生物塑料(PHBV)的微生物降解受到高微塑料负荷下营养物质可用性的限制

IF 3.5 Q3 ENGINEERING, ENVIRONMENTAL Environmental science. Advances Pub Date : 2024-10-29 DOI:10.1039/D4VA00311J
Michaela K. Reay, Martine Graf, Lucy M. Greenfield, Rafael Bargiela, Charles Onyije, Charlotte E. M. Lloyd, Ian D. Bull, Richard P. Evershed, Peter N. Golyshin, David R. Chadwick and Davey L. Jones
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摘要

可生物降解塑料为农业中使用的传统塑料提供了另一种选择。然而,与工业堆肥和微塑料的高产量相比,环境中较慢的降解日益受到关注,并提出了它们是否代表可行替代品的问题。目前尚不清楚所观察到的可生物降解塑料对土壤微生物群落和植物养分吸收的影响是来自微塑料本身的生物降解还是非生物效应。本研究的目的是通过热解/气相色谱-质谱联用(Py/GC-MS)技术量化增加微塑料负荷(0.06-3.2% w/w)时生物塑料聚(3-羟基丁酸酯-co-3-羟基戊酸酯)(PHBV)的生物降解以及对土壤健康和植物生长的影响。8周后,土壤中PHBV微塑料的降解率在1.5 ~ 5%之间,由于微生物氮(N)的限制,降解率随着PHBV浓度的增加而下降,这表明氮循环酶的投入增加。植物也受到氮和磷(P)的限制。更高的可提取土壤铵和硝态氮与氮的限制相矛盾,然而,土壤疏水性的增加可能限制了流动性,从而限制了植物和微生物的利用。因此,PHBV降解产生的C增加并没有导致微生物生物量的同时增加,在PHBV微塑料负荷较高时,微生物生物量减少,表明微生物碳利用效率较低。高PHBV微塑料负荷对微生物群落规模和结构、土壤性质和植物生长有显著影响,而低PHBV浓度(0.06% w/w)的影响最小。在高塑料负荷下观察到的养分限制对标准生物降解试验的设计具有重要意义,这些试验必须考虑微塑料对土壤养分循环的非生物和生物效应。
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Microbial degradation of bioplastic (PHBV) is limited by nutrient availability at high microplastic loadings†

Biodegradable plastic offers an alternative to conventional plastic for use in agriculture. However, slower degradation in the environment compared to industrial composting and high production of microplastics is of growing concern and poses the question whether they represent a viable replacement. It remains unclear whether observed effects of biodegradable plastics on the soil microbial community and plant nutrient uptake are from biodegradation or from the abiotic effects of the microplastics themselves. The aim of this study was to quantify the biodegradation of the bioplastic poly(3-hydroxybutyrate-co-3-hydroxyvalerate) (PHBV), at increasing microplastic loadings (0.06–3.2% w/w) via pyrolysis/gas chromatography-mass spectrometry (Py/GC-MS) alongside effects on soil health and plant growth (Zea mays L.). Between 1.5 and 5% of PHBV microplastic was degraded in soil after 8 weeks, with the rate declining with increasing PHBV concentrations due to microbial nitrogen (N) limitation, demonstrated by increased investment in N-cycling enzymes. Plants were also limited by both N and phosphorus (P). Greater extractable soil ammonium and nitrate contradicted N limitation, however, increases in soil hydrophobicity likely limited mobility, and thus plant and microbial utilisation. As a result, increased C from PHBV degradation did not result in a concurrent increase in microbial biomass, which was reduced under higher PHBV microplastic loading, indicating low microbial carbon use efficiency. While high PHBV microplastic loadings resulted in significant effects on the microbial community size and structure, soil properties and plant growth, there were minimal effects at low PHBV concentrations (0.06% w/w). Observations of nutrient limitation at higher plastic loadings has significant implications for the design of standard biodegradation assays, which must consider both abiotic and biotic effects of microplastic on soil nutrient cycling.

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