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en Evidence of microplastics in water and commercial fish from a high-altitude mountain lake (Lake Titicaca) -
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del recurso Distribución HTML a2026-06-25
(anteriormente2026-06-23
) en Evidence of microplastics in water and commercial fish from a high-altitude mountain lake (Lake Titicaca) -
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modified
del recurso https://pro.iepnb.gob.es/catalogo/dataset/8e2bcfd9-290b-5792-a8a5-cfc7f678a96b/resource/83728a9d-cbe7-46a3-8094-6ea87d29401f a2026-06-25
(anteriormente2026-06-23
) en Evidence of microplastics in water and commercial fish from a high-altitude mountain lake (Lake Titicaca)
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| 87 | "notes": "Microplastic pollution is a widespread environmental | 97 | "notes": "Microplastic pollution is a widespread environmental | ||
| 88 | concern. Like other anthro-pogenic pollutants, microplastics can reach | 98 | concern. Like other anthro-pogenic pollutants, microplastics can reach | ||
| 89 | aquatic ecosystems through rivers and interact with the aquatic biota. | 99 | aquatic ecosystems through rivers and interact with the aquatic biota. | ||
| 90 | For instance, Lake Titicaca (between Bolivia and Peru), one of the | 100 | For instance, Lake Titicaca (between Bolivia and Peru), one of the | ||
| 91 | great ancient lakes in South America (3,809 m a.s.l.), shows a | 101 | great ancient lakes in South America (3,809 m a.s.l.), shows a | ||
| 92 | pollution problem, particularly in the southern shallow basin (Lago | 102 | pollution problem, particularly in the southern shallow basin (Lago | ||
| 93 | Menor) in Bolivia. Nevertheless, our knowledge of the presence of | 103 | Menor) in Bolivia. Nevertheless, our knowledge of the presence of | ||
| 94 | microplastics and their interaction with the biota of Lake Titicaca is | 104 | microplastics and their interaction with the biota of Lake Titicaca is | ||
| 95 | limited. Therefore, this study evaluated the presence of microplastics | 105 | limited. Therefore, this study evaluated the presence of microplastics | ||
| 96 | in the stomach content of the four fish species targeted by local | 106 | in the stomach content of the four fish species targeted by local | ||
| 97 | fisheries in Lago Menor of Lake Titicaca (Orestias luteus, Orestias | 107 | fisheries in Lago Menor of Lake Titicaca (Orestias luteus, Orestias | ||
| 98 | agassizii, Trichomycterus dispar, and Odonthestes bonariensis; N = | 108 | agassizii, Trichomycterus dispar, and Odonthestes bonariensis; N = | ||
| 99 | 1,283), and looked for relationships with trophic guilds or fishing | 109 | 1,283), and looked for relationships with trophic guilds or fishing | ||
| 100 | areas. Additionally, surface water was analyzed to evaluate the | 110 | areas. Additionally, surface water was analyzed to evaluate the | ||
| 101 | presence of microplastics in the water. The evaluation of | 111 | presence of microplastics in the water. The evaluation of | ||
| 102 | microplastics was carried out by visual observations. We observed that | 112 | microplastics was carried out by visual observations. We observed that | ||
| 103 | the frequency of microplastic ingestion was low in all species (<5%). | 113 | the frequency of microplastic ingestion was low in all species (<5%). | ||
| 104 | Conversely, microplastic was present in the water, with the highest | 114 | Conversely, microplastic was present in the water, with the highest | ||
| 105 | quantity at the southern part of Lago Menor (103 +/- 20 particles per | 115 | quantity at the southern part of Lago Menor (103 +/- 20 particles per | ||
| 106 | L), without differences in the microplastic number between sites. Most | 116 | L), without differences in the microplastic number between sites. Most | ||
| 107 | microplastics counted in stomach contents were fibers, whereas water | 117 | microplastics counted in stomach contents were fibers, whereas water | ||
| 108 | samples mainly contained fragments. Our results point to microplastic | 118 | samples mainly contained fragments. Our results point to microplastic | ||
| 109 | pollution in Lago Menor of Lake Titicaca. However, we could not | 119 | pollution in Lago Menor of Lake Titicaca. However, we could not | ||
| 110 | determine the pollution rate due to considerable methodological | 120 | determine the pollution rate due to considerable methodological | ||
| 111 | limitations. Further research will be needed to robustly detect | 121 | limitations. Further research will be needed to robustly detect | ||
| 112 | microplastics in Lake Titicaca and their impact on the fish species in | 122 | microplastics in Lake Titicaca and their impact on the fish species in | ||
| 113 | the lake.", | 123 | the lake.", | ||
| 114 | "notes_translated": { | 124 | "notes_translated": { | ||
| 115 | "es": "Microplastic pollution is a widespread environmental | 125 | "es": "Microplastic pollution is a widespread environmental | ||
| 116 | concern. Like other anthro-pogenic pollutants, microplastics can reach | 126 | concern. Like other anthro-pogenic pollutants, microplastics can reach | ||
| 117 | aquatic ecosystems through rivers and interact with the aquatic biota. | 127 | aquatic ecosystems through rivers and interact with the aquatic biota. | ||
| 118 | For instance, Lake Titicaca (between Bolivia and Peru), one of the | 128 | For instance, Lake Titicaca (between Bolivia and Peru), one of the | ||
| 119 | great ancient lakes in South America (3,809 m a.s.l.), shows a | 129 | great ancient lakes in South America (3,809 m a.s.l.), shows a | ||
| 120 | pollution problem, particularly in the southern shallow basin (Lago | 130 | pollution problem, particularly in the southern shallow basin (Lago | ||
| 121 | Menor) in Bolivia. Nevertheless, our knowledge of the presence of | 131 | Menor) in Bolivia. Nevertheless, our knowledge of the presence of | ||
| 122 | microplastics and their interaction with the biota of Lake Titicaca is | 132 | microplastics and their interaction with the biota of Lake Titicaca is | ||
| 123 | limited. Therefore, this study evaluated the presence of microplastics | 133 | limited. Therefore, this study evaluated the presence of microplastics | ||
| 124 | in the stomach content of the four fish species targeted by local | 134 | in the stomach content of the four fish species targeted by local | ||
| 125 | fisheries in Lago Menor of Lake Titicaca (Orestias luteus, Orestias | 135 | fisheries in Lago Menor of Lake Titicaca (Orestias luteus, Orestias | ||
| 126 | agassizii, Trichomycterus dispar, and Odonthestes bonariensis; N = | 136 | agassizii, Trichomycterus dispar, and Odonthestes bonariensis; N = | ||
| 127 | 1,283), and looked for relationships with trophic guilds or fishing | 137 | 1,283), and looked for relationships with trophic guilds or fishing | ||
| 128 | areas. Additionally, surface water was analyzed to evaluate the | 138 | areas. Additionally, surface water was analyzed to evaluate the | ||
| 129 | presence of microplastics in the water. The evaluation of | 139 | presence of microplastics in the water. The evaluation of | ||
| 130 | microplastics was carried out by visual observations. We observed that | 140 | microplastics was carried out by visual observations. We observed that | ||
| 131 | the frequency of microplastic ingestion was low in all species (<5%). | 141 | the frequency of microplastic ingestion was low in all species (<5%). | ||
| 132 | Conversely, microplastic was present in the water, with the highest | 142 | Conversely, microplastic was present in the water, with the highest | ||
| 133 | quantity at the southern part of Lago Menor (103 +/- 20 particles per | 143 | quantity at the southern part of Lago Menor (103 +/- 20 particles per | ||
| 134 | L), without differences in the microplastic number between sites. Most | 144 | L), without differences in the microplastic number between sites. Most | ||
| 135 | microplastics counted in stomach contents were fibers, whereas water | 145 | microplastics counted in stomach contents were fibers, whereas water | ||
| 136 | samples mainly contained fragments. Our results point to microplastic | 146 | samples mainly contained fragments. Our results point to microplastic | ||
| 137 | pollution in Lago Menor of Lake Titicaca. However, we could not | 147 | pollution in Lago Menor of Lake Titicaca. However, we could not | ||
| 138 | determine the pollution rate due to considerable methodological | 148 | determine the pollution rate due to considerable methodological | ||
| 139 | limitations. Further research will be needed to robustly detect | 149 | limitations. Further research will be needed to robustly detect | ||
| 140 | microplastics in Lake Titicaca and their impact on the fish species in | 150 | microplastics in Lake Titicaca and their impact on the fish species in | ||
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