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聚乳酸微塑料的生物降解及其在活性污泥中生物污垢后的毒性效应。

The biodegradation of polylactic acid microplastic and their toxic effect after biofouling in activate sludge.

机构信息

Division of Environmental Science and Ecological Engineering, Korea University, Seoul, 02841, Republic of Korea.

OJeong Resilience Institute, Korea University, Seoul, 02841, Republic of Korea.

出版信息

Environ Pollut. 2024 Dec 1;362:125038. doi: 10.1016/j.envpol.2024.125038. Epub 2024 Sep 27.

Abstract

Biodegradable microplastics (MPs) can form biofilms through interactions with various microorganisms in aquatic system and can be exposed to organisms. This study first investigated biodegradability of polylactic acid (PLA) MPs and the characterization of PLA MPs before/after biofouling (4 weeks) and their toxic effects on the freshwater invertebrate Daphnia magna. The biodegradability rate of PLA MPs was up to 50% over 28 days, suggesting that even biodegradable MPs do not easily decompose under environmental conditions. Furthermore, biofouling of MPs led to an increase in size and, in the process, induced an additional functional peak in the PLA MPs. The exposure of biofouled MPs did not lead to a reduction in survival, reproduction, or growth during chronic exposure, nor did it cause feeding inhibition in juvenile (<4 days old) D. magna. However, pristine MPs significantly reduced survival, reproduction, and growth at concentrations of 5.0 mg L. Overall, pristine MPs caused inhibition of reproduction and growth and high mortality in D. magna, while the biofouling process did not induce these effects. Our findings highlight the complex interactions between MPs and biological components in aquatic environments, emphasizing the importance of considering biofouling dynamics when assessing the ecological impacts of biodegradable MPs.

摘要

可生物降解的微塑料(MPs)可以通过与水生系统中各种微生物的相互作用形成生物膜,并暴露于生物体中。本研究首先考察了聚乳酸(PLA) MPs 的生物降解性以及生物污损前后(4 周) PLA MPs 的特征,并研究了它们对淡水无脊椎动物大型溞(Daphnia magna)的毒性效应。PLA MPs 在 28 天内的生物降解率高达 50%,这表明即使是可生物降解的 MPs 在环境条件下也不容易分解。此外,MPs 的生物污损会导致其尺寸增加,并且在此过程中,在 PLA MPs 中诱导出一个额外的功能峰。在慢性暴露过程中,生物污损的 MPs 的暴露并没有导致存活、繁殖或生长减少,也没有导致幼体(<4 天大)大型溞的摄食抑制。然而,在 5.0mg/L 的浓度下,原始 MPs 显著降低了大型溞的存活率、繁殖率和生长率。总体而言,原始 MPs 导致了大型溞的繁殖和生长抑制以及高死亡率,而生物污损过程并没有诱导这些效应。我们的研究结果强调了 MPs 与水生环境中生物成分之间的复杂相互作用,当评估可生物降解 MPs 的生态影响时,考虑生物污损动态非常重要。

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