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a2026-06-25
en Transportation planning and quiet natural areas preservation: aircraft overflights noise assessment in a National Park. -
Modificado el valor del campo
modified
del recurso Acceso al recurso a2026-06-25
(anteriormente2026-06-23
) en Transportation planning and quiet natural areas preservation: aircraft overflights noise assessment in a National Park.
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| 82 | "notes": "Global transportation growth causes several | 96 | "notes": "Global transportation growth causes several | ||
| 83 | disproportionate impacts on the environment as, for instance, noise | 97 | disproportionate impacts on the environment as, for instance, noise | ||
| 84 | pollution which is related to negative effects on human health but | 98 | pollution which is related to negative effects on human health but | ||
| 85 | also to quiet natural areas decline and biodiversity loss. Besides, | 99 | also to quiet natural areas decline and biodiversity loss. Besides, | ||
| 86 | sound is a component of ecosystems severely threatened by | 100 | sound is a component of ecosystems severely threatened by | ||
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| 89 | natural environments from a multiple innovative perspective. It | 103 | natural environments from a multiple innovative perspective. It | ||
| 90 | complementarily combines: noise modeling, field measurements, | 104 | complementarily combines: noise modeling, field measurements, | ||
| 91 | soundscape audibility, human perception and spatial pattern tools for | 105 | soundscape audibility, human perception and spatial pattern tools for | ||
| 92 | assessing the chronic growing outdoor noise pollution of ecosystems at | 106 | assessing the chronic growing outdoor noise pollution of ecosystems at | ||
| 93 | landscape scale. Firstly, noticeable soundscape degradation from | 107 | landscape scale. Firstly, noticeable soundscape degradation from | ||
| 94 | aircraft overflights has been found causing severe acoustic | 108 | aircraft overflights has been found causing severe acoustic | ||
| 95 | fragmentation and disruptions in the quietness of a national park in | 109 | fragmentation and disruptions in the quietness of a national park in | ||
| 96 | Spain (European Union). Air traffic caused sound pressure levels to | 110 | Spain (European Union). Air traffic caused sound pressure levels to | ||
| 97 | increase by approximately 8 decibels from natural ambient levels. | 111 | increase by approximately 8 decibels from natural ambient levels. | ||
| 98 | Secondly, spatial pattern tools together with noise mapping have been | 112 | Secondly, spatial pattern tools together with noise mapping have been | ||
| 99 | found to be useful in providing decision support for decisions-making | 113 | found to be useful in providing decision support for decisions-making | ||
| 100 | through anthropogenic noise impact assessment on the natural | 114 | through anthropogenic noise impact assessment on the natural | ||
| 101 | environment. Finally, public opinion did not perceive aircraft | 115 | environment. Finally, public opinion did not perceive aircraft | ||
| 102 | noise-disruption as being as relevant as that quantified by technical | 116 | noise-disruption as being as relevant as that quantified by technical | ||
| 103 | procedures. Although 82% of visitors agree that anthropogenic noise | 117 | procedures. Although 82% of visitors agree that anthropogenic noise | ||
| 104 | pollution may negatively impact on conservation.", | 118 | pollution may negatively impact on conservation.", | ||
| 105 | "notes_translated": { | 119 | "notes_translated": { | ||
| 106 | "en": "Global transportation growth causes several | 120 | "en": "Global transportation growth causes several | ||
| 107 | disproportionate impacts on the environment as, for instance, noise | 121 | disproportionate impacts on the environment as, for instance, noise | ||
| 108 | pollution which is related to negative effects on human health but | 122 | pollution which is related to negative effects on human health but | ||
| 109 | also to quiet natural areas decline and biodiversity loss. Besides, | 123 | also to quiet natural areas decline and biodiversity loss. Besides, | ||
| 110 | sound is a component of ecosystems severely threatened by | 124 | sound is a component of ecosystems severely threatened by | ||
| 111 | transportation noise disturbance which is related to negative effects | 125 | transportation noise disturbance which is related to negative effects | ||
| 112 | on ecosystem functions. This study deals with aircraft noise impact on | 126 | on ecosystem functions. This study deals with aircraft noise impact on | ||
| 113 | natural environments from a multiple innovative perspective. It | 127 | natural environments from a multiple innovative perspective. It | ||
| 114 | complementarily combines: noise modeling, field measurements, | 128 | complementarily combines: noise modeling, field measurements, | ||
| 115 | soundscape audibility, human perception and spatial pattern tools for | 129 | soundscape audibility, human perception and spatial pattern tools for | ||
| 116 | assessing the chronic growing outdoor noise pollution of ecosystems at | 130 | assessing the chronic growing outdoor noise pollution of ecosystems at | ||
| 117 | landscape scale. Firstly, noticeable soundscape degradation from | 131 | landscape scale. Firstly, noticeable soundscape degradation from | ||
| 118 | aircraft overflights has been found causing severe acoustic | 132 | aircraft overflights has been found causing severe acoustic | ||
| 119 | fragmentation and disruptions in the quietness of a national park in | 133 | fragmentation and disruptions in the quietness of a national park in | ||
| 120 | Spain (European Union). Air traffic caused sound pressure levels to | 134 | Spain (European Union). Air traffic caused sound pressure levels to | ||
| 121 | increase by approximately 8\u00a0decibels\u00a0from natural ambient | 135 | increase by approximately 8\u00a0decibels\u00a0from natural ambient | ||
| 122 | levels. Secondly, spatial pattern tools together with noise mapping | 136 | levels. Secondly, spatial pattern tools together with noise mapping | ||
| 123 | have been found to be useful in providing decision support for | 137 | have been found to be useful in providing decision support for | ||
| 124 | decisions-making through anthropogenic noise impact assessment on the | 138 | decisions-making through anthropogenic noise impact assessment on the | ||
| 125 | natural environment. Finally,\u00a0public opinion\u00a0did not | 139 | natural environment. Finally,\u00a0public opinion\u00a0did not | ||
| 126 | perceive aircraft noise-disruption as being as relevant as that | 140 | perceive aircraft noise-disruption as being as relevant as that | ||
| 127 | quantified by technical procedures. Although 82% of visitors agree | 141 | quantified by technical procedures. Although 82% of visitors agree | ||
| 128 | that anthropogenic noise pollution may negatively impact on | 142 | that anthropogenic noise pollution may negatively impact on | ||
| 129 | conservation.", | 143 | conservation.", | ||
| 130 | "es": "Global transportation growth causes several | 144 | "es": "Global transportation growth causes several | ||
| 131 | disproportionate impacts on the environment as, for instance, noise | 145 | disproportionate impacts on the environment as, for instance, noise | ||
| 132 | pollution which is related to negative effects on human health but | 146 | pollution which is related to negative effects on human health but | ||
| 133 | also to quiet natural areas decline and biodiversity loss. Besides, | 147 | also to quiet natural areas decline and biodiversity loss. Besides, | ||
| 134 | sound is a component of ecosystems severely threatened by | 148 | sound is a component of ecosystems severely threatened by | ||
| 135 | transportation noise disturbance which is related to negative effects | 149 | transportation noise disturbance which is related to negative effects | ||
| 136 | on ecosystem functions. This study deals with aircraft noise impact on | 150 | on ecosystem functions. This study deals with aircraft noise impact on | ||
| 137 | natural environments from a multiple innovative perspective. It | 151 | natural environments from a multiple innovative perspective. It | ||
| 138 | complementarily combines: noise modeling, field measurements, | 152 | complementarily combines: noise modeling, field measurements, | ||
| 139 | soundscape audibility, human perception and spatial pattern tools for | 153 | soundscape audibility, human perception and spatial pattern tools for | ||
| 140 | assessing the chronic growing outdoor noise pollution of ecosystems at | 154 | assessing the chronic growing outdoor noise pollution of ecosystems at | ||
| 141 | landscape scale. Firstly, noticeable soundscape degradation from | 155 | landscape scale. Firstly, noticeable soundscape degradation from | ||
| 142 | aircraft overflights has been found causing severe acoustic | 156 | aircraft overflights has been found causing severe acoustic | ||
| 143 | fragmentation and disruptions in the quietness of a national park in | 157 | fragmentation and disruptions in the quietness of a national park in | ||
| 144 | Spain (European Union). Air traffic caused sound pressure levels to | 158 | Spain (European Union). Air traffic caused sound pressure levels to | ||
| 145 | increase by approximately 8 decibels from natural ambient levels. | 159 | increase by approximately 8 decibels from natural ambient levels. | ||
| 146 | Secondly, spatial pattern tools together with noise mapping have been | 160 | Secondly, spatial pattern tools together with noise mapping have been | ||
| 147 | found to be useful in providing decision support for decisions-making | 161 | found to be useful in providing decision support for decisions-making | ||
| 148 | through anthropogenic noise impact assessment on the natural | 162 | through anthropogenic noise impact assessment on the natural | ||
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| 298 | preservation: aircraft overflights noise assessment in a National | 312 | preservation: aircraft overflights noise assessment in a National | ||
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