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en Harmful algae and pathogens on plastics in three mediterranean coastal lagoons -
Modificado el valor del campo
modified
del recurso Distribución HTML a2026-06-25
(anteriormente2026-06-23
) en Harmful algae and pathogens on plastics in three mediterranean coastal lagoons
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| 94 | "notes": "Plastic is now a pervasive pollutant in all marine | 104 | "notes": "Plastic is now a pervasive pollutant in all marine | ||
| 95 | ecosystems. The microplastics and macroplastic debris were studied in | 105 | ecosystems. The microplastics and macroplastic debris were studied in | ||
| 96 | three French Mediterranean coastal lagoons (Prevost, Biguglia and | 106 | three French Mediterranean coastal lagoons (Prevost, Biguglia and | ||
| 97 | Diana lagoons), displaying different environmental characteristics. In | 107 | Diana lagoons), displaying different environmental characteristics. In | ||
| 98 | addition, biofilm samples were analyzed over the seasons to quantify | 108 | addition, biofilm samples were analyzed over the seasons to quantify | ||
| 99 | and identify microalgae communities colonizing macroplastics, and | 109 | and identify microalgae communities colonizing macroplastics, and | ||
| 100 | determine potentially harmful microorganisms. Results indicate low but | 110 | determine potentially harmful microorganisms. Results indicate low but | ||
| 101 | highly variable concentrations of microplastics, in relation to the | 111 | highly variable concentrations of microplastics, in relation to the | ||
| 102 | period and location of sampling. Micro-Raman spectroscopy analyses | 112 | period and location of sampling. Micro-Raman spectroscopy analyses | ||
| 103 | revealed that the majority of macroplastic debris corresponded to | 113 | revealed that the majority of macroplastic debris corresponded to | ||
| 104 | polyethylene (PE) and low-density polyethylene (LDPE), and to a far | 114 | polyethylene (PE) and low-density polyethylene (LDPE), and to a far | ||
| 105 | lesser extent to polypropylene (PP). The observations by Scanning | 115 | lesser extent to polypropylene (PP). The observations by Scanning | ||
| 106 | Electron Microscopy of microalgae communities colonizing macroplastic | 116 | Electron Microscopy of microalgae communities colonizing macroplastic | ||
| 107 | debris demonstrated differences depending on the seasons, with higher | 117 | debris demonstrated differences depending on the seasons, with higher | ||
| 108 | amounts in spring and summer, but without any variation between | 118 | amounts in spring and summer, but without any variation between | ||
| 109 | lagoons and polymers. Among the Diatomophyceae, the most dominant | 119 | lagoons and polymers. Among the Diatomophyceae, the most dominant | ||
| 110 | genera were Amphora spp., Cocconeis spp., and Navicula spp.. | 120 | genera were Amphora spp., Cocconeis spp., and Navicula spp.. | ||
| 111 | Cyanobacteria and Dinophyceae such as Prorocentrum cordatum, a | 121 | Cyanobacteria and Dinophyceae such as Prorocentrum cordatum, a | ||
| 112 | potentially toxic species, were also found sporadically. The use of | 122 | potentially toxic species, were also found sporadically. The use of | ||
| 113 | Primer specific DNA amplification tools enabled us to detect | 123 | Primer specific DNA amplification tools enabled us to detect | ||
| 114 | potentially harmful microorganisms colonizing plastics, such as | 124 | potentially harmful microorganisms colonizing plastics, such as | ||
| 115 | Alexandrium minutum or Vibrio spp. An additional in situ experiment | 125 | Alexandrium minutum or Vibrio spp. An additional in situ experiment | ||
| 116 | performed over one year revealed an increase in the diversity of | 126 | performed over one year revealed an increase in the diversity of | ||
| 117 | colonizing microalgae in relation to the duration of immersion for the | 127 | colonizing microalgae in relation to the duration of immersion for the | ||
| 118 | three tested polymers PE, LDPE and polyethylene terephthalates (PET). | 128 | three tested polymers PE, LDPE and polyethylene terephthalates (PET). | ||
| 119 | Vibrio settled durably after two weeks of immersion, whatever the | 129 | Vibrio settled durably after two weeks of immersion, whatever the | ||
| 120 | polymer. This study confirms that Mediterranean coastal lagoons are | 130 | polymer. This study confirms that Mediterranean coastal lagoons are | ||
| 121 | vulnerable to the presence of macroplastic debris that may passively | 131 | vulnerable to the presence of macroplastic debris that may passively | ||
| 122 | host and transport various species, including some potentially harmful | 132 | host and transport various species, including some potentially harmful | ||
| 123 | algal and bacterial microorganisms.", | 133 | algal and bacterial microorganisms.", | ||
| 124 | "notes_translated": { | 134 | "notes_translated": { | ||
| 125 | "es": "Plastic is now a pervasive pollutant in all marine | 135 | "es": "Plastic is now a pervasive pollutant in all marine | ||
| 126 | ecosystems. The microplastics and macroplastic debris were studied in | 136 | ecosystems. The microplastics and macroplastic debris were studied in | ||
| 127 | three French Mediterranean coastal lagoons (Prevost, Biguglia and | 137 | three French Mediterranean coastal lagoons (Prevost, Biguglia and | ||
| 128 | Diana lagoons), displaying different environmental characteristics. In | 138 | Diana lagoons), displaying different environmental characteristics. In | ||
| 129 | addition, biofilm samples were analyzed over the seasons to quantify | 139 | addition, biofilm samples were analyzed over the seasons to quantify | ||
| 130 | and identify microalgae communities colonizing macroplastics, and | 140 | and identify microalgae communities colonizing macroplastics, and | ||
| 131 | determine potentially harmful microorganisms. Results indicate low but | 141 | determine potentially harmful microorganisms. Results indicate low but | ||
| 132 | highly variable concentrations of microplastics, in relation to the | 142 | highly variable concentrations of microplastics, in relation to the | ||
| 133 | period and location of sampling. Micro-Raman spectroscopy analyses | 143 | period and location of sampling. Micro-Raman spectroscopy analyses | ||
| 134 | revealed that the majority of macroplastic debris corresponded to | 144 | revealed that the majority of macroplastic debris corresponded to | ||
| 135 | polyethylene (PE) and low-density polyethylene (LDPE), and to a far | 145 | polyethylene (PE) and low-density polyethylene (LDPE), and to a far | ||
| 136 | lesser extent to polypropylene (PP). The observations by Scanning | 146 | lesser extent to polypropylene (PP). The observations by Scanning | ||
| 137 | Electron Microscopy of microalgae communities colonizing macroplastic | 147 | Electron Microscopy of microalgae communities colonizing macroplastic | ||
| 138 | debris demonstrated differences depending on the seasons, with higher | 148 | debris demonstrated differences depending on the seasons, with higher | ||
| 139 | amounts in spring and summer, but without any variation between | 149 | amounts in spring and summer, but without any variation between | ||
| 140 | lagoons and polymers. Among the Diatomophyceae, the most dominant | 150 | lagoons and polymers. Among the Diatomophyceae, the most dominant | ||
| 141 | genera were Amphora spp., Cocconeis spp., and Navicula spp.. | 151 | genera were Amphora spp., Cocconeis spp., and Navicula spp.. | ||
| 142 | Cyanobacteria and Dinophyceae such as Prorocentrum cordatum, a | 152 | Cyanobacteria and Dinophyceae such as Prorocentrum cordatum, a | ||
| 143 | potentially toxic species, were also found sporadically. The use of | 153 | potentially toxic species, were also found sporadically. The use of | ||
| 144 | Primer specific DNA amplification tools enabled us to detect | 154 | Primer specific DNA amplification tools enabled us to detect | ||
| 145 | potentially harmful microorganisms colonizing plastics, such as | 155 | potentially harmful microorganisms colonizing plastics, such as | ||
| 146 | Alexandrium minutum or Vibrio spp. An additional in situ experiment | 156 | Alexandrium minutum or Vibrio spp. An additional in situ experiment | ||
| 147 | performed over one year revealed an increase in the diversity of | 157 | performed over one year revealed an increase in the diversity of | ||
| 148 | colonizing microalgae in relation to the duration of immersion for the | 158 | colonizing microalgae in relation to the duration of immersion for the | ||
| 149 | three tested polymers PE, LDPE and polyethylene terephthalates (PET). | 159 | three tested polymers PE, LDPE and polyethylene terephthalates (PET). | ||
| 150 | Vibrio settled durably after two weeks of immersion, whatever the | 160 | Vibrio settled durably after two weeks of immersion, whatever the | ||
| 151 | polymer. This study confirms that Mediterranean coastal lagoons are | 161 | polymer. This study confirms that Mediterranean coastal lagoons are | ||
| 152 | vulnerable to the presence of macroplastic debris that may passively | 162 | vulnerable to the presence of macroplastic debris that may passively | ||
| 153 | host and transport various species, including some potentially harmful | 163 | host and transport various species, including some potentially harmful | ||
| 154 | algal and bacterial microorganisms." | 164 | algal and bacterial microorganisms." | ||
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