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Toxicity of three rare earth elements, and their combinations to algae, microcrustaceans, and fungi.
Bergsten-Torralba, L R; Magalhães, D P; Giese, E C; Nascimento, C R S; Pinho, J V A; Buss, D F.
Afiliação
  • Bergsten-Torralba LR; Oswaldo Cruz Institute - IOC, Program in Biodiversity and Health, Fiocruz, Rio de Janeiro - Brazil; Oswaldo Cruz Institute - IOC, Laboratory of Evaluation and Promotion of Environmental Health (LAPSA), Fiocruz, Rio de Janeiro, Brazil. Electronic address: ludmila.bergsten@gmail.com.
  • Magalhães DP; Center for Mineral Technology - CETEM, Rio de Janeiro, Brazil.
  • Giese EC; Center for Mineral Technology - CETEM, Rio de Janeiro, Brazil.
  • Nascimento CRS; National Institute for Quality Control in Health - INCQS, Fiocruz, Rio de Janeiro, Brazil.
  • Pinho JVA; National School of Public Health Sergio Arouca - ENSP, Program of Public Health and Environment, Fiocruz, Rio de Janeiro, Brazil.
  • Buss DF; Pan American Health Organization: PAHO, Washington, D.C., USA.
Ecotoxicol Environ Saf ; 201: 110795, 2020 Sep 15.
Article em En | MEDLINE | ID: mdl-32544742
ABSTRACT
Rare earth elements (REEs) are naturally distributed in the environment, and are increasingly being used in agriculture and high technology materials worldwide, thereby increasing anthropogenic contamination and environmental risks. There exists scarce and contradictory toxicity information about REEs; hence, more studies are required, especially on their mixtures. Thus, this study aimed to assess the toxicities of La3+, Nd3+, Sm3+, and the combinations of these elements (binary 11 and ternary 111), to organisms from different trophic levels producers (the microalgae Chlorella vulgaris and Raphidocelis subcapitata), primary consumers (the microcrustaceans Daphnia similis and Artemia salina), and decomposers (the fungi Penicillium simplicissimum and Aspergillus japonicus). Ecotoxicological bioassays were performed, and toxic concentrations were determined. Thereafter, toxicities of single and mixture REEs were classified as slightly to highly toxic according to their toxic units. Finally, a concentration addition (CA) model was used to estimate how REEs interact upon combining. Nd3+ was the most toxic element for all organisms, especially D. similis (48 h LC50 9.41 mg.L-1), and was therefore classified as highly toxic. Sm3+ promoted cell agglomeration in Chlorella vulgaris and was the most toxic of the tested elements for this organism (72 h IC50 25.78 mg.L-1). The CA model revealed synergistic responses for most of the combinations, principally Nd3+ + Sm3+, which was the most toxic combination for the tested organisms. Both fungi were the most resistant organisms, and A. japonicus produced exudate and sclerotia, which help in the detoxification of chemicals. Owing not only to the fact that fungi displayed a higher resistance to REEs, but also due to the absence of regulations for REEs released from the agricultural or industrial sector, and the lack of methods to treat effluents or to dispose of technological items containing REEs, these organisms should be considered as a model for the biosorption or bioremediation of REEs. Finally, the toxic effects of REEs, particularly Nd3+, on the biota and human health should be the focus of future studies due to their increased use in technology.
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Texto completo: 1 Base de dados: MEDLINE Assunto principal: Penicillium / Aspergillus / Poluentes Químicos da Água / Daphnia / Chlorella vulgaris / Metais Terras Raras Idioma: En Ano de publicação: 2020 Tipo de documento: Article

Texto completo: 1 Base de dados: MEDLINE Assunto principal: Penicillium / Aspergillus / Poluentes Químicos da Água / Daphnia / Chlorella vulgaris / Metais Terras Raras Idioma: En Ano de publicação: 2020 Tipo de documento: Article