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a2026-06-25
en Soil development at the roadside: a case study of a novel ecosystem. -
Modificado el valor del campo
modified
del recurso Acceso al recurso a2026-06-25
(anteriormente2026-06-23
) en Soil development at the roadside: a case study of a novel ecosystem.
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| 82 | "notes": "Over the last few decades, road construction has increased | 96 | "notes": "Over the last few decades, road construction has increased | ||
| 83 | dramatically, and new surfaces have appeared in most landscapes. | 97 | dramatically, and new surfaces have appeared in most landscapes. | ||
| 84 | Standard roadside reclamation practices often fail, because vegetation | 98 | Standard roadside reclamation practices often fail, because vegetation | ||
| 85 | establishment appears to be limited by microsite availability. We | 99 | establishment appears to be limited by microsite availability. We | ||
| 86 | considered soil properties as a key factor driving vegetation | 100 | considered soil properties as a key factor driving vegetation | ||
| 87 | establishment on roadslopes over time. We address the following | 101 | establishment on roadslopes over time. We address the following | ||
| 88 | questions: (i) Are soil features conditioned by type of roadslope, | 102 | questions: (i) Are soil features conditioned by type of roadslope, | ||
| 89 | position thereupon or applied hydroseeding? (ii) Is there any evidence | 103 | position thereupon or applied hydroseeding? (ii) Is there any evidence | ||
| 90 | of soil development at the roadside four years after road | 104 | of soil development at the roadside four years after road | ||
| 91 | construction? (iii) Do mutual interactions exist between soil features | 105 | construction? (iii) Do mutual interactions exist between soil features | ||
| 92 | and vegetation cover? We designed an experimental set\u2010up on a | 106 | and vegetation cover? We designed an experimental set\u2010up on a | ||
| 93 | highway in Central Spain (Madrid). We selected 15 roadslopes (nine | 107 | highway in Central Spain (Madrid). We selected 15 roadslopes (nine | ||
| 94 | roadcuts and six embankments) with three hydroseeding treatments | 108 | roadcuts and six embankments) with three hydroseeding treatments | ||
| 95 | (commercial, alternative and untreated). Four years after the road | 109 | (commercial, alternative and untreated). Four years after the road | ||
| 96 | construction, we considered three roadslope positions (top, middle and | 110 | construction, we considered three roadslope positions (top, middle and | ||
| 97 | bottom) to take into account the geomorphological gradient. We | 111 | bottom) to take into account the geomorphological gradient. We | ||
| 98 | monitored soil features and vegetation cover over 4 years after the | 112 | monitored soil features and vegetation cover over 4 years after the | ||
| 99 | road construction. Soil chemical differences were found between | 113 | road construction. Soil chemical differences were found between | ||
| 100 | roadslope types, mainly resulted from topsoil spreading on embankments | 114 | roadslope types, mainly resulted from topsoil spreading on embankments | ||
| 101 | and the weathering of the newly exposed materials on roadcuts. Applied | 115 | and the weathering of the newly exposed materials on roadcuts. Applied | ||
| 102 | amendments do not affect soil fertility or vegetation cover. In the | 116 | amendments do not affect soil fertility or vegetation cover. In the | ||
| 103 | course of time, vegetation establishment and geomorphological | 117 | course of time, vegetation establishment and geomorphological | ||
| 104 | gradients operate differentially on roadcuts and embankments. | 118 | gradients operate differentially on roadcuts and embankments. | ||
| 105 | Accordingly, cycling back of organic compounds or geomorphological | 119 | Accordingly, cycling back of organic compounds or geomorphological | ||
| 106 | processes differs between roadslopes types. Restoration efforts should | 120 | processes differs between roadslopes types. Restoration efforts should | ||
| 107 | be directed to guarantee key ecological processes and support soil | 121 | be directed to guarantee key ecological processes and support soil | ||
| 108 | formation.", | 122 | formation.", | ||
| 109 | "notes_translated": { | 123 | "notes_translated": { | ||
| 110 | "en": "Over the last few decades, road construction has increased | 124 | "en": "Over the last few decades, road construction has increased | ||
| 111 | dramatically, and new surfaces have appeared in most landscapes. | 125 | dramatically, and new surfaces have appeared in most landscapes. | ||
| 112 | Standard roadside reclamation practices often fail, because vegetation | 126 | Standard roadside reclamation practices often fail, because vegetation | ||
| 113 | establishment appears to be limited by microsite availability. We | 127 | establishment appears to be limited by microsite availability. We | ||
| 114 | considered soil properties as a key factor driving vegetation | 128 | considered soil properties as a key factor driving vegetation | ||
| 115 | establishment on roadslopes over time. We address the following | 129 | establishment on roadslopes over time. We address the following | ||
| 116 | questions: (i) Are soil features conditioned by type of roadslope, | 130 | questions: (i) Are soil features conditioned by type of roadslope, | ||
| 117 | position thereupon or applied hydroseeding? (ii) Is there any evidence | 131 | position thereupon or applied hydroseeding? (ii) Is there any evidence | ||
| 118 | of soil development at the roadside four years after road | 132 | of soil development at the roadside four years after road | ||
| 119 | construction? (iii) Do mutual interactions exist between soil features | 133 | construction? (iii) Do mutual interactions exist between soil features | ||
| 120 | and vegetation cover? We designed an experimental set\u2010up on a | 134 | and vegetation cover? We designed an experimental set\u2010up on a | ||
| 121 | highway in Central Spain (Madrid). We selected 15 roadslopes (nine | 135 | highway in Central Spain (Madrid). We selected 15 roadslopes (nine | ||
| 122 | roadcuts and six embankments) with three hydroseeding treatments | 136 | roadcuts and six embankments) with three hydroseeding treatments | ||
| 123 | (commercial, alternative and untreated). Four years after the road | 137 | (commercial, alternative and untreated). Four years after the road | ||
| 124 | construction, we considered three roadslope positions (top, middle and | 138 | construction, we considered three roadslope positions (top, middle and | ||
| 125 | bottom) to take into account the geomorphological gradient. We | 139 | bottom) to take into account the geomorphological gradient. We | ||
| 126 | monitored soil features and vegetation cover over 4\u2009years after | 140 | monitored soil features and vegetation cover over 4\u2009years after | ||
| 127 | the road construction. Soil chemical differences were found between | 141 | the road construction. Soil chemical differences were found between | ||
| 128 | roadslope types, mainly resulted from topsoil spreading on embankments | 142 | roadslope types, mainly resulted from topsoil spreading on embankments | ||
| 129 | and the weathering of the newly exposed materials on roadcuts. Applied | 143 | and the weathering of the newly exposed materials on roadcuts. Applied | ||
| 130 | amendments do not affect soil fertility or vegetation cover. In the | 144 | amendments do not affect soil fertility or vegetation cover. In the | ||
| 131 | course of time, vegetation establishment and geomorphological | 145 | course of time, vegetation establishment and geomorphological | ||
| 132 | gradients operate differentially on roadcuts and embankments. | 146 | gradients operate differentially on roadcuts and embankments. | ||
| 133 | Accordingly, cycling back of organic compounds or geomorphological | 147 | Accordingly, cycling back of organic compounds or geomorphological | ||
| 134 | processes differs between roadslopes types. Restoration efforts should | 148 | processes differs between roadslopes types. Restoration efforts should | ||
| 135 | be directed to guarantee key ecological processes and support soil | 149 | be directed to guarantee key ecological processes and support soil | ||
| 136 | formation. Copyright \u00a9 2011 John Wiley & Sons, Ltd.", | 150 | formation. Copyright \u00a9 2011 John Wiley & Sons, Ltd.", | ||
| 137 | "es": "Over the last few decades, road construction has increased | 151 | "es": "Over the last few decades, road construction has increased | ||
| 138 | dramatically, and new surfaces have appeared in most landscapes. | 152 | dramatically, and new surfaces have appeared in most landscapes. | ||
| 139 | Standard roadside reclamation practices often fail, because vegetation | 153 | Standard roadside reclamation practices often fail, because vegetation | ||
| 140 | establishment appears to be limited by microsite availability. We | 154 | establishment appears to be limited by microsite availability. We | ||
| 141 | considered soil properties as a key factor driving vegetation | 155 | considered soil properties as a key factor driving vegetation | ||
| 142 | establishment on roadslopes over time. We address the following | 156 | establishment on roadslopes over time. We address the following | ||
| 143 | questions: (i) Are soil features conditioned by type of roadslope, | 157 | questions: (i) Are soil features conditioned by type of roadslope, | ||
| 144 | position thereupon or applied hydroseeding? (ii) Is there any evidence | 158 | position thereupon or applied hydroseeding? (ii) Is there any evidence | ||
| 145 | of soil development at the roadside four years after road | 159 | of soil development at the roadside four years after road | ||
| 146 | construction? (iii) Do mutual interactions exist between soil features | 160 | construction? (iii) Do mutual interactions exist between soil features | ||
| 147 | and vegetation cover? We designed an experimental set\u2010up on a | 161 | and vegetation cover? We designed an experimental set\u2010up on a | ||
| 148 | highway in Central Spain (Madrid). We selected 15 roadslopes (nine | 162 | highway in Central Spain (Madrid). We selected 15 roadslopes (nine | ||
| 149 | roadcuts and six embankments) with three hydroseeding treatments | 163 | roadcuts and six embankments) with three hydroseeding treatments | ||
| 150 | (commercial, alternative and untreated). Four years after the road | 164 | (commercial, alternative and untreated). Four years after the road | ||
| 151 | construction, we considered three roadslope positions (top, middle and | 165 | construction, we considered three roadslope positions (top, middle and | ||
| 152 | bottom) to take into account the geomorphological gradient. We | 166 | bottom) to take into account the geomorphological gradient. We | ||
| 153 | monitored soil features and vegetation cover over 4 years after the | 167 | monitored soil features and vegetation cover over 4 years after the | ||
| 154 | road construction. Soil chemical differences were found between | 168 | road construction. Soil chemical differences were found between | ||
| 155 | roadslope types, mainly resulted from topsoil spreading on embankments | 169 | roadslope types, mainly resulted from topsoil spreading on embankments | ||
| 156 | and the weathering of the newly exposed materials on roadcuts. Applied | 170 | and the weathering of the newly exposed materials on roadcuts. Applied | ||
| 157 | amendments do not affect soil fertility or vegetation cover. In the | 171 | amendments do not affect soil fertility or vegetation cover. In the | ||
| 158 | course of time, vegetation establishment and geomorphological | 172 | course of time, vegetation establishment and geomorphological | ||
| 159 | gradients operate differentially on roadcuts and embankments. | 173 | gradients operate differentially on roadcuts and embankments. | ||
| 160 | Accordingly, cycling back of organic compounds or geomorphological | 174 | Accordingly, cycling back of organic compounds or geomorphological | ||
| 161 | processes differs between roadslopes types. Restoration efforts should | 175 | processes differs between roadslopes types. Restoration efforts should | ||
| 162 | be directed to guarantee key ecological processes and support soil | 176 | be directed to guarantee key ecological processes and support soil | ||
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