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王洪铸. 引江济湖的主要目的不是稀释污染物,而是修复自然水文节律及自净能力[J]. 水生生物学报, 2021, 45(3): 692-699. DOI: 10.7541/2021.2020.286
引用本文: 王洪铸. 引江济湖的主要目的不是稀释污染物,而是修复自然水文节律及自净能力[J]. 水生生物学报, 2021, 45(3): 692-699. DOI: 10.7541/2021.2020.286
WANG Hong-Zhu. THE MAIN TARGET OF CONNECTION OF LAKES WITH RIVERS IS NOT TO DILUTE POLLUTANTS, BUT TO REHABILITATE NATURAL HYDROLOGICAL REGIMES AND SELF-PURIFICATION FUNCTION[J]. ACTA HYDROBIOLOGICA SINICA, 2021, 45(3): 692-699. DOI: 10.7541/2021.2020.286
Citation: WANG Hong-Zhu. THE MAIN TARGET OF CONNECTION OF LAKES WITH RIVERS IS NOT TO DILUTE POLLUTANTS, BUT TO REHABILITATE NATURAL HYDROLOGICAL REGIMES AND SELF-PURIFICATION FUNCTION[J]. ACTA HYDROBIOLOGICA SINICA, 2021, 45(3): 692-699. DOI: 10.7541/2021.2020.286

引江济湖的主要目的不是稀释污染物,而是修复自然水文节律及自净能力

THE MAIN TARGET OF CONNECTION OF LAKES WITH RIVERS IS NOT TO DILUTE POLLUTANTS, BUT TO REHABILITATE NATURAL HYDROLOGICAL REGIMES AND SELF-PURIFICATION FUNCTION

  • 摘要: 引水(江河等)济湖是常提的湖泊富营养化治理措施, 但实际效果十分有限。围绕“如何科学实施江湖连通”这个问题, 文章首先通过案例分析和模型模拟, 指出引水冲释的效果取决于是否有足够的低磷源水, 而这个条件往往难以满足。然后, 比较阻隔湖泊与通江湖泊的水质, 分析总结长江通江湖泊水质良好的机制, 即自然水位波动利于水生植被发育、湖滨带季节性变浅和干涸利于分解吸附污染物、湖水泥沙多且流动导致浮游藻类对营养的利用效率下降、生态复杂性较高, 指出江河与湖泊的连通工程应以修复自由水文连通和自然水位波动为主要目的, 从而增强湖泊自净能力, 并给出实施建议。文章对国内外引水济湖工程进行了系统综述, 提出了科学的新连通模式, 对有效实施江河与湖泊的连通工程具有重要指导价值。

     

    Abstract: Water diversion from rivers to lakes is popularly considered as a measure to control lake eutrophication, but the actual efficacy is quite limited in general. How to connect lakes with rivers in a scientific way? To answer this question, first, I analyze 5 diversion cases in China and other countries, and simulate effect of adding water using Vollenweider’s model. The results show that improving water quality by dilution depends upon whether there is large amount of input water with total phosphorus concentrations much lower than original inflow ones, but such a premise is generally difficult to meet. Second, I compare water quality of lakes disconnected and connected with the Yangtze mainstem, and find that chlorophyl a concentration of water in disconnected lakes are increased by 0.7—2.4 times when total phosphorus concentrations are in the same levels. The mechanisms of better water quality of connected lakes are fourfold, i.e., the natural water level fluctuation promotes vegetation development, seasonal trying-up and shallowing of lakeshore promotes pollutants decomposition and adsorption, turbid flowing water results in lower efficiency of nutrient utilization by phytoplankton, and the ecological complexity is higher with more heterogeneous habitats, higher biodiversity, and more complex food webs. Last, I point out that setting a scientific feasible target is the very basis to implement a river-lake connection project correctly. If the aim is to dilute pollutants, enough clean water is needed, and this can only be realized for smaller waterbodies. If the aim is to wash out phytoplankton, the flushing rate should be higher than specific growth rates of dominated algae, reaching 10%—20%/d, and this is also only feasible for smaller waterbodies. As for most lakes, in particular, shallow ones, connection of lakes with rivers should aim mainly to rehabilitate free hydrological connectivity and natural water level regimes, and then to enhance self-purification function. Such a mode costs a lesser amount of water, but reaches the best effect. This review provides important guidance for river-lake connection projects.

     

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