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Continuous Hydrologic and Water Quality Monitoring of Vernal Ponds
Published on: November 13, 2017
Unraveling contrasting summer endogenous nutrient release regimes in Two Karst Plateau Lakes: Evidence from
Ye Zheng1, Kun Wang2, Jianyin Huang3
1State Key Laboratory of Lake Watershed Science for Water Security, Nanjing Institute of Geography and Limnology, Chinese Academy of Sciences, Nanjing 211135, China; Key Laboratory for Lake Pollution Control of the Ministry of Ecology and Environment, National Engineering Laboratory for Lake Pollution Control and Ecological Restoration, Chinese Research Academy of Environmental Sciences, Beijing 100012, China.
Abstract:
High-altitude karst plateau lakes are increasingly threatened by eutrophication, yet limited knowledge of microscale sediment-water interface (SWI) biogeochemical processes constrains mechanistic understanding and management of internal nutrient loading. Here, we coupled colorimetric diffusive gradients/equilibrium in thin films (DGT/DET) with microelectrode profiling to co-map labile phosphorus (P) and ammonium (NH4+-N) at sub-millimeter resolution across the SWI of two contrasting karst lakes (deep, oligotrophic Lake Fuxian versus shallow, eutrophic Lake Dianchi) during the severe eutrophication period. 2D images revealed steep near-SWI gradients and discrete hotspots where labile P and NH4+-N were co-enriched within overlapping depth intervals, indicating a close microscale association between P and N mobilization. Generally, Lake Dianchi displayed markedly higher near-SWI labile P and NH4+-N concentrations and diffusive fluxes as compared with Lake Fuxian. Typically, Lake Fuxian maintained a relatively stable weakly alkaline pH and deeper O2 penetration across the SWI, together with low labile nutrient pools and Ca-P-dominated sediments, suggesting stronger near-interface nutrient retention. While Lake Dianchi appeared to be more strongly influenced by coupled water-column and sediment forcing. High OM loading likely altered the localized geochemical microenvironment through porewater acidification and the concurrent accumulation of Fe(II) and S(-II), processes that may have synergistically facilitated the interfacial co-release of P and N by weakening the oxidative barrier. These findings clarify the distinction between lake-scale ecological vulnerability to nutrient enrichment and local SWI-scale geochemical stabilization and reveal contrasting summer SWI nutrient migration patterns that can inform sediment-derived nutrient risk diagnosis in fragile karst plateau lakes.

