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a2026-06-25
en Major roads have a negative impact on the tawny owl Strix aluco and the little owl Athene noctua populations. -
Modificado el valor del campo
modified
del recurso Acceso al recurso a2026-06-25
(anteriormente2026-06-23
) en Major roads have a negative impact on the tawny owl Strix aluco and the little owl Athene noctua populations.
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| 85 | "notes": "The increasing road networks threaten ecosystems by direct | 99 | "notes": "The increasing road networks threaten ecosystems by direct | ||
| 86 | effects such as increased mortality due to collision with vehicles and | 100 | effects such as increased mortality due to collision with vehicles and | ||
| 87 | by various indirect effects leading to road avoidance. We censused | 101 | by various indirect effects leading to road avoidance. We censused | ||
| 88 | Tawny Owls Strix aluco and Little Owls Athene noctua in 2005, 2007 and | 102 | 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 | 103 | 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 | 104 | 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 | 105 | 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 | 106 | locations was coherent among years. Our results showed that Tawny Owl | ||
| 93 | density near major roads was lower, with the negative effects | 107 | density near major roads was lower, with the negative effects | ||
| 94 | extending possibly up to 2 km. The probability of Little Owl presence | 108 | extending possibly up to 2 km. The probability of Little Owl presence | ||
| 95 | was also negatively affected by the proximity to major roads. The | 109 | was also negatively affected by the proximity to major roads. The | ||
| 96 | negative effects of roads were significant even considering habitat | 110 | negative effects of roads were significant even considering habitat | ||
| 97 | preferences and spatial autocorrelation, which had the most marked | 111 | preferences and spatial autocorrelation, which had the most marked | ||
| 98 | effect on the density or presence of both owls. The reduced occupancy | 112 | 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 | 113 | by Tawny Owls and Little Owls of habitats near major roads may be | ||
| 100 | caused by several factors, including increased mortality, disturbance | 114 | caused by several factors, including increased mortality, disturbance | ||
| 101 | caused by high traffic density, and increased fragmentation. Traffic | 115 | caused by high traffic density, and increased fragmentation. Traffic | ||
| 102 | noise in particular may affect intra-specific communication and | 116 | noise in particular may affect intra-specific communication and | ||
| 103 | hunting efficiency. Consequently, habitat near roads may represent | 117 | hunting efficiency. Consequently, habitat near roads may represent | ||
| 104 | lower-quality territories for owls.", | 118 | lower-quality territories for owls.", | ||
| 105 | "notes_translated": { | 119 | "notes_translated": { | ||
| 106 | "en": "The increasing road networks threaten ecosystems by direct | 120 | "en": "The increasing road networks threaten ecosystems by direct | ||
| 107 | effects such as increased mortality due to collision with vehicles and | 121 | effects such as increased mortality due to collision with vehicles and | ||
| 108 | by various indirect effects leading to road avoidance. We censused | 122 | by various indirect effects leading to road avoidance. We censused | ||
| 109 | Tawny Owls\u00a0Strix aluco\u00a0and Little Owls\u00a0Athene | 123 | Tawny Owls\u00a0Strix aluco\u00a0and Little Owls\u00a0Athene | ||
| 110 | noctua\u00a0in 2005, 2007 and 2009 in a rural landscape in Southern | 124 | noctua\u00a0in 2005, 2007 and 2009 in a rural landscape in Southern | ||
| 111 | Portugal in order to study the effects of roads and habitat | 125 | Portugal in order to study the effects of roads and habitat | ||
| 112 | characteristics on Tawny Owl density and Little Owl presence. The | 126 | characteristics on Tawny Owl density and Little Owl presence. The | ||
| 113 | presence of both owl species in the 70 census locations was coherent | 127 | presence of both owl species in the 70 census locations was coherent | ||
| 114 | among years. Our results showed that Tawny Owl density near major | 128 | among years. Our results showed that Tawny Owl density near major | ||
| 115 | roads was lower, with the negative effects extending possibly up to 2 | 129 | roads was lower, with the negative effects extending possibly up to 2 | ||
| 116 | km. The probability of Little Owl presence was also negatively | 130 | km. The probability of Little Owl presence was also negatively | ||
| 117 | affected by the proximity to major roads. The negative effects of | 131 | affected by the proximity to major roads. The negative effects of | ||
| 118 | roads were significant even considering habitat preferences and | 132 | roads were significant even considering habitat preferences and | ||
| 119 | spatial autocorrelation, which had the most marked effect on the | 133 | spatial autocorrelation, which had the most marked effect on the | ||
| 120 | density or presence of both owls. The reduced occupancy by Tawny Owls | 134 | 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 | 135 | and Little Owls of habitats near major roads may be caused by several | ||
| 122 | factors, including increased mortality, disturbance caused by high | 136 | factors, including increased mortality, disturbance caused by high | ||
| 123 | traffic density, and increased fragmentation. Traffic noise in | 137 | traffic density, and increased fragmentation. Traffic noise in | ||
| 124 | particular may affect intra-specific communication and hunting | 138 | particular may affect intra-specific communication and hunting | ||
| 125 | efficiency. Consequently, habitat near roads may represent | 139 | efficiency. Consequently, habitat near roads may represent | ||
| 126 | lower-quality territories for owls.", | 140 | lower-quality territories for owls.", | ||
| 127 | "es": "The increasing road networks threaten ecosystems by direct | 141 | "es": "The increasing road networks threaten ecosystems by direct | ||
| 128 | effects such as increased mortality due to collision with vehicles and | 142 | effects such as increased mortality due to collision with vehicles and | ||
| 129 | by various indirect effects leading to road avoidance. We censused | 143 | by various indirect effects leading to road avoidance. We censused | ||
| 130 | Tawny Owls Strix aluco and Little Owls Athene noctua in 2005, 2007 and | 144 | 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 | 145 | 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 | 146 | 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 | 147 | 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 | 148 | locations was coherent among years. Our results showed that Tawny Owl | ||
| 135 | density near major roads was lower, with the negative effects | 149 | density near major roads was lower, with the negative effects | ||
| 136 | extending possibly up to 2 km. The probability of Little Owl presence | 150 | extending possibly up to 2 km. The probability of Little Owl presence | ||
| 137 | was also negatively affected by the proximity to major roads. The | 151 | was also negatively affected by the proximity to major roads. The | ||
| 138 | negative effects of roads were significant even considering habitat | 152 | negative effects of roads were significant even considering habitat | ||
| 139 | preferences and spatial autocorrelation, which had the most marked | 153 | preferences and spatial autocorrelation, which had the most marked | ||
| 140 | effect on the density or presence of both owls. The reduced occupancy | 154 | 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 | 155 | by Tawny Owls and Little Owls of habitats near major roads may be | ||
| 142 | caused by several factors, including increased mortality, disturbance | 156 | caused by several factors, including increased mortality, disturbance | ||
| 143 | caused by high traffic density, and increased fragmentation. Traffic | 157 | caused by high traffic density, and increased fragmentation. Traffic | ||
| 144 | noise in particular may affect intra-specific communication and | 158 | noise in particular may affect intra-specific communication and | ||
| 145 | hunting efficiency. Consequently, habitat near roads may represent | 159 | hunting efficiency. Consequently, habitat near roads may represent | ||
| 146 | lower-quality territories for owls." | 160 | lower-quality territories for owls." | ||
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