Wang Jiuqi, Yan Pengke, Wang Wan, Hao Xinhua, Xu Bing, Aurangzeib Muhammad, Zhang Shaoliang
Northeast Agricultural University, Harbin, China.
Front Microbiol. 2022 Apr 4;13:733804. doi: 10.3389/fmicb.2022.733804. eCollection 2022.
Degradation of microplastics (MPs) by both physicochemical and biological processes in the natural environment is determined by the enzymes inside the soil, and which was severely influenced by crop growth and straw amendment (SA). However, it is still unclear how crop growth and SA influence degradation of MPs in soils. In this study, both catalase and sucrase were measured, and the stereomicroscope combined with microscopic infrared spectroscopy and scanning electron microscope (SEM) was used to detect the morphology and quantity of low-density polyethylene microplastic (LDPE-MP) and low-density polypropylene microplastic (LDPP-MP), after crop growth (maize and soybean, with and without SA, 1 and 2% MP) in an outdoor pot experiment, in the Mollisols. The results showed that the growth of the crops changed the morphology, functional groups (e.g., methylene, carbonyl), total mass, and abundance ratio of MPs of different sizes. These were possibly caused by enzymes that were significantly influenced by crop types, abundance, and types of MPs in the soils. Maize growth decreased the mass of LDPE-MP and LDPP-MP by 28.7 and 32.7%, respectively, and 2% (w/w) of LDPP-MP addition in soil decreased mass of 9%, which was higher than that in 1% (w/w) LDPP-MP addition in soil. Soybean growth with SA decreased the mass of LDPE-MP and LDPP-MP by 36.6 and 20.7%, respectively, than the control treatment (CK). Compared with CK, both crop growth and SA changed the abundance of MPs of different sizes and decreased the mean size of MPs. The LDPE-MP could be more easily degraded by enzymes in the soils compared to LDPP-MP when the MP size was smaller with surface roughness. Generally, both maize and soybean growth can accelerate MP change in soils, and MP change process was mainly determined by SA, MP types, and the dose effect of MP.
在自然环境中,微塑料(MPs)通过物理化学和生物过程的降解取决于土壤中的酶,并且受到作物生长和秸秆添加(SA)的严重影响。然而,作物生长和秸秆添加如何影响土壤中微塑料的降解仍不清楚。在本研究中,测定了过氧化氢酶和蔗糖酶,并使用体视显微镜结合显微红外光谱和扫描电子显微镜(SEM),在室外盆栽试验中检测了 Mollisols 土壤中作物生长(玉米和大豆,添加和不添加 SA,1%和 2% MPs)后低密度聚乙烯微塑料(LDPE-MP)和低密度聚丙烯微塑料(LDPP-MP)的形态和数量。结果表明,作物生长改变了微塑料的形态、官能团(如亚甲基、羰基)、总质量以及不同尺寸微塑料的丰度比。这些可能是由土壤中受作物类型、丰度和微塑料类型显著影响的酶引起的。玉米生长分别使 LDPE-MP 和 LDPP-MP 的质量降低了 28.7%和 32.7%,土壤中添加 2%(w/w)的 LDPP-MP 使质量降低了 9%,高于土壤中添加 1%(w/w)LDPP-MP 的情况。与对照处理(CK)相比,添加 SA 的大豆生长分别使 LDPE-MP 和 LDPP-MP 的质量降低了 36.6%和 20.7%。与 CK 相比,作物生长和 SA 都改变了不同尺寸微塑料的丰度,并减小了微塑料的平均尺寸。当微塑料尺寸较小且表面粗糙时,与 LDPP-MP 相比,LDPE-MP 更容易被土壤中的酶降解。一般来说,玉米和大豆生长都能加速土壤中微塑料的变化,微塑料变化过程主要由 SA、微塑料类型和微塑料的剂量效应决定。