dmax) threshold values for species persistence. This is a value | 145 | (Dmax) threshold values for species persistence. This is a value | ||
| 146 | information for assisting on planning ecologically sustainable road | 146 | information for assisting on planning ecologically sustainable road | ||
| 147 | networks, particularly in times when a massive expansion of | 147 | networks, particularly in times when a massive expansion of | ||
| 148 | transportation infrastructures is foreseen (Meijer et al., 2018), with | 148 | transportation infrastructures is foreseen (Meijer et al., 2018), with | ||
| 149 | potential dramatic consequences for biodiversity. However, and this is | 149 | potential dramatic consequences for biodiversity. However, and this is | ||
| 150 | our main point, such a modeling exercise lacks a validation procedure | 150 | our main point, such a modeling exercise lacks a validation procedure | ||
| 151 | to inform the accuracy and robustness of the transferability of the | 151 | to inform the accuracy and robustness of the transferability of the | ||
| 152 | theoretical models developed by Borda-de-\u00c1gua et al.(2011) when | 152 | theoretical models developed by Borda-de-\u00c1gua et al.(2011) when | ||
| 153 | applied to this specific system. Recently, Ceia-Hasse et al.(2017) | 153 | applied to this specific system. Recently, Ceia-Hasse et al.(2017) | ||
| 154 | presented a modelling study aimed to assess the effects of | 154 | presented a modelling study aimed to assess the effects of | ||
| 155 | transportation infrastructures on carnivore population persistence at | 155 | transportation infrastructures on carnivore population persistence at | ||
| 156 | the global scale. Although \u2026" | 156 | the global scale. Although \u2026" | ||
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