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1.
Huan Jing Ke Xue ; 45(2): 1173-1184, 2024 Feb 08.
Artigo em Chinês | MEDLINE | ID: mdl-38471954

RESUMO

The effect of microplastics on the ecological environment and human health has become a topical issue, and research on the risks and harmful effects of MPs on human health in particular has attracted widespread attention. Due to the characteristics of small size, low degradability, and easy migration, MPs continuously migrate from the environment to the human body, and their main exposure pathways are oral ingestion, inhalation, and dermal contact, with the main exposure media being food, drinking water, dust, personal care products, etc. MPs have been detected in organs, fluids, and excreta of digestive, respiratory, cardiovascular, reproductive systems, etc. The abundance range of MPs in the human body is 0-1 206.94 particles per gram. After entering the human body, MPs can cause cytotoxicity, mitochondrial toxicity, DNA damage, cell membrane damage, and other effects on human cells and organs, leading to serious consequences such as local inflammation, ecological imbalance, metabolic disorders, etc., in various systems. Owing to their small specific surface area, they can also adsorb pollutants such as heavy metals, organic pollutants, antibiotics, pathogens, and harmful microorganisms, causing combined toxicity and immunotoxicity. In the end, we highlighted general deficiencies in existing studies and provided directions for future research on the influence of MPs on human health.


Assuntos
Poluentes Ambientais , Metais Pesados , Poluentes Químicos da Água , Humanos , Microplásticos , Plásticos , Poluentes Químicos da Água/análise
2.
Sci Total Environ ; 912: 169140, 2024 Feb 20.
Artigo em Inglês | MEDLINE | ID: mdl-38070561

RESUMO

Ocular surface diseases are common in the plateau city, Kunming China, the continued daily exposure to heavy metals in dust may be an important inducement. In this study, the 150 road dust samples from five functional areas in Kunming were collected. The concentrations, distribution, possible sources, and bioaccessibility of heavy metals were analyzed. The adverse effects of dust extracts on human corneal epithelial cells and the underlying mechanisms were also assessed. The concentrations (mg·kg-1) of As (19.1), Cd (2.67), Cr (90.5), Cu (123), Pb (78.4), and Zn (389) in road dust were higher than the soil background, with commercial and residential areas showing the highest pollution. Their bioaccessibility in artificial tears was As (6.59 %) > Cu (5.11 %) > Ni (1.47 %) > Cr (1.17 %) > Mn (0.84 %) > Cd (0.76 %) > Zn (0.50 %) > Pb (0.31 %). The two main sources of heavy metals included tire and mechanical abrasion (24.5 %) and traffic exhaust (21.6 %). All dust extracts induced cytotoxicity, evidenced by stronger inhibition of cell viability, higher production of ROS, and altered mRNA expression of antioxidant enzymes and cell cycle-related genes, with commercial- areas-2 (CA2)-dust extract showing the greatest oxidative damage and cell cycle arrest. Our data may provide new evidence that dust exposure in high geological background cities could trigger human cornea damage.


Assuntos
Poeira , Metais Pesados , Humanos , Poeira/análise , Cidades , Monitoramento Ambiental , Cádmio , Chumbo , Metais Pesados/toxicidade , Metais Pesados/análise , China , Medição de Risco
3.
Chemosphere ; 331: 138817, 2023 Aug.
Artigo em Inglês | MEDLINE | ID: mdl-37127200

RESUMO

Tris(2-chloroisopropyl) phosphate (TCPP) and Tris(2-chloroethyl) phosphate (TCEP) are the widely used organophosphorus flame retardants indoors and easily accessible to the eyes as the common adhesive components of dust and particle matter, however, hardly any evidence has demonstrated their corneal toxicity. In this study, the adverse effects of TCPP, TCEP, and TCPP + TCEP exposure on human corneal epithelial cells (HCECs) were investigated. The cell viability and morphology, intracellular reactive oxygen species (ROS), cell cycle, and the expressions of cell cycle and pyroptosis-related genes were assessed to explain the underlying mechanisms. Compared to individual exposure, co-exposure to TCPP20+TCEP20 showed higher cytotoxicity with a sharp decrease of >30% in viability and more serious oxidative damage by increasing ROS production to 110.92% compared to the control group. Furthermore, the cell cycle arrested at the S phase (36.20%) was observed after combined treatment, evidenced by the upregulation of cyclin D1, CDK2, CDK4, CDK6, p21, and p27. Interestingly, pyroptosis-related genes GSDMD, Caspase-1, NLRP3, IL-1ß, IL-18, NLRP1, and NLRC4 expressions were promoted with cell swelling and glowing morphology. Oxidative stress and cell cycle arrest probably acted as a key role in TCPP20+TCEP20-induced cytotoxicity and pyroptosis in HCECs. Our results suggested that TCPP20+TCEP20 co-exposure induced severer corneal damage, further illustrating its significance in estimating indoor health hazards to humans.


Assuntos
Retardadores de Chama , Piroptose , Humanos , Espécies Reativas de Oxigênio/metabolismo , Células Epiteliais/metabolismo , Estresse Oxidativo , Pontos de Checagem do Ciclo Celular , Fosfatos/metabolismo , Retardadores de Chama/toxicidade
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