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1.
Nat Commun ; 15(1): 922, 2024 Jan 31.
Artigo em Inglês | MEDLINE | ID: mdl-38297000

RESUMO

Due to the abundance of microplastics in the environment, research about its possible adverse effects is increasing exponentially. Most studies investigating the effect of microplastics on cells still rely on commercially available polystyrene microspheres. However, the choice of these model microplastic particles can affect the outcome of the studies, as even nominally identical model microplastics may interact differently with cells due to different surface properties such as the surface charge. Here, we show that nominally identical polystyrene microspheres from eight different manufacturers significantly differ in their ζ-potential, which is the electrical potential of a particle in a medium at its slipping plane. The ζ-potential of the polystyrene particles is additionally altered after environmental exposure. We developed a microfluidic microscopy platform to demonstrate that the ζ-potential determines particle-cell adhesion strength. Furthermore, we find that due to this effect, the ζ-potential also strongly determines the internalization of the microplastic particles into cells. Therefore, the ζ-potential can act as a proxy of microplastic-cell interactions and may govern adverse effects reported in various organisms exposed to microplastics.


Assuntos
Microplásticos , Poluentes Químicos da Água , Microplásticos/toxicidade , Plásticos , Poliestirenos/toxicidade , Microesferas , Comunicação Celular , Poluentes Químicos da Água/análise , Monitoramento Ambiental
2.
Langmuir ; 38(29): 8748-8756, 2022 07 26.
Artigo em Inglês | MEDLINE | ID: mdl-35736564

RESUMO

The environmental fate and toxicity of microplastic particles are dominated by their surface properties. In the environment, an adsorbed layer of biomolecules and natural organic matter forms the so-called eco-corona. A quantitative description of how this eco-corona changes the particles' colloidal interactions is still missing. Here, we demonstrate with colloidal probe-atomic force microscopy that eco-corona formation on microplastic particles introduces a compressible film on the surface, which changes the mechanical behavior. We measure single particle-particle interactions and find a pronounced increase of long-range repulsive interactions upon eco-corona formation. These force-separation characteristics follow the Alexander-de Gennes (AdG) polymer brush model under certain conditions. We further compare the obtained fitting parameters to known systems like polyelectrolyte multilayers and propose these as model systems for the eco-corona. Our results show that concepts of fundamental polymer physics, like the AdG model, also help in understanding more complex systems like biomolecules adsorbed to surfaces, i.e., the eco-corona.


Assuntos
Microplásticos , Polímeros , Microscopia de Força Atômica , Plásticos , Propriedades de Superfície
3.
J Hazard Mater ; 437: 129351, 2022 09 05.
Artigo em Inglês | MEDLINE | ID: mdl-35728319

RESUMO

In aquatic ecosystems, filter feeders like mussels are particularly vulnerable to microplastics (MP). However, little is known about how the polymer type and the associated properties (like additives or remaining monomers) of MP impact organisms, as the predominant type of MP used for effect studies on the organismic level are micron grade polystyrene spheres, without considering their chemical composition. Therefore, we exposed the freshwater mussel Dreissena bugensis (D. bugensis) to in-depth characterized fragments in the same concentration and size range (20-120 µm): recycled polyethylene terephthalate from drinking bottles, polyamide, polystyrene, polylactic acid, and mussel shell fragments as natural particle control. Real-time valvometry, used to study behavioral responses via the movement of the mussels' valves, showed that mussels cannot distinguish between natural and MP particles, and therefore do not cease their filtration, as when exposed to dissolved pollutants. This unintentional ingestion led to polymer type-dependent adverse effects (activity of antioxidant enzymes and proteomic alterations), related to chemicals and residual monomers found in MP. Overall, recycled PET elicited the strongest negative effects, likely caused by anthranilamide, anthranilonitrile and butylated hydroxytoluene, contained in the fragments, which are toxic to aquatic organisms. As PET is among the most abundant MP in the environment, sublethal effects may gradually manifest at the population level, leading to irreversible ecosystem changes.


Assuntos
Bivalves , Dreissena , Poluentes Químicos da Água , Animais , Ecossistema , Microplásticos/toxicidade , Plásticos/toxicidade , Polímeros/toxicidade , Poliestirenos/toxicidade , Proteômica , Poluentes Químicos da Água/análise
4.
J Hazard Mater ; 428: 128151, 2022 04 15.
Artigo em Inglês | MEDLINE | ID: mdl-35042167

RESUMO

Microplastic (MP) debris is considered as a potentially hazardous material. It is omnipresent in our environment, and evidence that MP is also abundant in the atmosphere is increasing. Consequently, the inhalation of these particles is a significant exposure route to humans. Concerns about potential effects of airborne MP on human health are rising. However, currently, there are not enough studies on the putative toxicity of airborne MP to adequately assess its impact on human health. Therefore, we examined potential drivers of airborne MP toxicity. Physicochemical properties like size, shape, ζ-potential, adsorbed molecules and pathogens, and the MP's bio-persistence have been proposed as possible drivers of MP toxicity. Since their role in MP toxicity is largely unknown, we reviewed the literature on toxicologically well-studied non-plastic airborne microparticles (asbestos, silica, soot, wood, cotton, hay). We aimed to link the observed health effects and toxicology of these microparticles to the abovementioned properties. By comparing this information with studies on the effects of airborne MP, we analyzed possible mechanisms of airborne MP toxicity. Thus, we provide a basis for a mechanistic understanding of airborne MP toxicity. This may enable the assessment of risks associated with airborne MP pollution, facilitating effective policymaking and product design.


Assuntos
Microplásticos , Plásticos , Atmosfera , Monitoramento Ambiental , Poluição Ambiental , Humanos , Plásticos/toxicidade
5.
J Cell Biol ; 157(5): 883-95, 2002 May 27.
Artigo em Inglês | MEDLINE | ID: mdl-12034776

RESUMO

Clustering of acetylcholine receptors (AChRs) is a critical step in neuromuscular synaptogenesis, and is induced by agrin and laminin which are thought to act through different signaling mechanisms. We addressed whether laminin redistributes postsynaptic proteins and requires key elements of the agrin signaling pathway to cause AChR aggregation. In myotubes, laminin-1 rearranged dystroglycans and syntrophins into a laminin-like network, whereas inducing AChR-containing clusters of dystrobrevin, utrophin, and, to a marginal degree, MuSK. Laminin-1 also caused extensive coclustering of rapsyn and phosphotyrosine with AChRs, but none of these clusters were observed in rapsyn -/- myotubes. In parallel with clustering, laminin-1 induced tyrosine phosphorylation of AChR beta and delta subunits. Staurosporine and herbimycin, inhibitors of tyrosine kinases, prevented laminin-induced AChR phosphorylation and AChR and phosphotyrosine clustering, and caused rapid dispersal of clusters previously induced by laminin-1. Finally, laminin-1 caused normal aggregation of AChRs and phosphotyrosine in myotubes lacking both Src and Fyn kinases, but these clusters dispersed rapidly after laminin withdrawal. Thus, laminin-1 redistributes postsynaptic proteins and, like agrin, requires tyrosine kinases for AChR phosphorylation and clustering, and rapsyn for AChR cluster formation, whereas cluster stabilization depends on Src and Fyn. Therefore, the laminin and agrin signaling pathways overlap intracellularly, which may be important for neuromuscular synapse formation.


Assuntos
Proteínas Associadas à Distrofina , Laminina/metabolismo , Proteínas Musculares/metabolismo , Proteínas Proto-Oncogênicas/metabolismo , Receptores Colinérgicos/metabolismo , Sinapses/enzimologia , Quinases da Família src/metabolismo , Animais , Benzoquinonas , Células Cultivadas , Proteínas do Citoesqueleto/metabolismo , Distroglicanas , Inibidores Enzimáticos/farmacologia , Lactamas Macrocíclicas , Glicoproteínas de Membrana/metabolismo , Proteínas de Membrana/metabolismo , Junção Neuromuscular/metabolismo , Neuropeptídeos/metabolismo , Fosforilação/efeitos dos fármacos , Proteínas Proto-Oncogênicas c-fyn , Quinonas/farmacologia , Receptores Proteína Tirosina Quinases/metabolismo , Rifabutina/análogos & derivados , Transdução de Sinais/fisiologia , Estaurosporina/farmacologia , Tirosina/metabolismo , Utrofina
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