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en Changes in soils and vegetation in a Mediterranean coastal salt marsh impacted by human activities -
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modified
del recurso Distribución HTML a2026-06-25
(anteriormente2026-06-23
) en Changes in soils and vegetation in a Mediterranean coastal salt marsh impacted by human activities
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| 94 | "notes": "This paper reports changes in vegetation distribution and | 104 | "notes": "This paper reports changes in vegetation distribution and | ||
| 95 | species cover in relation to soil factors and hydrology in a semiarid | 105 | species cover in relation to soil factors and hydrology in a semiarid | ||
| 96 | Mediterranean salt marsh adjacent to the Mar Menor saline lagoon. | 106 | Mediterranean salt marsh adjacent to the Mar Menor saline lagoon. | ||
| 97 | Species cover, soil salinity, and the groundwater level were monitored | 107 | Species cover, soil salinity, and the groundwater level were monitored | ||
| 98 | between 1991 and 1993 and between 2002 and 2004, and total organic | 108 | between 1991 and 1993 and between 2002 and 2004, and total organic | ||
| 99 | carbon, total nitrogen, total phosphorus, nitrates, ammonium and | 109 | carbon, total nitrogen, total phosphorus, nitrates, ammonium and | ||
| 100 | exchangeable phosphorus were measured in the soils in both study | 110 | exchangeable phosphorus were measured in the soils in both study | ||
| 101 | periods. In addition, three soil profiles were described in August | 111 | periods. In addition, three soil profiles were described in August | ||
| 102 | 1992 and August 2004. The results indicate an elevation of the water | 112 | 1992 and August 2004. The results indicate an elevation of the water | ||
| 103 | table throughout the 13-year period, which was attributable to water | 113 | table throughout the 13-year period, which was attributable to water | ||
| 104 | flowing from areas with intensive agri culture. Flooding increased and | 114 | flowing from areas with intensive agri culture. Flooding increased and | ||
| 105 | soil salinity dropped in the most saline sites and increased in the | 115 | soil salinity dropped in the most saline sites and increased in the | ||
| 106 | least saline ones. The morphology of the soil profiles reflected the | 116 | least saline ones. The morphology of the soil profiles reflected the | ||
| 107 | increase in flooding periods, due to the appearance of a greyer matrix | 117 | increase in flooding periods, due to the appearance of a greyer matrix | ||
| 108 | in the deeper horizons and a more diffuse pattern of Fe mottles. | 118 | in the deeper horizons and a more diffuse pattern of Fe mottles. | ||
| 109 | Following these environmental changes, Sarcocornia fruticosa, | 119 | Following these environmental changes, Sarcocornia fruticosa, | ||
| 110 | Phragmites australis and Juncus maritimus strongly expanded at the | 120 | Phragmites australis and Juncus maritimus strongly expanded at the | ||
| 111 | wettest sites, which led to the disappearance of the original zonation | 121 | wettest sites, which led to the disappearance of the original zonation | ||
| 112 | pattern. The cover of Limonium delicatulum, in turn, decreased with | 122 | pattern. The cover of Limonium delicatulum, in turn, decreased with | ||
| 113 | the increase in moisture but increased following the increase in | 123 | the increase in moisture but increased following the increase in | ||
| 114 | salinity. Changes in soil nutrients were only very evident in the | 124 | salinity. Changes in soil nutrients were only very evident in the | ||
| 115 | sandy soils of the beach, probably due to the influence of organic | 125 | sandy soils of the beach, probably due to the influence of organic | ||
| 116 | debris deposited on the shoreline by the storms and due to the strong | 126 | debris deposited on the shoreline by the storms and due to the strong | ||
| 117 | increase in the colonisation of this habitat by perennial species. | 127 | increase in the colonisation of this habitat by perennial species. | ||
| 118 | According to the results obtained, control measures are needed in | 128 | According to the results obtained, control measures are needed in | ||
| 119 | order to preserve habitat diversity in this and other salt marshes of | 129 | order to preserve habitat diversity in this and other salt marshes of | ||
| 120 | this area. Monitoring of the vegetation distribution could be a useful | 130 | this area. Monitoring of the vegetation distribution could be a useful | ||
| 121 | tool to identify environmental impacts, in order to implement remedial | 131 | tool to identify environmental impacts, in order to implement remedial | ||
| 122 | actions.", | 132 | actions.", | ||
| 123 | "notes_translated": { | 133 | "notes_translated": { | ||
| 124 | "es": "This paper reports changes in vegetation distribution and | 134 | "es": "This paper reports changes in vegetation distribution and | ||
| 125 | species cover in relation to soil factors and hydrology in a semiarid | 135 | species cover in relation to soil factors and hydrology in a semiarid | ||
| 126 | Mediterranean salt marsh adjacent to the Mar Menor saline lagoon. | 136 | Mediterranean salt marsh adjacent to the Mar Menor saline lagoon. | ||
| 127 | Species cover, soil salinity, and the groundwater level were monitored | 137 | Species cover, soil salinity, and the groundwater level were monitored | ||
| 128 | between 1991 and 1993 and between 2002 and 2004, and total organic | 138 | between 1991 and 1993 and between 2002 and 2004, and total organic | ||
| 129 | carbon, total nitrogen, total phosphorus, nitrates, ammonium and | 139 | carbon, total nitrogen, total phosphorus, nitrates, ammonium and | ||
| 130 | exchangeable phosphorus were measured in the soils in both study | 140 | exchangeable phosphorus were measured in the soils in both study | ||
| 131 | periods. In addition, three soil profiles were described in August | 141 | periods. In addition, three soil profiles were described in August | ||
| 132 | 1992 and August 2004. The results indicate an elevation of the water | 142 | 1992 and August 2004. The results indicate an elevation of the water | ||
| 133 | table throughout the 13-year period, which was attributable to water | 143 | table throughout the 13-year period, which was attributable to water | ||
| 134 | flowing from areas with intensive agri culture. Flooding increased and | 144 | flowing from areas with intensive agri culture. Flooding increased and | ||
| 135 | soil salinity dropped in the most saline sites and increased in the | 145 | soil salinity dropped in the most saline sites and increased in the | ||
| 136 | least saline ones. The morphology of the soil profiles reflected the | 146 | least saline ones. The morphology of the soil profiles reflected the | ||
| 137 | increase in flooding periods, due to the appearance of a greyer matrix | 147 | increase in flooding periods, due to the appearance of a greyer matrix | ||
| 138 | in the deeper horizons and a more diffuse pattern of Fe mottles. | 148 | in the deeper horizons and a more diffuse pattern of Fe mottles. | ||
| 139 | Following these environmental changes, Sarcocornia fruticosa, | 149 | Following these environmental changes, Sarcocornia fruticosa, | ||
| 140 | Phragmites australis and Juncus maritimus strongly expanded at the | 150 | Phragmites australis and Juncus maritimus strongly expanded at the | ||
| 141 | wettest sites, which led to the disappearance of the original zonation | 151 | wettest sites, which led to the disappearance of the original zonation | ||
| 142 | pattern. The cover of Limonium delicatulum, in turn, decreased with | 152 | pattern. The cover of Limonium delicatulum, in turn, decreased with | ||
| 143 | the increase in moisture but increased following the increase in | 153 | the increase in moisture but increased following the increase in | ||
| 144 | salinity. Changes in soil nutrients were only very evident in the | 154 | salinity. Changes in soil nutrients were only very evident in the | ||
| 145 | sandy soils of the beach, probably due to the influence of organic | 155 | sandy soils of the beach, probably due to the influence of organic | ||
| 146 | debris deposited on the shoreline by the storms and due to the strong | 156 | debris deposited on the shoreline by the storms and due to the strong | ||
| 147 | increase in the colonisation of this habitat by perennial species. | 157 | increase in the colonisation of this habitat by perennial species. | ||
| 148 | According to the results obtained, control measures are needed in | 158 | According to the results obtained, control measures are needed in | ||
| 149 | order to preserve habitat diversity in this and other salt marshes of | 159 | order to preserve habitat diversity in this and other salt marshes of | ||
| 150 | this area. Monitoring of the vegetation distribution could be a useful | 160 | this area. Monitoring of the vegetation distribution could be a useful | ||
| 151 | tool to identify environmental impacts, in order to implement remedial | 161 | tool to identify environmental impacts, in order to implement remedial | ||
| 152 | actions." | 162 | actions." | ||
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