School of Environmental Studies, China University of Geosciences, Wuhan, 430074, China; State Key Laboratory of Biogeology and Environmental Geology, China University of Geosciences, Wuhan, 430074, China.
School of Environmental Studies, China University of Geosciences, Wuhan, 430074, China; State Key Laboratory of Biogeology and Environmental Geology, China University of Geosciences, Wuhan, 430074, China.
Environ Pollut. 2020 Aug;263(Pt A):114441. doi: 10.1016/j.envpol.2020.114441. Epub 2020 Apr 2.
Organic carbon (OC) can help control greenhouse gas emissions by participating in biogeochemical reactions and preventing the migration of contaminants in groundwater systems. The association of OC with Fe (Iron) oxide minerals plays a significant role in stabilizing OC and regulating the biogeochemical cycles of OC on the earth's surface. Reclaiming farmland from lakes changes an original lake into a wetland, but the destiny of Fe bound-OC in the underlying aquitard during this process has been poorly understood. The mechanisms of migration and transformation of Fe bound-OC were investigated in subsurface aquitard sediments of three typical boreholes in the Chen Lake wetland, central China. The Fe bound-OC content in the natural sedimentary conditions (borehole A), transition area (borehole B), and intensive reclamation area (borehole C) were 0.17-3.87, 0.28-3.98 and 0.13-7.08 mg g, respectively. The reclamation changed the redox, water, and infiltration conditions of the surface environment, resulting in a transformation of Fe oxides phases, and then cause the change of content and structure of Fe bound-OC. The fresh organic matter provided by undecomposed crops causes oxygen- and nitrogen-rich compounds to combine with Fe oxides extensively through adsorption, resulting in higher δC values of Fe bound-OC than non-Fe bound-OC. Fe bound-OC has strong resistance to biodegradation. The Fe bound-OC: total OC ratios generated by adsorption and coprecipitation on the surface layer (0 to -3.5 m) of borehole C was 10.37% and 18.86%, 6.92% and 12.46% higher than those of boreholes A and B, respectively. Coprecipitation has a stronger OC-binding ability and enriches more carboxylates and aromatics, while adsorption gradually assumed a dominant position in OC-Fe interaction in deep aquitard. The reduction dissolution of Fe oxide causes Fe bound-OC to transfer into pore water, leading to an increase of Fe ion and dissolved OC in deep strata.
有机碳(OC)可以通过参与生物地球化学反应和防止地下水中污染物的迁移来控制温室气体排放。OC 与铁(Fe)氧化物矿物的结合在稳定 OC 和调节地球表面 OC 的生物地球化学循环方面起着重要作用。将湖泊开垦为农田会将原始湖泊转变为湿地,但在这个过程中,底层隔水层中结合态 Fe 的 OC 的命运还知之甚少。本研究通过对中国中部陈湖湿地的三个典型钻孔的地下隔水层沉积物进行研究,探讨了结合态 OC 的迁移和转化机制。在自然沉积条件(钻孔 A)、过渡区(钻孔 B)和集约化开垦区(钻孔 C)中,结合态 OC 的含量分别为 0.17-3.87、0.28-3.98 和 0.13-7.08 mg g。开垦改变了地表环境的氧化还原、水和渗透条件,导致 Fe 氧化物相的转化,进而引起结合态 OC 含量和结构的变化。未分解作物提供的新鲜有机物质导致富氧和富氮化合物通过吸附与 Fe 氧化物广泛结合,导致结合态 OC 的 δC 值高于非结合态 OC。结合态 OC 具有很强的抗生物降解性。在钻孔 C 的表层(0 到-3.5 m),吸附和共沉淀产生的结合态 OC:总 OC 比值分别比钻孔 A 和 B 高 10.37%和 18.86%,6.92%和 12.46%。共沉淀对 OC 的结合能力更强,使更多的羧酸盐和芳烃富集成结合态 OC,而在深部隔水层中,吸附逐渐在 OC-Fe 相互作用中占据主导地位。Fe 氧化物的还原溶解导致结合态 OC 转移到孔隙水中,导致深部地层中 Fe 离子和溶解 OC 的增加。