College of Water Sciences, Beijing Normal University, Beijing 100875, China; National Engineering Laboratory for Lake Water Pollution Control and Ecological Restoration Technology, Research Center of Lake Eco-Environment, Chinese Research Academy of Environmental Sciences, Beijing 100012 China; State Key Laboratory of Environmental Criteria and Risk Assessment, Chinese Research Academy of Environmental Sciences, Beijing 100012 China.
College of Water Sciences, Beijing Normal University, Beijing 100875, China; National Engineering Laboratory for Lake Water Pollution Control and Ecological Restoration Technology, Research Center of Lake Eco-Environment, Chinese Research Academy of Environmental Sciences, Beijing 100012 China; State Key Laboratory of Environmental Criteria and Risk Assessment, Chinese Research Academy of Environmental Sciences, Beijing 100012 China.
J Hazard Mater. 2018 May 15;350:189-200. doi: 10.1016/j.jhazmat.2018.02.005. Epub 2018 Feb 7.
DGT (diffusive gradients in thin films) technique and DIFS (DGT induced fluxes in sediment) model are firstly designed for macrophyte-rhizobox system and in-situ macrophytes in Lake Erhai. Dynamics of phosphorus (P) transfer in Zizania latifolia (ZL) and Myriophyllum verticiilatur (MV) rhizosphere is revealed and phytoremediation performance for P in sediment is evaluated. Dynamic transfer process of P at DGT/sediment interface includes (i) diffusion flux and concentration gradients at DGT(root)/porewater interface leading to porewater concentration (C) depletion and (ii) P desorption from labile P pool in sediment solid to resupply C depletion. Fe-redox controlled P release from Fe-bound P (BD-P2) and then NHCl-P1 in rhizosphere sediment resupplies porewater depletion due to DGT (root) sink. K (labile P pool size in solid phase), r (resupply ratio) and kinetic exchange (Tc and k) lead to change characters of DIFS curves of (1) r against deployment time and (2) C (dissolved concentration) against distance at 24 h. They include two opposite types of "fast" and "slow" rate of resupplies. Sediment properties and DIFS parameters control P diffusion and resupply in rhizosphere sediment. Phytoremoval ability for sediment P in lake is estimated to be 23.4 (ZL) or 15.0 t a (MV) by "DGT-flux" method.
DGT(薄膜扩散梯度)技术和 DIFS(DGT 诱导的沉积物通量)模型最初是为大型植物-根盒系统和洱海原位大型植物设计的。揭示了磷(P)在菰(ZL)和竹叶眼子菜(MV)根际中的迁移动力学,并评价了沉积物中 P 的植物修复性能。DGT/沉积物界面上 P 的动态迁移过程包括:(i)DGT(根)/孔隙水界面上的扩散通量和浓度梯度导致孔隙水浓度(C)耗尽,(ii)从沉积物固相中的可利用 P 库中解吸 P 以补充 C 耗尽。铁氧化还原控制 P 从 Fe 结合态 P(BD-P2)和根际沉积物中的 NHCl-P1 释放,从而补充 DGT(根)吸收造成的孔隙水消耗。K(固相中可利用 P 库的大小)、r(补给比)和动力学交换(Tc 和 k)导致(1)r 与部署时间和(2)C(溶解浓度)与 24 h 时距离的 DIFS 曲线的变化特征。它们包括两种相反类型的“快速”和“缓慢”补给速率。沉积物性质和 DIFS 参数控制根际沉积物中 P 的扩散和补给。通过“DGT 通量”法估计湖泊沉积物中 P 的植物去除能力为 23.4(ZL)或 15.0 t a(MV)。