Li Na, Li Yong, Lou Ruitao, Xu Hong, Saeed Laraib
Key Laboratory of Integrated Regulation and Resources Development on Shallow Lakes, Ministry of Education, Hohai University, Nanjing, 210098, China; College of Environment, Hohai University, Nanjing, 210098, China.
Key Laboratory of Integrated Regulation and Resources Development on Shallow Lakes, Ministry of Education, Hohai University, Nanjing, 210098, China; College of Environment, Hohai University, Nanjing, 210098, China.
J Environ Manage. 2023 Jun 15;336:117623. doi: 10.1016/j.jenvman.2023.117623. Epub 2023 Mar 7.
Nitrate-reducing ferrous [Fe(II)]-oxidizing (NRFO) has been reported from lake sediments as a natural reduction pathway. However, the effects of the contents of Fe(II) and sediment organic carbon (SOC) on the NRFO process still remain unclear. In this study, the influences of Fe(II) and organic carbon on nitrate reduction were analyzed quantitatively at two typical seasonal temperatures (25 °C representing summers and 5 °C for winters) by conducting a series of batch incubation experiments, using surficial sediments at the western zone of Lake Taihu (Eastern China). Results showed that Fe(II) greatly promoted NO‾-N reduction by denitrification (DNF) and dissimilatory nitrate reduction to ammonium (DNRA) processes at high-temperature (25 °C, representing summer season). As Fe (II) increased (e.g., Fe(II)/NO‾ = 4), the promotion effect on NO‾-N reduction was weakened, but on the other side, the DNRA process was enhanced. In comparison, the NO‾-N reduction rate obviously decreased at low-temperature (5 °C, representing the winter season). NRFO in sediments mainly belongs to biological rather than abiotic processes. A relatively high SOC content apparently increased the rate of NO‾-N reduction (r = 0.023-0.053 mM/d), particularly on the heterotrophic NRFO. It is interesting that the Fe(II) consistently remained active in the nitrate reduction processes no matter whether SOC was sufficient in the sediment, particularly at high-temperature. Overall, the combining effects of both Fe(II) and SOC in surficial sediments made a great contribution towards NO‾-N reduction and N removal in a lake system. These results provide a better understanding and estimation of N transformation in sediments of the aquatic ecosystem under different environmental conditions.
据报道,湖泊沉积物中存在硝酸盐还原亚铁[Fe(II)]氧化(NRFO)这一自然还原途径。然而,Fe(II)含量和沉积物有机碳(SOC)对NRFO过程的影响仍不清楚。在本研究中,通过开展一系列批次培养实验,利用中国东部太湖西部区域的表层沉积物,在两个典型季节温度(25℃代表夏季,5℃代表冬季)下,定量分析了Fe(II)和有机碳对硝酸盐还原的影响。结果表明,在高温(25℃,代表夏季)下,Fe(II)极大地促进了反硝化作用(DNF)和异化硝酸盐还原为铵(DNRA)过程对NO₃⁻-N的还原。随着Fe(II)增加(例如,Fe(II)/NO₃⁻ = 4),对NO₃⁻-N还原的促进作用减弱,但另一方面,DNRA过程增强。相比之下,在低温(5℃,代表冬季)下,NO₃⁻-N还原速率明显下降。沉积物中的NRFO主要属于生物过程而非非生物过程。相对较高的SOC含量明显提高了NO₃⁻-N还原速率(r = 0.023 - 0.053 mM/d),特别是对异养NRFO。有趣的是,无论沉积物中SOC是否充足,Fe(II)在硝酸盐还原过程中始终保持活性,尤其是在高温下。总体而言,表层沉积物中Fe(II)和SOC的综合作用对湖泊系统中NO₃⁻-N还原和氮去除有很大贡献。这些结果有助于更好地理解和估算不同环境条件下水生生态系统沉积物中的氮转化。