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Abiotic versus biotic immobilization of inorganic nitrogen in sediment as a potential pathway of nitrogen sequestration from coastal marine ecosystems

机译:沉积物中无机氮的非生物固定与生物固定,作为从沿海海洋生态系统固存氮的潜在途径

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摘要

Dissolved inorganic nitrogen (DIN), such as NO2- and NH4+, is known to react abiotically with organic matter to form organic N under specific conditions. However, the contribution of abiotic processes to the dynamics of DIN in marine environments has not been sufficiently evaluated. In this study, I demonstrated using N-15-labeled tracers that abiotic immobilization of DIN (particularly NO2-) occurred in coastal marine sediments after samples were autoclaved or treated with HgCl2, and compared it with the biotic immobilization (bacterial assimilation) of DIN in terms of reaction rate, produet yield, and the degradability of the organic N produced. Abiotic and biotic immobilization of N from DIN into solid sediment occurred within a period of days to a few weeks. NH4+, NO2-, and NO3- were significantly immobilized by biotic processes in the sediment investigated, although microbial dissimilatory reduction seemed to be the primary sink for NO2- and NO3-. In contrast, only NO2- was significantly immobilized in the sediment by abiotic processes. Abiotic immobilization of NO2- apparently obeyed first-order kinetics when the concentration of NO2- was <200 mu M. Decomposition experiments with natural sedimentary bacteria demonstrated that organic N formed biotically from NH4+ and abiotically from NO2- was operationally separated into a readily decomposable fraction and a refractory fraction. The refractory fraction of immobilized N ranged from 22% to 68% and was apparently dependent on the physical nature of the sediment (e.g., specific surface area), rather than whether it had been produced biotically or abiotically. This observation suggested that abiotically immobilized N can be preserved in sediment to a similar extent, and by similar mechanisms, as biotically produced organic N.
机译:已知溶解的无机氮(DIN)(例如NO2-和NH4 +)在特定条件下会与有机物发生非生物反应以形成有机N。但是,尚未充分评估非生物过程对海洋环境中DIN动力学的贡献。在这项研究中,我证明了使用N-15标记示踪剂将样品高压灭菌或用HgCl2处理后,沿海生物沉积物中发生了DIN的非生物固定化(尤其是NO2-),并将其与DIN的生物固定化(细菌吸收)进行了比较。在反应速率,产物收率和所产生的有机氮的可降解性方面。将DIN中的N非生物和生物固定在固体沉淀物中的过程在几天至几周的时间内发生。尽管微生物异化还原似乎是NO2-和NO3-的主要汇流区,但通过生物过程将NH4 +,NO2-和NO3-固定在了沉积物中。相比之下,非生物过程仅将NO2-明显地固定在沉积物中。当NO2-的浓度小于200μM时,NO2-的非生物固定化显然遵循一级动力学。天然沉积细菌的分解实验表明,由NH4 +通过生物方式形成的有机氮和从NO2-通过非生物方式形成的有机氮可分离为易于分解的馏分。和难熔部分。固定氮的耐火分数范围为22%至68%,显然取决于沉积物的物理性质(例如比表面积),而不是生物或非生物方式产生的。该观察结果表明,非生物固定化氮可以通过生物产生的有机氮,以相似的程度和通过类似的机理保存在沉积物中。

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