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木质素降解酶和芬顿样反应在云芝降解腐殖酸中的作用

Involvement of ligninolytic enzymes and Fenton-like reaction in humic acid degradation by Trametes sp.

机构信息

Department of Soil and Water Sciences, The Robert H. Smith Faculty of Agriculture, Food and Environment, The Hebrew University of Jerusalem, PO Box 12, Rehovot 76100, Israel.

出版信息

Appl Microbiol Biotechnol. 2011 Aug;91(4):1131-40. doi: 10.1007/s00253-011-3300-9. Epub 2011 May 4.

Abstract

Trametes sp. M23, isolated from biosolids compost was found to decompose humic acids (HA). A low N (LN) medium (C/N, 53) provided suitable conditions for HA degradation, whereas in a high N (HN) medium (C/N, 10), HA was not degraded. In the absence of Mn(2+), HA degradation was similar to that in Mn(2+)-containing medium. In contrast, MnP activity was significantly affected by Mn(2+). Laccase activity exhibited a negative correlation to HA degradation, while LiP activity was not detected. Thus, ligninolytic enzymes activity could provide only a partial explanation for the HA-degradation mechanism. The decolorization of two dyes, Orange II and Brilliant Blue R250, was also determined. Similar to HA degradation, under LN conditions, decolorization occurred independently of the presence of Mn(2+). We investigated the possible involvement of a Fenton-like reaction in HA degradation. The addition of DMSO, an OH-radical scavenger, to LN media resulted in a significant decrease in HA bleaching. The rate of extracellular Fe(3+) reduction was much higher in the LN vs. HN medium. In addition, the rate of reduction was even higher in the presence of HA in the medium. In vitro HA bleaching in non-inoculated media was observed with H(2)O(2) amendment to a final concentration of 200 mM (obtained by 50 mM amendments for 4 days) and Fe(2+) (36 mM). After 4 days of incubation, HA decolorization was similar to the biological treatment. These results support our hypothesis that a Fenton-like reaction is involved in HA degradation by Trametes sp. M23.

摘要

从生物固体堆肥中分离出的 Trametes sp. M23 被发现能够分解腐殖酸 (HA)。低氮 (LN) 培养基 (C/N,53) 为 HA 降解提供了适宜的条件,而在高氮 (HN) 培养基 (C/N,10) 中,HA 则不会被降解。在没有 Mn(2+)的情况下,HA 的降解与含有 Mn(2+)的培养基中的降解相似。相比之下,MnP 活性受到 Mn(2+)的显著影响。漆酶活性与 HA 降解呈负相关,而 LiP 活性则未检测到。因此,木质素降解酶活性只能为 HA 降解机制提供部分解释。两种染料(橙色 II 和亮蓝 R250)的脱色也被测定。与 HA 降解相似,在 LN 条件下,脱色的发生独立于 Mn(2+)的存在。我们研究了 Fenton 样反应在 HA 降解中的可能参与。在 LN 培养基中添加 DMSO,一种 OH-自由基清除剂,导致 HA 漂白显著减少。在 LN 与 HN 培养基中,细胞外 Fe(3+)的还原速率要高得多。此外,在培养基中存在 HA 的情况下,还原速率甚至更高。在非接种培养基中进行体外 HA 漂白时,添加终浓度为 200 mM 的 H2O2(通过 50 mM 试剂添加 4 天获得)和 Fe(2+)(36 mM)。孵育 4 天后,HA 的脱色与生物处理相似。这些结果支持我们的假设,即 Fenton 样反应参与了 Trametes sp. M23 对 HA 的降解。

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