Cambios
En el instante 23 de junio de 2026, 15:52:00 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 Roadkills in Europe: areas of high risk of collision and critical for populations persistence.
| f | 1 | { | f | 1 | { |
| 2 | "access_rights": | 2 | "access_rights": | ||
| 3 | .europa.eu/metadata-codelist/LimitationsOnPublicAccess/noLimitations", | 3 | .europa.eu/metadata-codelist/LimitationsOnPublicAccess/noLimitations", | ||
| 4 | "alternate_identifier": "ISBN: 978-972-778-182-9", | 4 | "alternate_identifier": "ISBN: 978-972-778-182-9", | ||
| 5 | "author": "Grilo, C., Koroleva, E., Andr\u00e1\u0161ik, R., | 5 | "author": "Grilo, C., Koroleva, E., Andr\u00e1\u0161ik, R., | ||
| 6 | B\u00edl, M. y Gonz\u00e1lez-Su\u00e1rez, M.", | 6 | B\u00edl, M. y Gonz\u00e1lez-Su\u00e1rez, M.", | ||
| 7 | "author_name": "Grilo, C., Koroleva, E., Andr\u00e1\u0161ik, R., | 7 | "author_name": "Grilo, C., Koroleva, E., Andr\u00e1\u0161ik, R., | ||
| 8 | B\u00edl, M. y Gonz\u00e1lez-Su\u00e1rez, M.", | 8 | B\u00edl, M. y Gonz\u00e1lez-Su\u00e1rez, M.", | ||
| 9 | "classification_variables": { | 9 | "classification_variables": { | ||
| 10 | "es": "" | 10 | "es": "" | ||
| 11 | }, | 11 | }, | ||
| 12 | "conforms_to": [ | 12 | "conforms_to": [ | ||
| 13 | "https://www.boe.es/eli/es/res/2013/02/19/(4)" | 13 | "https://www.boe.es/eli/es/res/2013/02/19/(4)" | ||
| 14 | ], | 14 | ], | ||
| 15 | "contact": [ | 15 | "contact": [ | ||
| 16 | { | 16 | { | ||
| 17 | "email": "organismo@example.org", | 17 | "email": "organismo@example.org", | ||
| 18 | "name": "Organismo publicador del Cat\u00e1logo", | 18 | "name": "Organismo publicador del Cat\u00e1logo", | ||
| 19 | "role": | 19 | "role": | ||
| 20 | e.ec.europa.eu/metadata-codelist/ResponsiblePartyRole/pointOfContact", | 20 | e.ec.europa.eu/metadata-codelist/ResponsiblePartyRole/pointOfContact", | ||
| 21 | "uri": | 21 | "uri": | ||
| 22 | "http://datos.gob.es/recurso/sector-publico/org/Organismo/EA0000000", | 22 | "http://datos.gob.es/recurso/sector-publico/org/Organismo/EA0000000", | ||
| 23 | "url": "https://organismo.example.org/" | 23 | "url": "https://organismo.example.org/" | ||
| 24 | } | 24 | } | ||
| 25 | ], | 25 | ], | ||
| 26 | "contact_email": "organismo@example.org", | 26 | "contact_email": "organismo@example.org", | ||
| 27 | "contact_name": "Organismo publicador del Cat\u00e1logo", | 27 | "contact_name": "Organismo publicador del Cat\u00e1logo", | ||
| 28 | "contact_role": | 28 | "contact_role": | ||
| 29 | e.ec.europa.eu/metadata-codelist/ResponsiblePartyRole/pointOfContact", | 29 | e.ec.europa.eu/metadata-codelist/ResponsiblePartyRole/pointOfContact", | ||
| 30 | "contact_uri": | 30 | "contact_uri": | ||
| 31 | "http://datos.gob.es/recurso/sector-publico/org/Organismo/EA0000000", | 31 | "http://datos.gob.es/recurso/sector-publico/org/Organismo/EA0000000", | ||
| 32 | "contact_url": "https://organismo.example.org/", | 32 | "contact_url": "https://organismo.example.org/", | ||
| 33 | "created": "2025-05-23", | 33 | "created": "2025-05-23", | ||
| 34 | "creator": [ | 34 | "creator": [ | ||
| 35 | { | 35 | { | ||
| 36 | "name": "Grilo, C., Koroleva, E., Andr\u00e1\u0161ik, R., | 36 | "name": "Grilo, C., Koroleva, E., Andr\u00e1\u0161ik, R., | ||
| 37 | B\u00edl, M. y Gonz\u00e1lez-Su\u00e1rez, M." | 37 | B\u00edl, M. y Gonz\u00e1lez-Su\u00e1rez, M." | ||
| 38 | } | 38 | } | ||
| 39 | ], | 39 | ], | ||
| 40 | "creator_user_id": "d24a314a-79ce-48c0-abd9-54cb42706da4", | 40 | "creator_user_id": "d24a314a-79ce-48c0-abd9-54cb42706da4", | ||
| 41 | "dataset_scope": "non_spatial_dataset", | 41 | "dataset_scope": "non_spatial_dataset", | ||
| 42 | "dcat_type": "http://purl.org/dc/dcmitype/Text", | 42 | "dcat_type": "http://purl.org/dc/dcmitype/Text", | ||
| 43 | "encoding": "UTF-8", | 43 | "encoding": "UTF-8", | ||
| 44 | "featured": false, | 44 | "featured": false, | ||
| 45 | "graphic_overview": | 45 | "graphic_overview": | ||
| 46 | om/images?q=tbn:ANd9GcRb54JGfwMSPjkYlDyIL_yeW3XeePRl4EebQDu0igf2yw&s", | 46 | om/images?q=tbn:ANd9GcRb54JGfwMSPjkYlDyIL_yeW3XeePRl4EebQDu0igf2yw&s", | ||
| 47 | "groups": [], | 47 | "groups": [], | ||
| 48 | "hvd": "non_hvd", | 48 | "hvd": "non_hvd", | ||
| 49 | "id": "d9d1665f-9f1a-57d4-9695-10fb3ae34592", | 49 | "id": "d9d1665f-9f1a-57d4-9695-10fb3ae34592", | ||
| 50 | "identifier": "d9d1665f-9f1a-57d4-9695-10fb3ae34592", | 50 | "identifier": "d9d1665f-9f1a-57d4-9695-10fb3ae34592", | ||
| 51 | "inspire_id": "", | 51 | "inspire_id": "", | ||
| 52 | "isopen": true, | 52 | "isopen": true, | ||
| 53 | "language": | 53 | "language": | ||
| 54 | "http://publications.europa.eu/resource/authority/language/SPA", | 54 | "http://publications.europa.eu/resource/authority/language/SPA", | ||
| 55 | "license_id": "cc-by", | 55 | "license_id": "cc-by", | ||
| 56 | "license_title": "Creative Commons Attribution", | 56 | "license_title": "Creative Commons Attribution", | ||
| 57 | "license_url": "http://www.opendefinition.org/licenses/cc-by", | 57 | "license_url": "http://www.opendefinition.org/licenses/cc-by", | ||
| 58 | "lineage_process_steps": [], | 58 | "lineage_process_steps": [], | ||
| 59 | "lineage_source": [ | 59 | "lineage_source": [ | ||
| 60 | "2020 IENE International Conference. Abstract book. Vol. 4.2.2", | 60 | "2020 IENE International Conference. Abstract book. Vol. 4.2.2", | ||
| 61 | "Num. 2", | 61 | "Num. 2", | ||
| 62 | "pag. 85" | 62 | "pag. 85" | ||
| 63 | ], | 63 | ], | ||
| 64 | "maintainer": "", | 64 | "maintainer": "", | ||
| 65 | "maintainer_name": "", | 65 | "maintainer_name": "", | ||
| 66 | "metadata_created": "2026-06-23T14:48:52.235799", | 66 | "metadata_created": "2026-06-23T14:48:52.235799", | ||
| n | 67 | "metadata_modified": "2026-06-23T14:48:52.235804", | n | 67 | "metadata_modified": "2026-06-23T15:51:59.931714", |
| 68 | "metadata_profile": [ | 68 | "metadata_profile": [ | ||
| 69 | "https://www.w3.org/TR/vocab-dcat-3/" | 69 | "https://www.w3.org/TR/vocab-dcat-3/" | ||
| 70 | ], | 70 | ], | ||
| 71 | "miteco_data_population": { | 71 | "miteco_data_population": { | ||
| 72 | "es": "" | 72 | "es": "" | ||
| 73 | }, | 73 | }, | ||
| 74 | "miteco_data_territory": { | 74 | "miteco_data_territory": { | ||
| 75 | "es": "" | 75 | "es": "" | ||
| 76 | }, | 76 | }, | ||
| 77 | "miteco_dataset_type": | 77 | "miteco_dataset_type": | ||
| 78 | //publications.europa.eu/resource/authority/dataset-type/STATISTICAL", | 78 | //publications.europa.eu/resource/authority/dataset-type/STATISTICAL", | ||
| 79 | "miteco_geo_level": "1", | 79 | "miteco_geo_level": "1", | ||
| 80 | "modified": "2026-06-23", | 80 | "modified": "2026-06-23", | ||
| 81 | "name": "d9d1665f-9f1a-57d4-9695-10fb3ae34592", | 81 | "name": "d9d1665f-9f1a-57d4-9695-10fb3ae34592", | ||
| 82 | "notes": "Roads and other linear infrastructures are among the | 82 | "notes": "Roads and other linear infrastructures are among the | ||
| 83 | largest and most visible human-made artefacts on the planet today and | 83 | largest and most visible human-made artefacts on the planet today and | ||
| 84 | represent a threat for both endangered and common species, mainly due | 84 | represent a threat for both endangered and common species, mainly due | ||
| 85 | to additional mortality from collisions with vehicles. There is strong | 85 | to additional mortality from collisions with vehicles. There is strong | ||
| 86 | evidence that additional non-natural mortality affects many species | 86 | evidence that additional non-natural mortality affects many species | ||
| 87 | and a growing number of populations could have increased risk of | 87 | and a growing number of populations could have increased risk of | ||
| 88 | extinction unless effective mitigation actions are applied. At a | 88 | extinction unless effective mitigation actions are applied. At a | ||
| 89 | global scale, Europe is among the regions with highest transport | 89 | global scale, Europe is among the regions with highest transport | ||
| 90 | infrastructures density. Between 1970 and 2000 the kilometres of built | 90 | infrastructures density. Between 1970 and 2000 the kilometres of built | ||
| 91 | roads more than tripled in several countries in Europe (EU-15) | 91 | roads more than tripled in several countries in Europe (EU-15) | ||
| 92 | reaching up to 3 million km of which around 51 500 km consisted of | 92 | reaching up to 3 million km of which around 51 500 km consisted of | ||
| 93 | motorways (1.7%). Currently, 50% of the continent is within 1.5 km of | 93 | motorways (1.7%). Currently, 50% of the continent is within 1.5 km of | ||
| 94 | transportation infrastructure which may lead to declines in birds and | 94 | transportation infrastructure which may lead to declines in birds and | ||
| 95 | mammals. We urgently need to advance our understanding of how roads | 95 | mammals. We urgently need to advance our understanding of how roads | ||
| 96 | affect biodiversity through two steps: 1) identifying which species | 96 | affect biodiversity through two steps: 1) identifying which species | ||
| 97 | and regions are more at risk from infrastructures; and 2) determining | 97 | and regions are more at risk from infrastructures; and 2) determining | ||
| 98 | where those risks result in impacts (loss of biodiversity). Road | 98 | where those risks result in impacts (loss of biodiversity). Road | ||
| 99 | ecology as a discipline has largely focused on the first step. In | 99 | ecology as a discipline has largely focused on the first step. In | ||
| 100 | Europe, roadkill rates have been estimated for a wide range of | 100 | Europe, roadkill rates have been estimated for a wide range of | ||
| 101 | vertebrates with millions of casualties detected each year. However, | 101 | vertebrates with millions of casualties detected each year. However, | ||
| 102 | we still lack estimates for all species or areas, even in well-studied | 102 | we still lack estimates for all species or areas, even in well-studied | ||
| 103 | regions. The aim of this study is to determine which species are at | 103 | regions. The aim of this study is to determine which species are at | ||
| 104 | risk due to roads and where roads can impact population persistence | 104 | risk due to roads and where roads can impact population persistence | ||
| 105 | and biodiversity. We focused on bird and mammalian species in Europe | 105 | and biodiversity. We focused on bird and mammalian species in Europe | ||
| 106 | as a case study. First, we developed a predictive model of roadkill | 106 | as a case study. First, we developed a predictive model of roadkill | ||
| 107 | rates based on diverse species traits which allowed us to predict | 107 | rates based on diverse species traits which allowed us to predict | ||
| 108 | rates for all European terrestrial bird and mammal species and to map | 108 | rates for all European terrestrial bird and mammal species and to map | ||
| 109 | the potential incidence of roadkills. We fitted trait-based random | 109 | the potential incidence of roadkills. We fitted trait-based random | ||
| 110 | forest regression models separately for birds and mammals to explain | 110 | forest regression models separately for birds and mammals to explain | ||
| 111 | empirical roadkill rates. We used all available roadkill rates and the | 111 | empirical roadkill rates. We used all available roadkill rates and the | ||
| 112 | following predictors: species trait data, multiple characteristics of | 112 | following predictors: species trait data, multiple characteristics of | ||
| 113 | the study (latitude and longitude and survey interval) to account for | 113 | the study (latitude and longitude and survey interval) to account for | ||
| 114 | species abundance and detectability, and taxonomic order to account | 114 | species abundance and detectability, and taxonomic order to account | ||
| 115 | for evolutionary relationships. Second, we used a generalized | 115 | for evolutionary relationships. Second, we used a generalized | ||
| 116 | population model to estimate long-term vulnerability to road | 116 | population model to estimate long-term vulnerability to road | ||
| 117 | mortality. We estimated ~194 million birds and ~29 million mammals may | 117 | mortality. We estimated ~194 million birds and ~29 million mammals may | ||
| 118 | be killed each year on the European road network. Overall, species | 118 | be killed each year on the European road network. Overall, species | ||
| 119 | with higher roadkill rates differ from those in which roadkill is | 119 | with higher roadkill rates differ from those in which roadkill is | ||
| 120 | likely to affect long-term persistence. Simplified models of species | 120 | likely to affect long-term persistence. Simplified models of species | ||
| 121 | traits and wildlife-roads interactions at a macro scale allow a first | 121 | traits and wildlife-roads interactions at a macro scale allow a first | ||
| 122 | assessment of the road mortality on wildlife and implications on | 122 | assessment of the road mortality on wildlife and implications on | ||
| 123 | population\u2019s persistence. This macroecological approach provide | 123 | population\u2019s persistence. This macroecological approach provide | ||
| 124 | guidance for national road planning, support the definition of target | 124 | guidance for national road planning, support the definition of target | ||
| 125 | areas for further testing at a finer-scale resolution, and ultimately | 125 | areas for further testing at a finer-scale resolution, and ultimately | ||
| 126 | prioritize site-specific areas where mitigation would be most | 126 | prioritize site-specific areas where mitigation would be most | ||
| 127 | beneficial.", | 127 | beneficial.", | ||
| 128 | "notes_translated": { | 128 | "notes_translated": { | ||
| 129 | "en": "Roads and other linear infrastructures are among the | 129 | "en": "Roads and other linear infrastructures are among the | ||
| 130 | largest and most visible human-made artefacts on the planet today and | 130 | largest and most visible human-made artefacts on the planet today and | ||
| 131 | represent a threat for both endangered and common species, mainly due | 131 | represent a threat for both endangered and common species, mainly due | ||
| 132 | to additional mortality from collisions with vehicles. There is strong | 132 | to additional mortality from collisions with vehicles. There is strong | ||
| 133 | evidence that additional non-natural mortality affects many species | 133 | evidence that additional non-natural mortality affects many species | ||
| 134 | and a growing number of populations could have increased risk of | 134 | and a growing number of populations could have increased risk of | ||
| 135 | extinction unless effective mitigation actions are applied. At a | 135 | extinction unless effective mitigation actions are applied. At a | ||
| 136 | global scale, Europe is among the regions with highest transport | 136 | global scale, Europe is among the regions with highest transport | ||
| 137 | infrastructures density. Between 1970 and 2000 the kilometres of built | 137 | infrastructures density. Between 1970 and 2000 the kilometres of built | ||
| 138 | roads more than tripled in several countries in Europe (EU-15) | 138 | roads more than tripled in several countries in Europe (EU-15) | ||
| 139 | reaching up to 3 million km of which around 51 500 km consisted of | 139 | reaching up to 3 million km of which around 51 500 km consisted of | ||
| 140 | motorways (1.7%). Currently, 50% of the continent is within 1.5 km of | 140 | motorways (1.7%). Currently, 50% of the continent is within 1.5 km of | ||
| 141 | transportation infrastructure which may lead to declines in birds and | 141 | transportation infrastructure which may lead to declines in birds and | ||
| 142 | mammals. We urgently need to advance our understanding of how roads | 142 | mammals. We urgently need to advance our understanding of how roads | ||
| 143 | affect biodiversity through two steps: 1) identifying which species | 143 | affect biodiversity through two steps: 1) identifying which species | ||
| 144 | and regions are more at risk from infrastructures; and 2) determining | 144 | and regions are more at risk from infrastructures; and 2) determining | ||
| 145 | where those risks result in impacts (loss of biodiversity). Road | 145 | where those risks result in impacts (loss of biodiversity). Road | ||
| 146 | ecology as a discipline has largely focused on the first step. In | 146 | ecology as a discipline has largely focused on the first step. In | ||
| 147 | Europe, roadkill rates have been estimated for a wide range of | 147 | Europe, roadkill rates have been estimated for a wide range of | ||
| 148 | vertebrates with millions of casualties detected each year. However, | 148 | vertebrates with millions of casualties detected each year. However, | ||
| 149 | we still lack estimates for all species or areas, even in well-studied | 149 | we still lack estimates for all species or areas, even in well-studied | ||
| 150 | regions. The aim of this study is to determine which species are at | 150 | regions. The aim of this study is to determine which species are at | ||
| 151 | risk due to roads and where roads can impact population persistence | 151 | risk due to roads and where roads can impact population persistence | ||
| 152 | and biodiversity. We focused on bird and mammalian species in Europe | 152 | and biodiversity. We focused on bird and mammalian species in Europe | ||
| 153 | as a case study. First, we developed a predictive model of roadkill | 153 | as a case study. First, we developed a predictive model of roadkill | ||
| 154 | rates based on diverse species traits which allowed us to predict | 154 | rates based on diverse species traits which allowed us to predict | ||
| 155 | rates for all European terrestrial bird and mammal species and to map | 155 | rates for all European terrestrial bird and mammal species and to map | ||
| 156 | the potential incidence of roadkills. We fitted trait-based random | 156 | the potential incidence of roadkills. We fitted trait-based random | ||
| 157 | forest regression models separately for birds and mammals to explain | 157 | forest regression models separately for birds and mammals to explain | ||
| 158 | empirical roadkill rates. We used all available roadkill rates and the | 158 | empirical roadkill rates. We used all available roadkill rates and the | ||
| 159 | following predictors: species trait data, multiple characteristics of | 159 | following predictors: species trait data, multiple characteristics of | ||
| 160 | the study (latitude and longitude and survey interval) to account for | 160 | the study (latitude and longitude and survey interval) to account for | ||
| 161 | species abundance and detectability, and taxonomic order to account | 161 | species abundance and detectability, and taxonomic order to account | ||
| 162 | for evolutionary relationships. Second, we used a generalized | 162 | for evolutionary relationships. Second, we used a generalized | ||
| 163 | population model to estimate long-term vulnerability to road | 163 | population model to estimate long-term vulnerability to road | ||
| 164 | mortality. We estimated ~194 million birds and ~29 million mammals may | 164 | mortality. We estimated ~194 million birds and ~29 million mammals may | ||
| 165 | be killed each year on the European road network. Overall, species | 165 | be killed each year on the European road network. Overall, species | ||
| 166 | with higher roadkill rates differ from those in which roadkill is | 166 | with higher roadkill rates differ from those in which roadkill is | ||
| 167 | likely to affect long-term persistence. Simplified models of species | 167 | likely to affect long-term persistence. Simplified models of species | ||
| 168 | traits and wildlife-roads interactions at a macro scale allow a first | 168 | traits and wildlife-roads interactions at a macro scale allow a first | ||
| 169 | assessment of the road mortality on wildlife and implications on | 169 | assessment of the road mortality on wildlife and implications on | ||
| 170 | population\u2019s persistence. This macroecological approach provide | 170 | population\u2019s persistence. This macroecological approach provide | ||
| 171 | guidance for national road planning, support the definition of target | 171 | guidance for national road planning, support the definition of target | ||
| 172 | areas for further testing at a finer-scale resolution, and ultimately | 172 | areas for further testing at a finer-scale resolution, and ultimately | ||
| 173 | prioritize site-specific areas where mitigation would be most | 173 | prioritize site-specific areas where mitigation would be most | ||
| 174 | beneficial.", | 174 | beneficial.", | ||
| 175 | "es": "Roads and other linear infrastructures are among the | 175 | "es": "Roads and other linear infrastructures are among the | ||
| 176 | largest and most visible human-made artefacts on the planet today and | 176 | largest and most visible human-made artefacts on the planet today and | ||
| 177 | represent a threat for both endangered and common species, mainly due | 177 | represent a threat for both endangered and common species, mainly due | ||
| 178 | to additional mortality from collisions with vehicles. There is strong | 178 | to additional mortality from collisions with vehicles. There is strong | ||
| 179 | evidence that additional non-natural mortality affects many species | 179 | evidence that additional non-natural mortality affects many species | ||
| 180 | and a growing number of populations could have increased risk of | 180 | and a growing number of populations could have increased risk of | ||
| 181 | extinction unless effective mitigation actions are applied. At a | 181 | extinction unless effective mitigation actions are applied. At a | ||
| 182 | global scale, Europe is among the regions with highest transport | 182 | global scale, Europe is among the regions with highest transport | ||
| 183 | infrastructures density. Between 1970 and 2000 the kilometres of built | 183 | infrastructures density. Between 1970 and 2000 the kilometres of built | ||
| 184 | roads more than tripled in several countries in Europe (EU-15) | 184 | roads more than tripled in several countries in Europe (EU-15) | ||
| 185 | reaching up to 3 million km of which around 51 500 km consisted of | 185 | reaching up to 3 million km of which around 51 500 km consisted of | ||
| 186 | motorways (1.7%). Currently, 50% of the continent is within 1.5 km of | 186 | motorways (1.7%). Currently, 50% of the continent is within 1.5 km of | ||
| 187 | transportation infrastructure which may lead to declines in birds and | 187 | transportation infrastructure which may lead to declines in birds and | ||
| 188 | mammals. We urgently need to advance our understanding of how roads | 188 | mammals. We urgently need to advance our understanding of how roads | ||
| 189 | affect biodiversity through two steps: 1) identifying which species | 189 | affect biodiversity through two steps: 1) identifying which species | ||
| 190 | and regions are more at risk from infrastructures; and 2) determining | 190 | and regions are more at risk from infrastructures; and 2) determining | ||
| 191 | where those risks result in impacts (loss of biodiversity). Road | 191 | where those risks result in impacts (loss of biodiversity). Road | ||
| 192 | ecology as a discipline has largely focused on the first step. In | 192 | ecology as a discipline has largely focused on the first step. In | ||
| 193 | Europe, roadkill rates have been estimated for a wide range of | 193 | Europe, roadkill rates have been estimated for a wide range of | ||
| 194 | vertebrates with millions of casualties detected each year. However, | 194 | vertebrates with millions of casualties detected each year. However, | ||
| 195 | we still lack estimates for all species or areas, even in well-studied | 195 | we still lack estimates for all species or areas, even in well-studied | ||
| 196 | regions. The aim of this study is to determine which species are at | 196 | regions. The aim of this study is to determine which species are at | ||
| 197 | risk due to roads and where roads can impact population persistence | 197 | risk due to roads and where roads can impact population persistence | ||
| 198 | and biodiversity. We focused on bird and mammalian species in Europe | 198 | and biodiversity. We focused on bird and mammalian species in Europe | ||
| 199 | as a case study. First, we developed a predictive model of roadkill | 199 | as a case study. First, we developed a predictive model of roadkill | ||
| 200 | rates based on diverse species traits which allowed us to predict | 200 | rates based on diverse species traits which allowed us to predict | ||
| 201 | rates for all European terrestrial bird and mammal species and to map | 201 | rates for all European terrestrial bird and mammal species and to map | ||
| 202 | the potential incidence of roadkills. We fitted trait-based random | 202 | the potential incidence of roadkills. We fitted trait-based random | ||
| 203 | forest regression models separately for birds and mammals to explain | 203 | forest regression models separately for birds and mammals to explain | ||
| 204 | empirical roadkill rates. We used all available roadkill rates and the | 204 | empirical roadkill rates. We used all available roadkill rates and the | ||
| 205 | following predictors: species trait data, multiple characteristics of | 205 | following predictors: species trait data, multiple characteristics of | ||
| 206 | the study (latitude and longitude and survey interval) to account for | 206 | the study (latitude and longitude and survey interval) to account for | ||
| 207 | species abundance and detectability, and taxonomic order to account | 207 | species abundance and detectability, and taxonomic order to account | ||
| 208 | for evolutionary relationships. Second, we used a generalized | 208 | for evolutionary relationships. Second, we used a generalized | ||
| 209 | population model to estimate long-term vulnerability to road | 209 | population model to estimate long-term vulnerability to road | ||
| 210 | mortality. We estimated ~194 million birds and ~29 million mammals may | 210 | mortality. We estimated ~194 million birds and ~29 million mammals may | ||
| 211 | be killed each year on the European road network. Overall, species | 211 | be killed each year on the European road network. Overall, species | ||
| 212 | with higher roadkill rates differ from those in which roadkill is | 212 | with higher roadkill rates differ from those in which roadkill is | ||
| 213 | likely to affect long-term persistence. Simplified models of species | 213 | likely to affect long-term persistence. Simplified models of species | ||
| 214 | traits and wildlife-roads interactions at a macro scale allow a first | 214 | traits and wildlife-roads interactions at a macro scale allow a first | ||
| 215 | assessment of the road mortality on wildlife and implications on | 215 | assessment of the road mortality on wildlife and implications on | ||
| 216 | population\u2019s persistence. This macroecological approach provide | 216 | population\u2019s persistence. This macroecological approach provide | ||
| 217 | guidance for national road planning, support the definition of target | 217 | guidance for national road planning, support the definition of target | ||
| 218 | areas for further testing at a finer-scale resolution, and ultimately | 218 | areas for further testing at a finer-scale resolution, and ultimately | ||
| 219 | prioritize site-specific areas where mitigation would be most | 219 | prioritize site-specific areas where mitigation would be most | ||
| 220 | beneficial." | 220 | beneficial." | ||
| 221 | }, | 221 | }, | ||
| 222 | "num_resources": 1, | 222 | "num_resources": 1, | ||
| 223 | "num_tags": 2, | 223 | "num_tags": 2, | ||
| 224 | "organization": { | 224 | "organization": { | ||
| 225 | "approval_status": "approved", | 225 | "approval_status": "approved", | ||
| 226 | "created": "2026-06-23T14:36:08.942021", | 226 | "created": "2026-06-23T14:36:08.942021", | ||
| 227 | "description": "", | 227 | "description": "", | ||
| 228 | "id": "bca483f7-26e2-4ed8-99e8-65f5b3c7a26e", | 228 | "id": "bca483f7-26e2-4ed8-99e8-65f5b3c7a26e", | ||
| 229 | "image_url": "", | 229 | "image_url": "", | ||
| 230 | "is_organization": true, | 230 | "is_organization": true, | ||
| 231 | "name": "iepnb", | 231 | "name": "iepnb", | ||
| 232 | "state": "active", | 232 | "state": "active", | ||
| 233 | "title": "", | 233 | "title": "", | ||
| 234 | "type": "organization" | 234 | "type": "organization" | ||
| 235 | }, | 235 | }, | ||
| 236 | "owner_org": "bca483f7-26e2-4ed8-99e8-65f5b3c7a26e", | 236 | "owner_org": "bca483f7-26e2-4ed8-99e8-65f5b3c7a26e", | ||
| 237 | "private": false, | 237 | "private": false, | ||
| 238 | "provenance": { | 238 | "provenance": { | ||
| 239 | "en": "", | 239 | "en": "", | ||
| 240 | "es": "" | 240 | "es": "" | ||
| 241 | }, | 241 | }, | ||
| 242 | "publisher": [ | 242 | "publisher": [ | ||
| 243 | { | 243 | { | ||
| 244 | "email": "buzon-bdatos@miteco.es", | 244 | "email": "buzon-bdatos@miteco.es", | ||
| 245 | "name": "\u00c1rea de Banco de Datos de la Naturaleza. | 245 | "name": "\u00c1rea de Banco de Datos de la Naturaleza. | ||
| 246 | Direcci\u00f3n General Biodiversidad, Bosques y Desertificaci\u00f3n. | 246 | Direcci\u00f3n General Biodiversidad, Bosques y Desertificaci\u00f3n. | ||
| 247 | Ministerio para la Transici\u00f3n Ecol\u00f3gica y el Reto | 247 | Ministerio para la Transici\u00f3n Ecol\u00f3gica y el Reto | ||
| 248 | Demogr\u00e1fico", | 248 | Demogr\u00e1fico", | ||
| 249 | "type": "http://purl.org/adms/publishertype/NationalAuthority", | 249 | "type": "http://purl.org/adms/publishertype/NationalAuthority", | ||
| 250 | "uri": "https://iepnb.es/catalogo/organization/iepnb", | 250 | "uri": "https://iepnb.es/catalogo/organization/iepnb", | ||
| 251 | "url": "https://www.miteco.gob.es/" | 251 | "url": "https://www.miteco.gob.es/" | ||
| 252 | } | 252 | } | ||
| 253 | ], | 253 | ], | ||
| 254 | "publisher_email": "buzon-bdatos@miteco.es", | 254 | "publisher_email": "buzon-bdatos@miteco.es", | ||
| 255 | "publisher_name": "\u00c1rea de Banco de Datos de la Naturaleza. | 255 | "publisher_name": "\u00c1rea de Banco de Datos de la Naturaleza. | ||
| 256 | Direcci\u00f3n General Biodiversidad, Bosques y Desertificaci\u00f3n. | 256 | Direcci\u00f3n General Biodiversidad, Bosques y Desertificaci\u00f3n. | ||
| 257 | Ministerio para la Transici\u00f3n Ecol\u00f3gica y el Reto | 257 | Ministerio para la Transici\u00f3n Ecol\u00f3gica y el Reto | ||
| 258 | Demogr\u00e1fico", | 258 | Demogr\u00e1fico", | ||
| 259 | "publisher_type": | 259 | "publisher_type": | ||
| 260 | "http://purl.org/adms/publishertype/NationalAuthority", | 260 | "http://purl.org/adms/publishertype/NationalAuthority", | ||
| 261 | "publisher_uri": "https://iepnb.es/catalogo/organization/iepnb", | 261 | "publisher_uri": "https://iepnb.es/catalogo/organization/iepnb", | ||
| 262 | "publisher_url": "https://www.miteco.gob.es/", | 262 | "publisher_url": "https://www.miteco.gob.es/", | ||
| 263 | "purpose": { | 263 | "purpose": { | ||
| 264 | "en": "", | 264 | "en": "", | ||
| 265 | "es": "" | 265 | "es": "" | ||
| 266 | }, | 266 | }, | ||
| 267 | "reference": [], | 267 | "reference": [], | ||
| 268 | "relationships_as_object": [], | 268 | "relationships_as_object": [], | ||
| 269 | "relationships_as_subject": [], | 269 | "relationships_as_subject": [], | ||
| 270 | "resources": [ | 270 | "resources": [ | ||
| 271 | { | 271 | { | ||
| 272 | "access_url": | 272 | "access_url": | ||
| 273 | 57d4-9695-10fb3ae34592/resource/68fe50b5-b6e7-4a53-b3c5-ee07f9336803", | 273 | 57d4-9695-10fb3ae34592/resource/68fe50b5-b6e7-4a53-b3c5-ee07f9336803", | ||
| 274 | "availability": | 274 | "availability": | ||
| 275 | ications.europa.eu/resource/authority/planned-availability/AVAILABLE", | 275 | ications.europa.eu/resource/authority/planned-availability/AVAILABLE", | ||
| 276 | "cache_last_updated": null, | 276 | "cache_last_updated": null, | ||
| 277 | "cache_url": null, | 277 | "cache_url": null, | ||
| 278 | "created": "2021-01-14T00:00:00", | 278 | "created": "2021-01-14T00:00:00", | ||
| 279 | "dataset_id": "087218b0-d9a6-4436-9e2c-799520f2bee8", | 279 | "dataset_id": "087218b0-d9a6-4436-9e2c-799520f2bee8", | ||
| 280 | "datastore_active": false, | 280 | "datastore_active": false, | ||
| 281 | "datastore_contains_all_records_of_source_file": false, | 281 | "datastore_contains_all_records_of_source_file": false, | ||
| 282 | "description": "Art\u00edculo en libro", | 282 | "description": "Art\u00edculo en libro", | ||
| 283 | "download_url": | 283 | "download_url": | ||
| 284 | "https://www.iene.info/content/uploads/iene2020-abstract-book.pdf", | 284 | "https://www.iene.info/content/uploads/iene2020-abstract-book.pdf", | ||
| 285 | "encoding": "UTF-8", | 285 | "encoding": "UTF-8", | ||
| 286 | "format": "HTML", | 286 | "format": "HTML", | ||
| 287 | "hash": "", | 287 | "hash": "", | ||
| 288 | "id": "68fe50b5-b6e7-4a53-b3c5-ee07f9336803", | 288 | "id": "68fe50b5-b6e7-4a53-b3c5-ee07f9336803", | ||
| 289 | "issued": "", | 289 | "issued": "", | ||
| 290 | "language": | 290 | "language": | ||
| 291 | "http://publications.europa.eu/resource/authority/language/ENG", | 291 | "http://publications.europa.eu/resource/authority/language/ENG", | ||
| 292 | "last_modified": null, | 292 | "last_modified": null, | ||
| 293 | "license": "http://creativecommons.org/licenses/by/4.0/", | 293 | "license": "http://creativecommons.org/licenses/by/4.0/", | ||
| 294 | "license_id": "cc-by", | 294 | "license_id": "cc-by", | ||
| n | 295 | "metadata_modified": "2026-06-23T14:48:52.232354", | n | 295 | "metadata_modified": "2026-06-23T15:51:59.935738", |
| 296 | "mimetype": | 296 | "mimetype": | ||
| 297 | "https://www.iana.org/assignments/media-types/text/html", | 297 | "https://www.iana.org/assignments/media-types/text/html", | ||
| 298 | "mimetype_inner": null, | 298 | "mimetype_inner": null, | ||
| 299 | "modified": "2026-06-23", | 299 | "modified": "2026-06-23", | ||
| 300 | "name": "Acceso al recurso", | 300 | "name": "Acceso al recurso", | ||
| 301 | "package_id": "d9d1665f-9f1a-57d4-9695-10fb3ae34592", | 301 | "package_id": "d9d1665f-9f1a-57d4-9695-10fb3ae34592", | ||
| 302 | "position": 0, | 302 | "position": 0, | ||
| 303 | "protocol": null, | 303 | "protocol": null, | ||
| 304 | "resource_type": null, | 304 | "resource_type": null, | ||
| 305 | "rights": | 305 | "rights": | ||
| 306 | .europa.eu/metadata-codelist/LimitationsOnPublicAccess/noLimitations", | 306 | .europa.eu/metadata-codelist/LimitationsOnPublicAccess/noLimitations", | ||
| 307 | "size": 0, | 307 | "size": 0, | ||
| 308 | "state": "active", | 308 | "state": "active", | ||
| 309 | "status": "http://purl.org/adms/status/Completed", | 309 | "status": "http://purl.org/adms/status/Completed", | ||
| 310 | "url": | 310 | "url": | ||
| 311 | "https://www.iene.info/content/uploads/iene2020-abstract-book.pdf", | 311 | "https://www.iene.info/content/uploads/iene2020-abstract-book.pdf", | ||
| 312 | "url_type": null | 312 | "url_type": null | ||
| 313 | } | 313 | } | ||
| 314 | ], | 314 | ], | ||
| 315 | "schemingdcat_xls_metadata_template": false, | 315 | "schemingdcat_xls_metadata_template": false, | ||
| 316 | "source": "", | 316 | "source": "", | ||
| 317 | "spatial": "{\"type\": \"Polygon\", \"coordinates\": [[[-18.16, | 317 | "spatial": "{\"type\": \"Polygon\", \"coordinates\": [[[-18.16, | ||
| 318 | 27.64], [4.32, 27.64], [4.32, 43.79], [-18.16, 43.79], [-18.16, | 318 | 27.64], [4.32, 27.64], [4.32, 43.79], [-18.16, 43.79], [-18.16, | ||
| 319 | 27.64]]]}", | 319 | 27.64]]]}", | ||
| 320 | "spatial_coverage": [ | 320 | "spatial_coverage": [ | ||
| 321 | { | 321 | { | ||
| t | 322 | "bbox": { | t | 322 | "bbox": "{\"type\": \"Polygon\", \"coordinates\": [[[-18.16, |
| 323 | "coordinates": [ | 323 | 27.64], [4.32, 27.64], [4.32, 43.79], [-18.16, 43.79], [-18.16, | ||
| 324 | [ | 324 | 27.64]]]}", | ||
| 325 | [ | 325 | "centroid": "{\"type\": \"Point\", \"coordinates\": [-6.92, | ||
| 326 | -18.16, | 326 | 35.715]}", | ||
| 327 | 27.64 | ||||
| 328 | ], | ||||
| 329 | [ | ||||
| 330 | 4.32, | ||||
| 331 | 27.64 | ||||
| 332 | ], | ||||
| 333 | [ | ||||
| 334 | 4.32, | ||||
| 335 | 43.79 | ||||
| 336 | ], | ||||
| 337 | [ | ||||
| 338 | -18.16, | ||||
| 339 | 43.79 | ||||
| 340 | ], | ||||
| 341 | [ | ||||
| 342 | -18.16, | ||||
| 343 | 27.64 | ||||
| 344 | ] | ||||
| 345 | ] | ||||
| 346 | ], | ||||
| 347 | "type": "Polygon" | ||||
| 348 | }, | ||||
| 349 | "centroid": { | ||||
| 350 | "coordinates": [ | ||||
| 351 | -6.92, | ||||
| 352 | 35.715 | ||||
| 353 | ], | ||||
| 354 | "type": "Point" | ||||
| 355 | }, | ||||
| 356 | "text": "Espa\u00f1a", | 327 | "text": "Espa\u00f1a", | ||
| 357 | "uri": | 328 | "uri": | ||
| 358 | ttp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a" | 329 | ttp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a" | ||
| 359 | } | 330 | } | ||
| 360 | ], | 331 | ], | ||
| 361 | "spatial_resolution_in_meters": "", | 332 | "spatial_resolution_in_meters": "", | ||
| 362 | "spatial_uri": | 333 | "spatial_uri": | ||
| 363 | tp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a", | 334 | tp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a", | ||
| 364 | "state": "active", | 335 | "state": "active", | ||
| 365 | "study_variables": { | 336 | "study_variables": { | ||
| 366 | "es": "" | 337 | "es": "" | ||
| 367 | }, | 338 | }, | ||
| 368 | "tag_uri": [ | 339 | "tag_uri": [ | ||
| 369 | 340 | ||||
| 370 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | 341 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | ||
| 371 | ], | 342 | ], | ||
| 372 | "tags": [ | 343 | "tags": [ | ||
| 373 | { | 344 | { | ||
| 374 | "display_name": "accidentes-y-atropellos-de-fauna", | 345 | "display_name": "accidentes-y-atropellos-de-fauna", | ||
| 375 | "id": "629c6d17-b04f-404c-900a-8c31fae0ecc4", | 346 | "id": "629c6d17-b04f-404c-900a-8c31fae0ecc4", | ||
| 376 | "name": "accidentes-y-atropellos-de-fauna", | 347 | "name": "accidentes-y-atropellos-de-fauna", | ||
| 377 | "state": "active", | 348 | "state": "active", | ||
| 378 | "vocabulary_id": null | 349 | "vocabulary_id": null | ||
| 379 | }, | 350 | }, | ||
| 380 | { | 351 | { | ||
| 381 | "display_name": "fragmentacion", | 352 | "display_name": "fragmentacion", | ||
| 382 | "id": "627f9c0a-a199-4c69-b563-0c8d626e3194", | 353 | "id": "627f9c0a-a199-4c69-b563-0c8d626e3194", | ||
| 383 | "name": "fragmentacion", | 354 | "name": "fragmentacion", | ||
| 384 | "state": "active", | 355 | "state": "active", | ||
| 385 | "vocabulary_id": null | 356 | "vocabulary_id": null | ||
| 386 | } | 357 | } | ||
| 387 | ], | 358 | ], | ||
| 388 | "thematic_area": [ | 359 | "thematic_area": [ | ||
| 389 | "especies_silvestres" | 360 | "especies_silvestres" | ||
| 390 | ], | 361 | ], | ||
| 391 | "theme_es": [ | 362 | "theme_es": [ | ||
| 392 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | 363 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | ||
| 393 | ], | 364 | ], | ||
| 394 | "title": "Roadkills in Europe: areas of high risk of collision and | 365 | "title": "Roadkills in Europe: areas of high risk of collision and | ||
| 395 | critical for populations persistence.", | 366 | critical for populations persistence.", | ||
| 396 | "title_translated": { | 367 | "title_translated": { | ||
| 397 | "en": "", | 368 | "en": "", | ||
| 398 | "es": "Roadkills in Europe: areas of high risk of collision and | 369 | "es": "Roadkills in Europe: areas of high risk of collision and | ||
| 399 | critical for populations persistence." | 370 | critical for populations persistence." | ||
| 400 | }, | 371 | }, | ||
| 401 | "topic": | 372 | "topic": | ||
| 402 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | 373 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | ||
| 403 | "type": "dataset", | 374 | "type": "dataset", | ||
| 404 | "url": | 375 | "url": | ||
| 405 | //iepnb.es:443/catalogo/dataset/d9d1665f-9f1a-57d4-9695-10fb3ae34592", | 376 | //iepnb.es:443/catalogo/dataset/d9d1665f-9f1a-57d4-9695-10fb3ae34592", | ||
| 406 | "version": "", | 377 | "version": "", | ||
| 407 | "version_notes": { | 378 | "version_notes": { | ||
| 408 | "en": "", | 379 | "en": "", | ||
| 409 | "es": "" | 380 | "es": "" | ||
| 410 | } | 381 | } | ||
| 411 | } | 382 | } |