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En el instante 25 de junio de 2026, 12:31:28 UTC,
-
Modificado el valor del campo
modified
a2026-06-25
en Improvement of mitigation measures on an existing road crossing a wetland area proposed for the inclusion on Nature 2000 Network (Catalonia, NE Spain). -
Modificado el valor del campo
modified
del recurso Acceso al recurso a2026-06-25
(anteriormente2026-06-23
) en Improvement of mitigation measures on an existing road crossing a wetland area proposed for the inclusion on Nature 2000 Network (Catalonia, NE Spain).
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| 5 | "author": "Nav\u00e0s, F. y Rosell, C.", | 5 | "author": "Nav\u00e0s, F. y Rosell, C.", | ||
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| 31 | "created": "2025-05-23", | 31 | "created": "2025-05-23", | ||
| 32 | "creator": [ | 32 | "creator": [ | ||
| 33 | { | 33 | { | ||
| 34 | "name": "Nav\u00e0s, F. y Rosell, C." | 34 | "name": "Nav\u00e0s, F. y Rosell, C." | ||
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| 38 | "dataset_scope": "non_spatial_dataset", | 38 | "dataset_scope": "non_spatial_dataset", | ||
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| 41 | "featured": false, | 41 | "featured": false, | ||
| n | 42 | "groups": [], | n | 42 | "groups": [ |
| 43 | { | ||||
| 44 | "description": "La fragmentaci\u00f3n del h\u00e1bitat se define | ||||
| 45 | como el proceso durante el cual una gran extensi\u00f3n de | ||||
| 46 | h\u00e1bitat se transforma en una serie de parches m\u00e1s | ||||
| 47 | peque\u00f1os de menor superficie total aislados entre s\u00ed por una | ||||
| 48 | matriz de h\u00e1bitats distinta de la original", | ||||
| 49 | "display_name": "Fragmentaci\u00f3n del h\u00e1bitat", | ||||
| 50 | "id": "10439641-6830-4144-a3ab-117add931cd5", | ||||
| 51 | "image_display_url": | ||||
| 52 | e_2010_UE_Illustr.jpg/320px-Green_infrastructure_2010_UE_Illustr.jpg", | ||||
| 53 | "name": "fragmentacion-habitat", | ||||
| 54 | "title": "Fragmentaci\u00f3n del h\u00e1bitat" | ||||
| 55 | } | ||||
| 56 | ], | ||||
| 43 | "hvd": "non_hvd", | 57 | "hvd": "non_hvd", | ||
| 44 | "id": "abee74a6-031c-561d-8683-1e93f148c4c0", | 58 | "id": "abee74a6-031c-561d-8683-1e93f148c4c0", | ||
| 45 | "identifier": "abee74a6-031c-561d-8683-1e93f148c4c0", | 59 | "identifier": "abee74a6-031c-561d-8683-1e93f148c4c0", | ||
| 46 | "inspire_id": "", | 60 | "inspire_id": "", | ||
| 47 | "isopen": true, | 61 | "isopen": true, | ||
| 48 | "language": | 62 | "language": | ||
| 49 | "http://publications.europa.eu/resource/authority/language/SPA", | 63 | "http://publications.europa.eu/resource/authority/language/SPA", | ||
| 50 | "license_id": "cc-by", | 64 | "license_id": "cc-by", | ||
| 51 | "license_title": "Creative Commons Attribution", | 65 | "license_title": "Creative Commons Attribution", | ||
| 52 | "license_url": "http://www.opendefinition.org/licenses/cc-by", | 66 | "license_url": "http://www.opendefinition.org/licenses/cc-by", | ||
| 53 | "lineage_process_steps": [], | 67 | "lineage_process_steps": [], | ||
| 54 | "lineage_source": [ | 68 | "lineage_source": [ | ||
| 55 | "Habitat Fragmentation due to Transport Infrastructure & | 69 | "Habitat Fragmentation due to Transport Infrastructure & | ||
| 56 | Presentation of COST action 341 products" | 70 | Presentation of COST action 341 products" | ||
| 57 | ], | 71 | ], | ||
| 58 | "maintainer": "", | 72 | "maintainer": "", | ||
| 59 | "maintainer_name": "", | 73 | "maintainer_name": "", | ||
| 60 | "metadata_created": "2026-06-23T14:51:00.400370", | 74 | "metadata_created": "2026-06-23T14:51:00.400370", | ||
| n | 61 | "metadata_modified": "2026-06-23T16:01:43.909535", | n | 75 | "metadata_modified": "2026-06-25T12:31:28.126539", |
| 62 | "metadata_profile": [ | 76 | "metadata_profile": [ | ||
| 63 | "https://www.w3.org/TR/vocab-dcat-3/" | 77 | "https://www.w3.org/TR/vocab-dcat-3/" | ||
| 64 | ], | 78 | ], | ||
| 65 | "miteco_data_population": { | 79 | "miteco_data_population": { | ||
| 66 | "es": "" | 80 | "es": "" | ||
| 67 | }, | 81 | }, | ||
| 68 | "miteco_data_territory": { | 82 | "miteco_data_territory": { | ||
| 69 | "es": "" | 83 | "es": "" | ||
| 70 | }, | 84 | }, | ||
| 71 | "miteco_dataset_type": | 85 | "miteco_dataset_type": | ||
| 72 | //publications.europa.eu/resource/authority/dataset-type/STATISTICAL", | 86 | //publications.europa.eu/resource/authority/dataset-type/STATISTICAL", | ||
| 73 | "miteco_geo_level": "1", | 87 | "miteco_geo_level": "1", | ||
| n | 74 | "modified": "2026-06-23", | n | 88 | "modified": "2026-06-25", |
| 75 | "name": "abee74a6-031c-561d-8683-1e93f148c4c0", | 89 | "name": "abee74a6-031c-561d-8683-1e93f148c4c0", | ||
| 76 | "notes": "The Aiguamolls de l\u2019Empord\u00e0 Natural Park is a | 90 | "notes": "The Aiguamolls de l\u2019Empord\u00e0 Natural Park is a | ||
| 77 | wetland area of Catalonia (north-eastern Spain) proposed for the | 91 | wetland area of Catalonia (north-eastern Spain) proposed for the | ||
| 78 | Nature 2000 Network as a Site of Community Importance. On year 2000, a | 92 | Nature 2000 Network as a Site of Community Importance. On year 2000, a | ||
| 79 | local road crossing this Natural Park (and a Natural Reserve), with | 93 | local road crossing this Natural Park (and a Natural Reserve), with | ||
| 80 | some 25.000 vehicles per day, was converted into a motorway. The | 94 | some 25.000 vehicles per day, was converted into a motorway. The | ||
| 81 | motorway was fenced and, for the first time in Catalonia, specific | 95 | motorway was fenced and, for the first time in Catalonia, specific | ||
| 82 | wildlife passages were built in order to minimize fauna impact, | 96 | wildlife passages were built in order to minimize fauna impact, | ||
| 83 | especially for amphibian, carnivores (polecat, Mustela putorius, and | 97 | especially for amphibian, carnivores (polecat, Mustela putorius, and | ||
| 84 | otter, Lutra lutra) and ungulates (wild boar, Sus scrofa, and fallow | 98 | otter, Lutra lutra) and ungulates (wild boar, Sus scrofa, and fallow | ||
| 85 | deer, Dama dama)\n During spring and autumn of 2001 a study was | 99 | deer, Dama dama)\n During spring and autumn of 2001 a study was | ||
| 86 | carried out, on the 2,2 km stretch crossing the Natural Park, to | 100 | carried out, on the 2,2 km stretch crossing the Natural Park, to | ||
| 87 | assess the effectiveness of fauna passages, to identify black spots of | 101 | assess the effectiveness of fauna passages, to identify black spots of | ||
| 88 | fauna casualties and to make some proposals to enhance the use of | 102 | fauna casualties and to make some proposals to enhance the use of | ||
| 89 | these structures by fauna and to improve other mitigation measures. 17 | 103 | these structures by fauna and to improve other mitigation measures. 17 | ||
| 90 | fauna passages and adapted drainages were checked for a week in each | 104 | fauna passages and adapted drainages were checked for a week in each | ||
| 91 | season by using a marble powder substrate to register animal tracks | 105 | season by using a marble powder substrate to register animal tracks | ||
| 92 | and infra-red photographic cameras. Identification of black spots was | 106 | and infra-red photographic cameras. Identification of black spots was | ||
| 93 | made by collecting all the vertebrate carcasses found on the road | 107 | made by collecting all the vertebrate carcasses found on the road | ||
| 94 | during one month each season.\n The fauna passages were intensively | 108 | during one month each season.\n The fauna passages were intensively | ||
| 95 | used by almost the whole terrestrial animal groups in the area. There | 109 | used by almost the whole terrestrial animal groups in the area. There | ||
| 96 | were identified 15 wildlife species, plus some birds that also cross | 110 | were identified 15 wildlife species, plus some birds that also cross | ||
| 97 | these structures. Polecat was identified in one structure (with a | 111 | these structures. Polecat was identified in one structure (with a | ||
| 98 | diameter of 0,8 m), otter in three adapted drains and wild boar in the | 112 | diameter of 0,8 m), otter in three adapted drains and wild boar in the | ||
| 99 | two wider structures (10 and 11 m width each one). Fallow deer | 113 | two wider structures (10 and 11 m width each one). Fallow deer | ||
| 100 | don\u2019t use these structures (probably due to height that it is 2 m | 114 | don\u2019t use these structures (probably due to height that it is 2 m | ||
| 101 | as a maximum).\n Over the road, there were found 117 carcasses of a | 115 | as a maximum).\n Over the road, there were found 117 carcasses of a | ||
| 102 | minimum of 29 vertebrate species. The most affected group were birds | 116 | minimum of 29 vertebrate species. The most affected group were birds | ||
| 103 | (53% of total mortality). Some of the species identified are | 117 | (53% of total mortality). Some of the species identified are | ||
| 104 | catalogued as species of Special Interest in Spain: tree frog (Hyla | 118 | catalogued as species of Special Interest in Spain: tree frog (Hyla | ||
| 105 | meridionalis), ladder snake (Elaphe scalaris), purple gallinule | 119 | meridionalis), ladder snake (Elaphe scalaris), purple gallinule | ||
| 106 | (Porphyrio porphyrio), Savi's warbler (Locustella luscinioides) or | 120 | (Porphyrio porphyrio), Savi's warbler (Locustella luscinioides) or | ||
| 107 | Great reed warbler (Acrocephalus arundinaceus). There were found also | 121 | Great reed warbler (Acrocephalus arundinaceus). There were found also | ||
| 108 | some birds that had died after collision with glass acoustic screens | 122 | some birds that had died after collision with glass acoustic screens | ||
| 109 | installed to reduce nuisance to nesting birds, despite the use of | 123 | installed to reduce nuisance to nesting birds, despite the use of | ||
| 110 | adhesive bird of prey silhouettes which, it was hoped, would frighten | 124 | adhesive bird of prey silhouettes which, it was hoped, would frighten | ||
| 111 | the birds away. This measure was proved to be completely | 125 | the birds away. This measure was proved to be completely | ||
| 112 | inefficient.\n Some of the proposals made to enhance use of passages | 126 | inefficient.\n Some of the proposals made to enhance use of passages | ||
| 113 | and to reduce fauna casualties include:\n - Installation of an opaque | 127 | and to reduce fauna casualties include:\n - Installation of an opaque | ||
| 114 | barrier, close to the perimeter fencing, to prevent amphibians and | 128 | barrier, close to the perimeter fencing, to prevent amphibians and | ||
| 115 | reptiles crossing over and to guide them to the passages.\n - | 129 | reptiles crossing over and to guide them to the passages.\n - | ||
| 116 | Lengthening the lateral platforms, that provide a dry zone in case of | 130 | Lengthening the lateral platforms, that provide a dry zone in case of | ||
| 117 | flooding, on four adapted drainages, that were not built on the | 131 | flooding, on four adapted drainages, that were not built on the | ||
| 118 | ancient structure when upgrading the road. Also it is proposed to | 132 | ancient structure when upgrading the road. Also it is proposed to | ||
| 119 | construct ramps that must facilitate the access of animals to these | 133 | construct ramps that must facilitate the access of animals to these | ||
| 120 | platforms.\n - Planting of vegetal screens to force birds to fly | 134 | platforms.\n - Planting of vegetal screens to force birds to fly | ||
| 121 | higher.\n - Adhesion of vertical strips on the transparent acoustic | 135 | higher.\n - Adhesion of vertical strips on the transparent acoustic | ||
| 122 | screens, to make they visible to birds and to avoid their collision.\n | 136 | screens, to make they visible to birds and to avoid their collision.\n | ||
| 123 | Assessment of applied measures effectiveness, when the road is already | 137 | Assessment of applied measures effectiveness, when the road is already | ||
| 124 | in use, is a fundamental element to improve future design of measures | 138 | in use, is a fundamental element to improve future design of measures | ||
| 125 | and also to correct detected deficiencies and to reduce the impact of | 139 | and also to correct detected deficiencies and to reduce the impact of | ||
| 126 | the road on the fauna.\n Palabras clave: Connectivity, Enhancement | 140 | the road on the fauna.\n Palabras clave: Connectivity, Enhancement | ||
| 127 | measure, Fauna, Fauna passage, Habitat fragmentation, Motorway, | 141 | measure, Fauna, Fauna passage, Habitat fragmentation, Motorway, | ||
| 128 | Wetland", | 142 | Wetland", | ||
| 129 | "notes_translated": { | 143 | "notes_translated": { | ||
| 130 | "en": "The Aiguamolls de l\u2019Empord\u00e0 Natural Park is a | 144 | "en": "The Aiguamolls de l\u2019Empord\u00e0 Natural Park is a | ||
| 131 | wetland area of Catalonia (north-eastern Spain) proposed for the | 145 | wetland area of Catalonia (north-eastern Spain) proposed for the | ||
| 132 | Nature 2000 Network as a Site of Community Importance. On year 2000, a | 146 | Nature 2000 Network as a Site of Community Importance. On year 2000, a | ||
| 133 | local road crossing this Natural Park (and a Natural Reserve), with | 147 | local road crossing this Natural Park (and a Natural Reserve), with | ||
| 134 | some 25.000 vehicles per day, was converted into a motorway. The | 148 | some 25.000 vehicles per day, was converted into a motorway. The | ||
| 135 | motorway was fenced and, for the first time in Catalonia, specific | 149 | motorway was fenced and, for the first time in Catalonia, specific | ||
| 136 | wildlife passages were built in order to minimize fauna impact, | 150 | wildlife passages were built in order to minimize fauna impact, | ||
| 137 | especially for amphibian, carnivores (polecat, Mustela putorius, and | 151 | especially for amphibian, carnivores (polecat, Mustela putorius, and | ||
| 138 | otter, Lutra lutra) and ungulates (wild boar, Sus scrofa, and fallow | 152 | otter, Lutra lutra) and ungulates (wild boar, Sus scrofa, and fallow | ||
| 139 | deer, Dama dama)\nDuring spring and autumn of 2001 a study was carried | 153 | deer, Dama dama)\nDuring spring and autumn of 2001 a study was carried | ||
| 140 | out, on the 2,2 km stretch crossing the Natural Park, to assess the | 154 | out, on the 2,2 km stretch crossing the Natural Park, to assess the | ||
| 141 | effectiveness of fauna passages, to identify black spots of fauna | 155 | effectiveness of fauna passages, to identify black spots of fauna | ||
| 142 | casualties and to make some proposals to enhance the use of these | 156 | casualties and to make some proposals to enhance the use of these | ||
| 143 | structures by fauna and to improve other mitigation measures. 17 fauna | 157 | structures by fauna and to improve other mitigation measures. 17 fauna | ||
| 144 | passages and adapted drainages were checked for a week in each season | 158 | passages and adapted drainages were checked for a week in each season | ||
| 145 | by using a marble powder substrate to register animal tracks and | 159 | by using a marble powder substrate to register animal tracks and | ||
| 146 | infra-red photographic cameras. Identification of black spots was made | 160 | infra-red photographic cameras. Identification of black spots was made | ||
| 147 | by collecting all the vertebrate carcasses found on the road during | 161 | by collecting all the vertebrate carcasses found on the road during | ||
| 148 | one month each season.\nThe fauna passages were intensively used by | 162 | one month each season.\nThe fauna passages were intensively used by | ||
| 149 | almost the whole terrestrial animal groups in the area. There were | 163 | almost the whole terrestrial animal groups in the area. There were | ||
| 150 | identified 15 wildlife species, plus some birds that also cross these | 164 | identified 15 wildlife species, plus some birds that also cross these | ||
| 151 | structures. Polecat was identified in one structure (with a diameter | 165 | structures. Polecat was identified in one structure (with a diameter | ||
| 152 | of 0,8 m), otter in three adapted drains and wild boar in the two | 166 | of 0,8 m), otter in three adapted drains and wild boar in the two | ||
| 153 | wider structures (10 and 11 m width each one). Fallow deer don\u2019t | 167 | wider structures (10 and 11 m width each one). Fallow deer don\u2019t | ||
| 154 | use these structures (probably due to height that it is 2 m as a | 168 | use these structures (probably due to height that it is 2 m as a | ||
| 155 | maximum).\nOver the road, there were found 117 carcasses of a minimum | 169 | maximum).\nOver the road, there were found 117 carcasses of a minimum | ||
| 156 | of 29 vertebrate species. The most affected group were birds (53% of | 170 | of 29 vertebrate species. The most affected group were birds (53% of | ||
| 157 | total mortality). Some of the species identified are catalogued as | 171 | total mortality). Some of the species identified are catalogued as | ||
| 158 | species of Special Interest in Spain: tree frog (Hyla meridionalis), | 172 | species of Special Interest in Spain: tree frog (Hyla meridionalis), | ||
| 159 | ladder snake (Elaphe scalaris), purple gallinule (Porphyrio | 173 | ladder snake (Elaphe scalaris), purple gallinule (Porphyrio | ||
| 160 | porphyrio), Savi's warbler (Locustella luscinioides) or Great reed | 174 | porphyrio), Savi's warbler (Locustella luscinioides) or Great reed | ||
| 161 | warbler (Acrocephalus arundinaceus). There were found also some birds | 175 | warbler (Acrocephalus arundinaceus). There were found also some birds | ||
| 162 | that had died after collision with glass acoustic screens installed to | 176 | that had died after collision with glass acoustic screens installed to | ||
| 163 | reduce nuisance to nesting birds, despite the use of adhesive bird of | 177 | reduce nuisance to nesting birds, despite the use of adhesive bird of | ||
| 164 | prey silhouettes which, it was hoped, would frighten the birds away. | 178 | prey silhouettes which, it was hoped, would frighten the birds away. | ||
| 165 | This measure was proved to be completely inefficient.\nSome of the | 179 | This measure was proved to be completely inefficient.\nSome of the | ||
| 166 | proposals made to enhance use of passages and to reduce fauna | 180 | proposals made to enhance use of passages and to reduce fauna | ||
| 167 | casualties include:\n- Installation of an opaque barrier, close to the | 181 | casualties include:\n- Installation of an opaque barrier, close to the | ||
| 168 | perimeter fencing, to prevent amphibians and reptiles crossing over | 182 | perimeter fencing, to prevent amphibians and reptiles crossing over | ||
| 169 | and to guide them to the passages.\n- Lengthening the lateral | 183 | and to guide them to the passages.\n- Lengthening the lateral | ||
| 170 | platforms, that provide a dry zone in case of flooding, on four | 184 | platforms, that provide a dry zone in case of flooding, on four | ||
| 171 | adapted drainages, that were not built on the ancient structure when | 185 | adapted drainages, that were not built on the ancient structure when | ||
| 172 | upgrading the road. Also it is proposed to construct ramps that must | 186 | upgrading the road. Also it is proposed to construct ramps that must | ||
| 173 | facilitate the access of animals to these platforms.\n- Planting of | 187 | facilitate the access of animals to these platforms.\n- Planting of | ||
| 174 | vegetal screens to force birds to fly higher.\n- Adhesion of vertical | 188 | vegetal screens to force birds to fly higher.\n- Adhesion of vertical | ||
| 175 | strips on the transparent acoustic screens, to make they visible to | 189 | strips on the transparent acoustic screens, to make they visible to | ||
| 176 | birds and to avoid their collision.\nAssessment of applied measures | 190 | birds and to avoid their collision.\nAssessment of applied measures | ||
| 177 | effectiveness, when the road is already in use, is a fundamental | 191 | effectiveness, when the road is already in use, is a fundamental | ||
| 178 | element to improve future design of measures and also to correct | 192 | element to improve future design of measures and also to correct | ||
| 179 | detected deficiencies and to reduce the impact of the road on the | 193 | detected deficiencies and to reduce the impact of the road on the | ||
| 180 | fauna.", | 194 | fauna.", | ||
| 181 | "es": "The Aiguamolls de l\u2019Empord\u00e0 Natural Park is a | 195 | "es": "The Aiguamolls de l\u2019Empord\u00e0 Natural Park is a | ||
| 182 | wetland area of Catalonia (north-eastern Spain) proposed for the | 196 | wetland area of Catalonia (north-eastern Spain) proposed for the | ||
| 183 | Nature 2000 Network as a Site of Community Importance. On year 2000, a | 197 | Nature 2000 Network as a Site of Community Importance. On year 2000, a | ||
| 184 | local road crossing this Natural Park (and a Natural Reserve), with | 198 | local road crossing this Natural Park (and a Natural Reserve), with | ||
| 185 | some 25.000 vehicles per day, was converted into a motorway. The | 199 | some 25.000 vehicles per day, was converted into a motorway. The | ||
| 186 | motorway was fenced and, for the first time in Catalonia, specific | 200 | motorway was fenced and, for the first time in Catalonia, specific | ||
| 187 | wildlife passages were built in order to minimize fauna impact, | 201 | wildlife passages were built in order to minimize fauna impact, | ||
| 188 | especially for amphibian, carnivores (polecat, Mustela putorius, and | 202 | especially for amphibian, carnivores (polecat, Mustela putorius, and | ||
| 189 | otter, Lutra lutra) and ungulates (wild boar, Sus scrofa, and fallow | 203 | otter, Lutra lutra) and ungulates (wild boar, Sus scrofa, and fallow | ||
| 190 | deer, Dama dama)\n During spring and autumn of 2001 a study was | 204 | deer, Dama dama)\n During spring and autumn of 2001 a study was | ||
| 191 | carried out, on the 2,2 km stretch crossing the Natural Park, to | 205 | carried out, on the 2,2 km stretch crossing the Natural Park, to | ||
| 192 | assess the effectiveness of fauna passages, to identify black spots of | 206 | assess the effectiveness of fauna passages, to identify black spots of | ||
| 193 | fauna casualties and to make some proposals to enhance the use of | 207 | fauna casualties and to make some proposals to enhance the use of | ||
| 194 | these structures by fauna and to improve other mitigation measures. 17 | 208 | these structures by fauna and to improve other mitigation measures. 17 | ||
| 195 | fauna passages and adapted drainages were checked for a week in each | 209 | fauna passages and adapted drainages were checked for a week in each | ||
| 196 | season by using a marble powder substrate to register animal tracks | 210 | season by using a marble powder substrate to register animal tracks | ||
| 197 | and infra-red photographic cameras. Identification of black spots was | 211 | and infra-red photographic cameras. Identification of black spots was | ||
| 198 | made by collecting all the vertebrate carcasses found on the road | 212 | made by collecting all the vertebrate carcasses found on the road | ||
| 199 | during one month each season.\n The fauna passages were intensively | 213 | during one month each season.\n The fauna passages were intensively | ||
| 200 | used by almost the whole terrestrial animal groups in the area. There | 214 | used by almost the whole terrestrial animal groups in the area. There | ||
| 201 | were identified 15 wildlife species, plus some birds that also cross | 215 | were identified 15 wildlife species, plus some birds that also cross | ||
| 202 | these structures. Polecat was identified in one structure (with a | 216 | these structures. Polecat was identified in one structure (with a | ||
| 203 | diameter of 0,8 m), otter in three adapted drains and wild boar in the | 217 | diameter of 0,8 m), otter in three adapted drains and wild boar in the | ||
| 204 | two wider structures (10 and 11 m width each one). Fallow deer | 218 | two wider structures (10 and 11 m width each one). Fallow deer | ||
| 205 | don\u2019t use these structures (probably due to height that it is 2 m | 219 | don\u2019t use these structures (probably due to height that it is 2 m | ||
| 206 | as a maximum).\n Over the road, there were found 117 carcasses of a | 220 | as a maximum).\n Over the road, there were found 117 carcasses of a | ||
| 207 | minimum of 29 vertebrate species. The most affected group were birds | 221 | minimum of 29 vertebrate species. The most affected group were birds | ||
| 208 | (53% of total mortality). Some of the species identified are | 222 | (53% of total mortality). Some of the species identified are | ||
| 209 | catalogued as species of Special Interest in Spain: tree frog (Hyla | 223 | catalogued as species of Special Interest in Spain: tree frog (Hyla | ||
| 210 | meridionalis), ladder snake (Elaphe scalaris), purple gallinule | 224 | meridionalis), ladder snake (Elaphe scalaris), purple gallinule | ||
| 211 | (Porphyrio porphyrio), Savi's warbler (Locustella luscinioides) or | 225 | (Porphyrio porphyrio), Savi's warbler (Locustella luscinioides) or | ||
| 212 | Great reed warbler (Acrocephalus arundinaceus). There were found also | 226 | Great reed warbler (Acrocephalus arundinaceus). There were found also | ||
| 213 | some birds that had died after collision with glass acoustic screens | 227 | some birds that had died after collision with glass acoustic screens | ||
| 214 | installed to reduce nuisance to nesting birds, despite the use of | 228 | installed to reduce nuisance to nesting birds, despite the use of | ||
| 215 | adhesive bird of prey silhouettes which, it was hoped, would frighten | 229 | adhesive bird of prey silhouettes which, it was hoped, would frighten | ||
| 216 | the birds away. This measure was proved to be completely | 230 | the birds away. This measure was proved to be completely | ||
| 217 | inefficient.\n Some of the proposals made to enhance use of passages | 231 | inefficient.\n Some of the proposals made to enhance use of passages | ||
| 218 | and to reduce fauna casualties include:\n - Installation of an opaque | 232 | and to reduce fauna casualties include:\n - Installation of an opaque | ||
| 219 | barrier, close to the perimeter fencing, to prevent amphibians and | 233 | barrier, close to the perimeter fencing, to prevent amphibians and | ||
| 220 | reptiles crossing over and to guide them to the passages.\n - | 234 | reptiles crossing over and to guide them to the passages.\n - | ||
| 221 | Lengthening the lateral platforms, that provide a dry zone in case of | 235 | Lengthening the lateral platforms, that provide a dry zone in case of | ||
| 222 | flooding, on four adapted drainages, that were not built on the | 236 | flooding, on four adapted drainages, that were not built on the | ||
| 223 | ancient structure when upgrading the road. Also it is proposed to | 237 | ancient structure when upgrading the road. Also it is proposed to | ||
| 224 | construct ramps that must facilitate the access of animals to these | 238 | construct ramps that must facilitate the access of animals to these | ||
| 225 | platforms.\n - Planting of vegetal screens to force birds to fly | 239 | platforms.\n - Planting of vegetal screens to force birds to fly | ||
| 226 | higher.\n - Adhesion of vertical strips on the transparent acoustic | 240 | higher.\n - Adhesion of vertical strips on the transparent acoustic | ||
| 227 | screens, to make they visible to birds and to avoid their collision.\n | 241 | screens, to make they visible to birds and to avoid their collision.\n | ||
| 228 | Assessment of applied measures effectiveness, when the road is already | 242 | Assessment of applied measures effectiveness, when the road is already | ||
| 229 | in use, is a fundamental element to improve future design of measures | 243 | in use, is a fundamental element to improve future design of measures | ||
| 230 | and also to correct detected deficiencies and to reduce the impact of | 244 | and also to correct detected deficiencies and to reduce the impact of | ||
| 231 | the road on the fauna.\n Palabras clave: Connectivity, Enhancement | 245 | the road on the fauna.\n Palabras clave: Connectivity, Enhancement | ||
| 232 | measure, Fauna, Fauna passage, Habitat fragmentation, Motorway, | 246 | measure, Fauna, Fauna passage, Habitat fragmentation, Motorway, | ||
| 233 | Wetland" | 247 | Wetland" | ||
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