Effects of LDPE and PBAT plastics on soil organic carbon and carbon-enzymes: A mesocosm experiment under field conditions

IF 7.6 2区 环境科学与生态学 Q1 ENVIRONMENTAL SCIENCES Environmental Pollution Pub Date : 2024-09-14 DOI:10.1016/j.envpol.2024.124965
Xinkai Jia, Yu Yao, Gaowei Tan, Sha Xue, Mengjuan Liu, Darrell W.S. Tang, Violette Geissen, Xiaomei Yang
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Abstract

Although the effects of plastic residues on soil organic carbon (SOC) have been studied, variations in SOC and soil carbon-enzyme activities at different plant growth stages have been largely overlooked. There remains a knowledge gap on how various varieties of plastics affect SOC and carbon-enzyme activity dynamics during the different growing stages of plants. In this study, we conducted a mesocosm experiment under field conditions using low-density polyethylene and poly (butylene adipate-co-terephthalate) debris (LDPE-D and PBAT-D, 500–2000 μm (pieces), 0%, 0.05%, 0.1%, 0.2%, 0.5%, 1%, 2%), and low-density polyethylene microplastics (LDPE-M, 500–1000 μm (powder), 0%, 0.05%, 0.1%, 0.5%) to investigate SOC and C-enzyme activities (β-xylosidase, cellobiohydrolase, β-glucosidase) at the sowing, seedling, flowering and harvesting stages of soybean (). The results showed that SOC in the LDPE-D treatments significantly increased from the flowering to harvesting stage, by 12.69%–13.26% ( < 0.05), but significantly decreased in the 0.05% and 0.1% LDPE-M treatments from the sowing to seedling stage ( < 0.05). However, PBAT-D had no significant effect on SOC during the whole growing period. For C-enzyme activities, only LDPE-D treatments inhibited GH (17.22–38.56%), BG (46.7–66.53%) and CBH (13.19–23.16%), compared to treatment without plastic addition, from the flowering stage to harvesting stage. Meanwhile, C-enzyme activities and SOC responded nonmonotonically to plastic abundance and the impacts significantly varied among the growing stages, especially in treatments with PBAT-D ( < 0.05). These risks to soil organic carbon cycling are likely mediated by the effects of plastic contamination and degradation soil microbe. These effects are sensitive to plastic characteristics such as type, size, and shape, which, in turn, affect the biogeochemical and mechanical interactions involving plastic particles. Therefore, further research on the interactions between plastic degradation processes and the soil microbial community may provide better mechanistic understanding the effect of plastic contamination on soil organic carbon cycling.
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LDPE 和 PBAT 塑料对土壤有机碳和碳酶的影响:实地条件下的中观实验
尽管塑料残留物对土壤有机碳(SOC)的影响已被研究过,但植物不同生长阶段的 SOC 和土壤碳酶活性的变化却在很大程度上被忽视了。关于各种塑料如何影响植物不同生长阶段的 SOC 和碳酶活性动态,目前仍是一个知识空白。在本研究中,我们在野外条件下使用低密度聚乙烯和聚(己二酸丁二醇酯-对苯二甲酸丁二酯)碎片(LDPE-D 和 PBAT-D,500-2000 μm(块),0%,0.05%,0.1%,0.2%,0.5%、1%、2%)和低密度聚乙烯微塑料(LDPE-M,500-1000 μm(粉末),0%、0.05%、0.1%、0.5%)来研究大豆播种期、幼苗期、开花期和收获期的 SOC 和 C 酶(β-木糖苷酶、纤维生物水解酶、β-葡萄糖苷酶)活性。结果表明,LDPE-D 处理中的 SOC 从开花期到收获期显著增加了 12.69%-13.26% (< 0.05),但 0.05% 和 0.1% LDPE-M 处理中的 SOC 从播种期到苗期显著减少(< 0.05)。然而,在整个生长期,PBAT-D 对 SOC 没有明显影响。在 C 酶活性方面,与未添加塑料的处理相比,从开花期到采收期,只有 LDPE-D 处理对 GH(17.22%-38.56%)、BG(46.7%-66.53%)和 CBH(13.19%-23.16%)有抑制作用。同时,C-酶活性和 SOC 对塑料丰度的反应是非单调的,其影响在不同生长阶段有显著差异,尤其是在添加 PBAT-D 的处理中 ( < 0.05)。这些对土壤有机碳循环的风险可能是由塑料污染和降解土壤微生物的影响介导的。这些影响对塑料的类型、大小和形状等特性非常敏感,而这些特性又会影响塑料颗粒的生物地球化学和机械相互作用。因此,进一步研究塑料降解过程与土壤微生物群落之间的相互作用,可以更好地从机理上理解塑料污染对土壤有机碳循环的影响。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
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来源期刊
Environmental Pollution
Environmental Pollution 环境科学-环境科学
CiteScore
16.00
自引率
6.70%
发文量
2082
审稿时长
2.9 months
期刊介绍: Environmental Pollution is an international peer-reviewed journal that publishes high-quality research papers and review articles covering all aspects of environmental pollution and its impacts on ecosystems and human health. Subject areas include, but are not limited to: • Sources and occurrences of pollutants that are clearly defined and measured in environmental compartments, food and food-related items, and human bodies; • Interlinks between contaminant exposure and biological, ecological, and human health effects, including those of climate change; • Contaminants of emerging concerns (including but not limited to antibiotic resistant microorganisms or genes, microplastics/nanoplastics, electronic wastes, light, and noise) and/or their biological, ecological, or human health effects; • Laboratory and field studies on the remediation/mitigation of environmental pollution via new techniques and with clear links to biological, ecological, or human health effects; • Modeling of pollution processes, patterns, or trends that is of clear environmental and/or human health interest; • New techniques that measure and examine environmental occurrences, transport, behavior, and effects of pollutants within the environment or the laboratory, provided that they can be clearly used to address problems within regional or global environmental compartments.
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