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| 4 | "alternate_identifier": "DOI: 10.3161/000164512X653917", | 4 | "alternate_identifier": "DOI: 10.3161/000164512X653917", | ||
| 5 | "author": "Silva, C.C., Louren\u00e7o, R., Godinho, S., Gomes, E., | 5 | "author": "Silva, C.C., Louren\u00e7o, R., Godinho, S., Gomes, E., | ||
| 6 | Sabino-Marques, H., Medinas, D., Neves, V., Silva, C., Raba\u00e7a, | 6 | Sabino-Marques, H., Medinas, D., Neves, V., Silva, C., Raba\u00e7a, | ||
| 7 | J.E. y Mira, A.", | 7 | J.E. y Mira, A.", | ||
| 8 | "author_name": "Silva, C.C., Louren\u00e7o, R., Godinho, S., Gomes, | 8 | "author_name": "Silva, C.C., Louren\u00e7o, R., Godinho, S., Gomes, | ||
| 9 | E., Sabino-Marques, H., Medinas, D., Neves, V., Silva, C., | 9 | E., Sabino-Marques, H., Medinas, D., Neves, V., Silva, C., | ||
| 10 | Raba\u00e7a, J.E. y Mira, A.", | 10 | Raba\u00e7a, J.E. y Mira, A.", | ||
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| 38 | "name": "Silva, C.C., Louren\u00e7o, R., Godinho, S., Gomes, E., | 38 | "name": "Silva, C.C., Louren\u00e7o, R., Godinho, S., Gomes, E., | ||
| 39 | Sabino-Marques, H., Medinas, D., Neves, V., Silva, C., Raba\u00e7a, | 39 | Sabino-Marques, H., Medinas, D., Neves, V., Silva, C., Raba\u00e7a, | ||
| 40 | J.E. y Mira, A." | 40 | J.E. y Mira, A." | ||
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| 63 | "Acta Ornithologica. Vol. 47", | 63 | "Acta Ornithologica. Vol. 47", | ||
| 64 | "Num. 1", | 64 | "Num. 1", | ||
| 65 | "pags. 47-54" | 65 | "pags. 47-54" | ||
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| 85 | "notes": "The increasing road networks threaten ecosystems by direct | 85 | "notes": "The increasing road networks threaten ecosystems by direct | ||
| 86 | effects such as increased mortality due to collision with vehicles and | 86 | effects such as increased mortality due to collision with vehicles and | ||
| 87 | by various indirect effects leading to road avoidance. We censused | 87 | by various indirect effects leading to road avoidance. We censused | ||
| 88 | Tawny Owls Strix aluco and Little Owls Athene noctua in 2005, 2007 and | 88 | Tawny Owls Strix aluco and Little Owls Athene noctua in 2005, 2007 and | ||
| 89 | 2009 in a rural landscape in Southern Portugal in order to study the | 89 | 2009 in a rural landscape in Southern Portugal in order to study the | ||
| 90 | effects of roads and habitat characteristics on Tawny Owl density and | 90 | effects of roads and habitat characteristics on Tawny Owl density and | ||
| 91 | Little Owl presence. The presence of both owl species in the 70 census | 91 | Little Owl presence. The presence of both owl species in the 70 census | ||
| 92 | locations was coherent among years. Our results showed that Tawny Owl | 92 | locations was coherent among years. Our results showed that Tawny Owl | ||
| 93 | density near major roads was lower, with the negative effects | 93 | density near major roads was lower, with the negative effects | ||
| 94 | extending possibly up to 2 km. The probability of Little Owl presence | 94 | extending possibly up to 2 km. The probability of Little Owl presence | ||
| 95 | was also negatively affected by the proximity to major roads. The | 95 | was also negatively affected by the proximity to major roads. The | ||
| 96 | negative effects of roads were significant even considering habitat | 96 | negative effects of roads were significant even considering habitat | ||
| 97 | preferences and spatial autocorrelation, which had the most marked | 97 | preferences and spatial autocorrelation, which had the most marked | ||
| 98 | effect on the density or presence of both owls. The reduced occupancy | 98 | effect on the density or presence of both owls. The reduced occupancy | ||
| 99 | by Tawny Owls and Little Owls of habitats near major roads may be | 99 | by Tawny Owls and Little Owls of habitats near major roads may be | ||
| 100 | caused by several factors, including increased mortality, disturbance | 100 | caused by several factors, including increased mortality, disturbance | ||
| 101 | caused by high traffic density, and increased fragmentation. Traffic | 101 | caused by high traffic density, and increased fragmentation. Traffic | ||
| 102 | noise in particular may affect intra-specific communication and | 102 | noise in particular may affect intra-specific communication and | ||
| 103 | hunting efficiency. Consequently, habitat near roads may represent | 103 | hunting efficiency. Consequently, habitat near roads may represent | ||
| 104 | lower-quality territories for owls.", | 104 | lower-quality territories for owls.", | ||
| 105 | "notes_translated": { | 105 | "notes_translated": { | ||
| 106 | "en": "The increasing road networks threaten ecosystems by direct | 106 | "en": "The increasing road networks threaten ecosystems by direct | ||
| 107 | effects such as increased mortality due to collision with vehicles and | 107 | effects such as increased mortality due to collision with vehicles and | ||
| 108 | by various indirect effects leading to road avoidance. We censused | 108 | by various indirect effects leading to road avoidance. We censused | ||
| 109 | Tawny Owls\u00a0Strix aluco\u00a0and Little Owls\u00a0Athene | 109 | Tawny Owls\u00a0Strix aluco\u00a0and Little Owls\u00a0Athene | ||
| 110 | noctua\u00a0in 2005, 2007 and 2009 in a rural landscape in Southern | 110 | noctua\u00a0in 2005, 2007 and 2009 in a rural landscape in Southern | ||
| 111 | Portugal in order to study the effects of roads and habitat | 111 | Portugal in order to study the effects of roads and habitat | ||
| 112 | characteristics on Tawny Owl density and Little Owl presence. The | 112 | characteristics on Tawny Owl density and Little Owl presence. The | ||
| 113 | presence of both owl species in the 70 census locations was coherent | 113 | presence of both owl species in the 70 census locations was coherent | ||
| 114 | among years. Our results showed that Tawny Owl density near major | 114 | among years. Our results showed that Tawny Owl density near major | ||
| 115 | roads was lower, with the negative effects extending possibly up to 2 | 115 | roads was lower, with the negative effects extending possibly up to 2 | ||
| 116 | km. The probability of Little Owl presence was also negatively | 116 | km. The probability of Little Owl presence was also negatively | ||
| 117 | affected by the proximity to major roads. The negative effects of | 117 | affected by the proximity to major roads. The negative effects of | ||
| 118 | roads were significant even considering habitat preferences and | 118 | roads were significant even considering habitat preferences and | ||
| 119 | spatial autocorrelation, which had the most marked effect on the | 119 | spatial autocorrelation, which had the most marked effect on the | ||
| 120 | density or presence of both owls. The reduced occupancy by Tawny Owls | 120 | density or presence of both owls. The reduced occupancy by Tawny Owls | ||
| 121 | and Little Owls of habitats near major roads may be caused by several | 121 | and Little Owls of habitats near major roads may be caused by several | ||
| 122 | factors, including increased mortality, disturbance caused by high | 122 | factors, including increased mortality, disturbance caused by high | ||
| 123 | traffic density, and increased fragmentation. Traffic noise in | 123 | traffic density, and increased fragmentation. Traffic noise in | ||
| 124 | particular may affect intra-specific communication and hunting | 124 | particular may affect intra-specific communication and hunting | ||
| 125 | efficiency. Consequently, habitat near roads may represent | 125 | efficiency. Consequently, habitat near roads may represent | ||
| 126 | lower-quality territories for owls.", | 126 | lower-quality territories for owls.", | ||
| 127 | "es": "The increasing road networks threaten ecosystems by direct | 127 | "es": "The increasing road networks threaten ecosystems by direct | ||
| 128 | effects such as increased mortality due to collision with vehicles and | 128 | effects such as increased mortality due to collision with vehicles and | ||
| 129 | by various indirect effects leading to road avoidance. We censused | 129 | by various indirect effects leading to road avoidance. We censused | ||
| 130 | Tawny Owls Strix aluco and Little Owls Athene noctua in 2005, 2007 and | 130 | Tawny Owls Strix aluco and Little Owls Athene noctua in 2005, 2007 and | ||
| 131 | 2009 in a rural landscape in Southern Portugal in order to study the | 131 | 2009 in a rural landscape in Southern Portugal in order to study the | ||
| 132 | effects of roads and habitat characteristics on Tawny Owl density and | 132 | effects of roads and habitat characteristics on Tawny Owl density and | ||
| 133 | Little Owl presence. The presence of both owl species in the 70 census | 133 | Little Owl presence. The presence of both owl species in the 70 census | ||
| 134 | locations was coherent among years. Our results showed that Tawny Owl | 134 | locations was coherent among years. Our results showed that Tawny Owl | ||
| 135 | density near major roads was lower, with the negative effects | 135 | density near major roads was lower, with the negative effects | ||
| 136 | extending possibly up to 2 km. The probability of Little Owl presence | 136 | extending possibly up to 2 km. The probability of Little Owl presence | ||
| 137 | was also negatively affected by the proximity to major roads. The | 137 | was also negatively affected by the proximity to major roads. The | ||
| 138 | negative effects of roads were significant even considering habitat | 138 | negative effects of roads were significant even considering habitat | ||
| 139 | preferences and spatial autocorrelation, which had the most marked | 139 | preferences and spatial autocorrelation, which had the most marked | ||
| 140 | effect on the density or presence of both owls. The reduced occupancy | 140 | effect on the density or presence of both owls. The reduced occupancy | ||
| 141 | by Tawny Owls and Little Owls of habitats near major roads may be | 141 | by Tawny Owls and Little Owls of habitats near major roads may be | ||
| 142 | caused by several factors, including increased mortality, disturbance | 142 | caused by several factors, including increased mortality, disturbance | ||
| 143 | caused by high traffic density, and increased fragmentation. Traffic | 143 | caused by high traffic density, and increased fragmentation. Traffic | ||
| 144 | noise in particular may affect intra-specific communication and | 144 | noise in particular may affect intra-specific communication and | ||
| 145 | hunting efficiency. Consequently, habitat near roads may represent | 145 | hunting efficiency. Consequently, habitat near roads may represent | ||
| 146 | lower-quality territories for owls." | 146 | lower-quality territories for owls." | ||
| 147 | }, | 147 | }, | ||
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| 279 | "id": "627f9c0a-a199-4c69-b563-0c8d626e3194", | 279 | "id": "627f9c0a-a199-4c69-b563-0c8d626e3194", | ||
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| 292 | aluco and the little owl Athene noctua populations.", | 292 | aluco and the little owl Athene noctua populations.", | ||
| 293 | "title_translated": { | 293 | "title_translated": { | ||
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| 296 | aluco and the little owl Athene noctua populations." | 296 | aluco and the little owl Athene noctua populations." | ||
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