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生物 Fenton 工艺 - 淡水有机碳矿化的一种可能机制。

Biogenic Fenton process - A possible mechanism for the mineralization of organic carbon in fresh waters.

机构信息

Department of Biological and Environmental Science, University of Jyväskylä, 40014, Jyväskylä, Finland; Lammi Biological Station, University of Helsinki, 16900, Lammi, Finland.

Department of Biological and Environmental Science, University of Jyväskylä, 40014, Jyväskylä, Finland; School of Environmental & Municipal Engineering, Qingdao University of Technology, 266033, Qingdao, China.

出版信息

Water Res. 2021 Jan 1;188:116483. doi: 10.1016/j.watres.2020.116483. Epub 2020 Sep 30.

Abstract

To explore the mechanisms that mineralize poorly bioavailable natural organic carbon (OC), we measured the mineralization of OC in two lake waters over long-term experiments (up to 623 days) at different pH and iron (Fe) levels. Both the microbial and photochemical mineralization of OC was higher at pH acidified to 4 than at the ambient pH 5 or an elevated pH 6. During 244 days, microbes mineralized up to 60% of OC in the 10-µm filtrates of lake water and more than 27% in the 1-µm filtrates indicating that large-sized microbes/grazers enhance the mineralization of OC. A reactivity continuum model indicated that the acidification stimulated the microbial mineralization of OC especially in the later (>weeks) phases of experiment when the bioavailability of OC was poor. The reactive oxygen species produced by light or microbial metabolism could have contributed to the mineralization of poorly bioavailable OC through photochemical and biogenic Fenton processes catalyzed by the indigenous Fe in lake water. When Fe was introduced to artificial lake water to the concentration found in the study lakes, it increased the densities of bacteria growing on solid phase extracted dissolved organic matter and in a larger extent at low pH 4 than at pH 5. Our results suggest that in addition to the photochemical Fenton process (photo-Fenton), microbes can transfer poorly bioavailable OC into labile forms and CO through extracellular Fe-catalyzed reactions (i.e., biogenic Fenton process).

摘要

为了探索能够矿化生物利用度较差的天然有机碳(OC)的机制,我们在不同 pH 值和铁(Fe)水平下,通过长期实验(长达 623 天)测量了两种湖水 OC 的矿化作用。OC 的微生物矿化和光化学矿化在酸化至 pH4 时均高于环境 pH5 或升高的 pH6。在 244 天内,微生物矿化了湖水中 10μm 滤过物中高达 60%的 OC,在 1μm 滤过物中矿化了超过 27%的 OC,这表明较大尺寸的微生物/食草动物能够促进 OC 的矿化。反应连续统模型表明,酸化刺激了 OC 的微生物矿化,尤其是在实验后期(>数周),当 OC 的生物利用度较差时。光或微生物代谢产生的活性氧可能通过光化学和生物 Fenton 过程促进了生物利用度较差的 OC 的矿化,这些过程由湖水中的天然 Fe 催化。当 Fe 被引入人工湖水至研究湖中发现的浓度时,它增加了在固相提取溶解有机质上生长的细菌的密度,并且在 pH4 下比在 pH5 下的增加程度更大。我们的结果表明,除了光化学 Fenton 过程(photo-Fenton)之外,微生物还可以通过细胞外 Fe 催化的反应(即生物 Fenton 过程)将生物利用度较差的 OC 转化为不稳定的形式和 CO。

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