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del recurso Distribución HTML a2026-06-25
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) en Effects of mining wastes on a seagrass ecosystem: metal accumulation and bioavailability, seagrass dynamics and associated community structure
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| 97 | "notes": "Two different Cymodocea nodosa (Ucria) Ascherson beds | 107 | "notes": "Two different Cymodocea nodosa (Ucria) Ascherson beds | ||
| 98 | growing in mining-contaminated sediments were compared with two | 108 | growing in mining-contaminated sediments were compared with two | ||
| 99 | reference beds in the Mar Menor coastal lagoon. The accumulation of | 109 | reference beds in the Mar Menor coastal lagoon. The accumulation of | ||
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| 101 | parameters that regulate the availability of metals, the seabed | 111 | parameters that regulate the availability of metals, the seabed | ||
| 102 | structure and dynamics of each seagrass bed and its associated | 112 | structure and dynamics of each seagrass bed and its associated | ||
| 103 | macroinvertebrate community were studied. C nodosa accumulates metals | 113 | macroinvertebrate community were studied. C nodosa accumulates metals | ||
| 104 | from the sediments and reflects their bioavailability for this | 114 | from the sediments and reflects their bioavailability for this | ||
| 105 | seagrass. At each station, the metal content of the rhizomes was lower | 115 | seagrass. At each station, the metal content of the rhizomes was lower | ||
| 106 | than that of leaves and roots. The concentration of acid-volatile | 116 | than that of leaves and roots. The concentration of acid-volatile | ||
| 107 | sulfides does not seem to influence the availability of metals to the | 117 | sulfides does not seem to influence the availability of metals to the | ||
| 108 | seagrass, possibly due to oxygen transport to underground tissues. The | 118 | seagrass, possibly due to oxygen transport to underground tissues. The | ||
| 109 | highest metal concentration in all the contaminated stations was found | 119 | highest metal concentration in all the contaminated stations was found | ||
| 110 | in the leaf-biofilm, due to the formation of complexes between metals | 120 | in the leaf-biofilm, due to the formation of complexes between metals | ||
| 111 | and the extracellular polymeric substances that form the biofilm. All | 121 | and the extracellular polymeric substances that form the biofilm. All | ||
| 112 | the seagrass beds were seen to be undergoing expansion, those growing | 122 | the seagrass beds were seen to be undergoing expansion, those growing | ||
| 113 | in contaminated sediments accumulating great quantities of metals and | 123 | in contaminated sediments accumulating great quantities of metals and | ||
| 114 | showing highest photosynthetic leaf surface area and highest leaf | 124 | showing highest photosynthetic leaf surface area and highest leaf | ||
| 115 | biomass. However, these structural parameters were not seen to be | 125 | biomass. However, these structural parameters were not seen to be | ||
| 116 | responsible for the differences in the faunal composition observed | 126 | responsible for the differences in the faunal composition observed | ||
| 117 | between contaminated and reference beds. Moreover, the multivariate | 127 | between contaminated and reference beds. Moreover, the multivariate | ||
| 118 | analysis identified the metal content of leaves, biofilm and sediments | 128 | analysis identified the metal content of leaves, biofilm and sediments | ||
| 119 | as important variables that may be responsible for these differences | 129 | as important variables that may be responsible for these differences | ||
| 120 | in faunal composition. In this study we have demonstrated that both | 130 | in faunal composition. In this study we have demonstrated that both | ||
| 121 | the seagrass C nodosa and the biofilm on the plant leaves may be used | 131 | the seagrass C nodosa and the biofilm on the plant leaves may be used | ||
| 122 | as environmental tools in the Mar Menor lagoon. The former is an | 132 | as environmental tools in the Mar Menor lagoon. The former is an | ||
| 123 | useful indicator of sediment contamination, whereas the latter seems | 133 | useful indicator of sediment contamination, whereas the latter seems | ||
| 124 | to be a good sentinel of water quality. (c) 2004 Elsevier Ltd. All | 134 | to be a good sentinel of water quality. (c) 2004 Elsevier Ltd. All | ||
| 125 | rights reserved.", | 135 | rights reserved.", | ||
| 126 | "notes_translated": { | 136 | "notes_translated": { | ||
| 127 | "es": "Two different Cymodocea nodosa (Ucria) Ascherson beds | 137 | "es": "Two different Cymodocea nodosa (Ucria) Ascherson beds | ||
| 128 | growing in mining-contaminated sediments were compared with two | 138 | growing in mining-contaminated sediments were compared with two | ||
| 129 | reference beds in the Mar Menor coastal lagoon. The accumulation of | 139 | reference beds in the Mar Menor coastal lagoon. The accumulation of | ||
| 130 | Zn, Pb and Cd in different fractions of the plant, the sediment | 140 | Zn, Pb and Cd in different fractions of the plant, the sediment | ||
| 131 | parameters that regulate the availability of metals, the seabed | 141 | parameters that regulate the availability of metals, the seabed | ||
| 132 | structure and dynamics of each seagrass bed and its associated | 142 | structure and dynamics of each seagrass bed and its associated | ||
| 133 | macroinvertebrate community were studied. C nodosa accumulates metals | 143 | macroinvertebrate community were studied. C nodosa accumulates metals | ||
| 134 | from the sediments and reflects their bioavailability for this | 144 | from the sediments and reflects their bioavailability for this | ||
| 135 | seagrass. At each station, the metal content of the rhizomes was lower | 145 | seagrass. At each station, the metal content of the rhizomes was lower | ||
| 136 | than that of leaves and roots. The concentration of acid-volatile | 146 | than that of leaves and roots. The concentration of acid-volatile | ||
| 137 | sulfides does not seem to influence the availability of metals to the | 147 | sulfides does not seem to influence the availability of metals to the | ||
| 138 | seagrass, possibly due to oxygen transport to underground tissues. The | 148 | seagrass, possibly due to oxygen transport to underground tissues. The | ||
| 139 | highest metal concentration in all the contaminated stations was found | 149 | highest metal concentration in all the contaminated stations was found | ||
| 140 | in the leaf-biofilm, due to the formation of complexes between metals | 150 | in the leaf-biofilm, due to the formation of complexes between metals | ||
| 141 | and the extracellular polymeric substances that form the biofilm. All | 151 | and the extracellular polymeric substances that form the biofilm. All | ||
| 142 | the seagrass beds were seen to be undergoing expansion, those growing | 152 | the seagrass beds were seen to be undergoing expansion, those growing | ||
| 143 | in contaminated sediments accumulating great quantities of metals and | 153 | in contaminated sediments accumulating great quantities of metals and | ||
| 144 | showing highest photosynthetic leaf surface area and highest leaf | 154 | showing highest photosynthetic leaf surface area and highest leaf | ||
| 145 | biomass. However, these structural parameters were not seen to be | 155 | biomass. However, these structural parameters were not seen to be | ||
| 146 | responsible for the differences in the faunal composition observed | 156 | responsible for the differences in the faunal composition observed | ||
| 147 | between contaminated and reference beds. Moreover, the multivariate | 157 | between contaminated and reference beds. Moreover, the multivariate | ||
| 148 | analysis identified the metal content of leaves, biofilm and sediments | 158 | analysis identified the metal content of leaves, biofilm and sediments | ||
| 149 | as important variables that may be responsible for these differences | 159 | as important variables that may be responsible for these differences | ||
| 150 | in faunal composition. In this study we have demonstrated that both | 160 | in faunal composition. In this study we have demonstrated that both | ||
| 151 | the seagrass C nodosa and the biofilm on the plant leaves may be used | 161 | the seagrass C nodosa and the biofilm on the plant leaves may be used | ||
| 152 | as environmental tools in the Mar Menor lagoon. The former is an | 162 | as environmental tools in the Mar Menor lagoon. The former is an | ||
| 153 | useful indicator of sediment contamination, whereas the latter seems | 163 | useful indicator of sediment contamination, whereas the latter seems | ||
| 154 | to be a good sentinel of water quality. (c) 2004 Elsevier Ltd. All | 164 | to be a good sentinel of water quality. (c) 2004 Elsevier Ltd. All | ||
| 155 | rights reserved." | 165 | rights reserved." | ||
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