闸控湖泊水生植物恢复的敏感生态水位研究以固城湖为例

Research on the sensitive ecological water level for the restoration of aquatic plants in gate-controlled lakes: a case study of Gucheng Lake

  • 摘要: 水位变化对湖泊水生植物生长发育有着重要影响。分析了固城湖2006—2023年水位、2013—2021年水生植物变化特征,探讨了固城湖水生植物对水位变化的响应关系,提出了基于水生植物恢复的闸控湖泊敏感期生态水位。研究结果表明:(1)2006—2011年固城湖平均水位为8.47 m;2012年新建出入湖水闸投入使用,为提高水资源利用量,固城湖汛后蓄水位由8.50 m提高到9.50 m,2012—2015年平均水位达到9.69 m;2016年以来,受芜申航道通航影响,湖泊水位年内波动较大,2016—2023年平均水位为8.98 m。(2)2013—2021年固城湖水生植物种类呈下降趋势;优势种由菹草、竹叶眼子菜、荇菜转变为菹草,水生植物群落逐渐趋向单一化,存在由草型湖泊向藻型湖泊转变的趋势。(3)固城湖3—4月、12月—次年4月水位超过9.00 m的天数与5月份水生植物生物量呈显著负相关(p≤0.05),水生植物萌发的关键时期保持较高的水位状态,是水生植物生物量明显下降的重要原因。(4)2024年水碧桥泵站的建成启用为进一步加强固城湖水资源精细化调度提供客观条件,为恢复水生植物多样性,初步拟定7.50 m作为固城湖水生植物萌发的敏感生态水位,湖泊水位在敏感期(3—4月)可根据水生植物萌发情况在7.50~8.50 m之间适当调整,使之与湖泊水资源利用及通航需要相协调。建议加强湖区水生态监测,进一步确定水生植物恢复的关键时期和重点区域;加强水利枢纽工程调度管理,制定精细化的调度方案,营造有利于恢复水生植物的水位变化过程,统筹实现防洪、供水、灌溉、生态、航运等多个目标。

     

    Abstract: Water level fluctuations have a significant impact on the growth and development of aquatic plants in lakes. This study analyzes the water level data of Gucheng Lake from 2006 to 2023 and the aquatic plant variations from 2013 to 2021, investigating the relationship between aquatic plants' responses and water level changes. It proposes a sensitive ecological water level for gate-controlled lakes based on the restoration of aquatic plants. The findings show that: (1) The average water level of Gucheng Lake from 2006 to 2011 was 8.47 m; in 2012, a new inlet and outlet sluice was put into operation, increasing the post-flood storage water level from 8.50 m to 9.50 m. From 2012 to 2015, the average water level was 9.69 m. Since 2016, due to the influence of the Wushan Navigation Channel, the lake's water level fluctuated greatly within the year, with an average of 8.98 m from 2016 to 2023. (2) Between 2013 and 2021, the species diversity of aquatic plants in Gucheng Lake showed a decreasing trend; dominant species shifted from Potamogeton pectinatus, Potamogeton crispus, and Najas marina to Potamogeton pectinatus, leading to a gradual simplification of the aquatic plant community and a trend towards a transition from macrophyte-dominated to algae-dominated lakes. (3) The number of days with water levels exceeding 9.00 m in March–April and December–April was significantly negatively correlated (p≤0.05) with the biomass of aquatic plants in May. Maintaining higher water levels during the critical germination period of aquatic plants is a key factor contributing to the substantial decline in biomass. (4) The completion and operation of the Shuibi Bridge Pump Station in 2024 will provide objective conditions for further refining the water resource management of Gucheng Lake, and a preliminary sensitive ecological water level of 7.50 m is proposed for the germination of aquatic plants. During the sensitive period (March–April), the water level can be adjusted between 7.50 m and 8.50 m according to the plant germination status to balance water resource utilization and navigation requirements. It is recommended to strengthen aquatic ecological monitoring, further determine key restoration periods and priority areas for aquatic plants, and enhance the management of water conservancy projects to create favorable water level changes that support aquatic plant restoration, achieving a balanced approach to flood control, water supply, irrigation, ecology, and navigation

     

/

返回文章
返回