Macrogenomic analysis of tolerance and degradation mechanisms of polycyclic aromatic hydrocarbon in carbon and nitrogen metabolic pathways and associated bacterial communities during endogenous partial denitrification

IF 11.4 1区 环境科学与生态学 Q1 ENGINEERING, ENVIRONMENTAL Water Research Pub Date : 2024-10-15 DOI:10.1016/j.watres.2024.122628
Baodan Jin, Ye Liu, Fukun Zhao, Yeyu Yan, Zhixuan Bai, Jingjing Du, Yuanqian Xu, Chuang Ma, Jiantao Ji
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Abstract

The effective production of NO2-N through endogenous partial denitrification (EPD) provides a promising perspective for the broader adoption and application of anaerobic ammonia oxidation. However, the accumulation of polycyclic aromatic hydrocarbons (PAHs) in the environment may worsen the operational challenges of the EPD system. This study evaluated the resilience of the EPD system to the toxic impacts of phenanthrene (PHE) and anthracene (ANT) through macrogenomic analysis. A control group was maintained under identical conditions for comparison. The results revealed that PHE and ANT had a relatively minimal impact on NO3-N transformation and organic matter removal but significantly affected PO43−-P removal and NO2-N accumulation in the EPD process. The PHE system achieved a higher NO2-N accumulation, with a maximum NO3-N to NO2-N conversion ratio of 90.08%. In contrast, the ANT system exhibited higher efficiency in the PO43−-P removal, achieving a peak removal rate of 74.94%. Macrogenomic analysis revealed that PAHs significantly enriched both denitrifying glycogen-accumulating organisms (including Candidatus_Competibacter) and denitrifying polyphosphate-accumulating organisms (such as Thauera, Candidatus_Contendobacter, and Candidatus_Accumulibacter). This enrichment stabilized these organisms, facilitating NO2-N accumulation and PO43−-P removal. Metabolic pathway analysis indicated that PHE promoted the enrichment of NO3-N reductase and inhibited NO2-N reductase activity. However, ANT stimulated oxidative phosphorylation and the phosphate cycle. Moreover, PAH metabolites enhanced the expression of key genes encoding succinate dehydrogenase and isocitrate dehydrogenase in the tricarboxylic acid cycle within the EPD process, leading to increase the synthesis and utilization of acetyl coenzyme-A. Notably, significant differences were observed between the effects of PHE and ANT on these metabolic processes. This study provides new methods for treating PAH-containing wastewater through the combination of EPD and anaerobic ammonia oxidation.

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内源部分脱氮过程中多环芳烃在碳氮代谢途径和相关细菌群落中的耐受性和降解机制的宏基因组分析
通过内源部分反硝化作用(EPD)有效地产生氮氧化物(NO2--N),为更广泛地采用和应用厌氧氨氧化技术提供了一个前景广阔的前景。然而,环境中多环芳烃(PAHs)的积累可能会加剧 EPD 系统的运行挑战。本研究通过宏基因组分析评估了 EPD 系统对菲(PHE)和蒽(ANT)毒性影响的适应能力。同时还在相同条件下保留了一个对照组进行比较。结果表明,PHE 和 ANT 对 NO3-N 转化和有机物去除的影响相对较小,但对 EPD 过程中 PO43-P 的去除和 NO2-N 的积累有显著影响。PHE 系统实现了更高的 NO2-N 积累,NO3-N 与 NO2-N 的最大转化率为 90.08%。相比之下,ANT 系统对 PO43-P 的去除效率更高,达到了 74.94% 的峰值去除率。宏基因组分析表明,多环芳烃显著富集了反硝化糖原累积型生物(包括Competibacter念珠菌)和反硝化聚磷酸酯累积型生物(如Thauera、Contendobacter念珠菌和Accumulibacter念珠菌)。这种富集稳定了这些生物,促进了 NO2-N 的积累和 PO43-P 的去除。代谢途径分析表明,PHE促进了NO3--N还原酶的富集,抑制了NO2--N还原酶的活性。然而,ANT能刺激氧化磷酸化和磷酸循环。此外,多环芳烃代谢物还能增强 EPD 过程中三羧酸循环中编码琥珀酸脱氢酶和异柠檬酸脱氢酶的关键基因的表达,从而增加乙酰辅酶 A 的合成和利用。值得注意的是,PHE 和 ANT 对这些代谢过程的影响存在明显差异。这项研究为通过结合 EPD 和厌氧氨氧化处理含 PAH 废水提供了新方法。
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来源期刊
Water Research
Water Research 环境科学-工程:环境
CiteScore
20.80
自引率
9.40%
发文量
1307
审稿时长
38 days
期刊介绍: Water Research, along with its open access companion journal Water Research X, serves as a platform for publishing original research papers covering various aspects of the science and technology related to the anthropogenic water cycle, water quality, and its management worldwide. The audience targeted by the journal comprises biologists, chemical engineers, chemists, civil engineers, environmental engineers, limnologists, and microbiologists. The scope of the journal include: •Treatment processes for water and wastewaters (municipal, agricultural, industrial, and on-site treatment), including resource recovery and residuals management; •Urban hydrology including sewer systems, stormwater management, and green infrastructure; •Drinking water treatment and distribution; •Potable and non-potable water reuse; •Sanitation, public health, and risk assessment; •Anaerobic digestion, solid and hazardous waste management, including source characterization and the effects and control of leachates and gaseous emissions; •Contaminants (chemical, microbial, anthropogenic particles such as nanoparticles or microplastics) and related water quality sensing, monitoring, fate, and assessment; •Anthropogenic impacts on inland, tidal, coastal and urban waters, focusing on surface and ground waters, and point and non-point sources of pollution; •Environmental restoration, linked to surface water, groundwater and groundwater remediation; •Analysis of the interfaces between sediments and water, and between water and atmosphere, focusing specifically on anthropogenic impacts; •Mathematical modelling, systems analysis, machine learning, and beneficial use of big data related to the anthropogenic water cycle; •Socio-economic, policy, and regulations studies.
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