基于Phillips滞留模型的洪泽湖生态缓冲带边界划定

    Delimiting of Ecological Buffer Zone in Hongze Lake Based on Phillips Retention Model

    • 摘要: 生态缓冲带在统筹湖泊生态环境治理与修复方面具有重要作用。以面源污染阻控为目标, 利用Phillips滞留模型, 结合Sentinel-2卫星数据, 对洪泽湖生态缓冲带边界进行划定, 并通过景观生态风险评价比较未划定、固定和非固定宽度缓冲带对生态环境的贡献。结果表明: (1)洪泽湖生态缓冲带宽度集中分布在2~60 m, 其占比为85.50%, 且在该区间内分布较均匀。(2)参考《河湖生态缓冲带保护修复技术指南》, 将湖滨带分为植被良好型、农田型、养殖塘型、村落型、城镇型和河口型6种类型, 并分别提出57.62、34.05、32.79、40.18、38.99和22.99 m的优化生态缓冲带宽度值。(3)单一地表覆盖类型构建下, 非固定宽度生态缓冲带对洪泽湖湖滨带生态风险具有降低作用, 而固定宽度缓冲带的生态风险却有所提升。影响洪泽湖生态缓冲带缓冲效率的关键因子为坡度和土壤条件, 因此地方政府划定缓冲带时应适当进行地形调整和土壤改良, 优先考虑非固定宽度的缓冲带划定, 并在确定固定宽度时及时进行生态风险评估。

       

      Abstract: Ecological buffer zone (EBZ) of lakes plays substantial role in intercepting pollutants and ecological restoration. In this study, based on the Sentinel-2 satellite data, the boundary of ecological buffer zone of Hongze Lake was delimited by using Phillips detention model targeting at non-point pollutions control. Finally, comparisons were conducted on the environmental performances of un-delimited, fixed-width and non-fixed width buffer zones by applying landscape ecological risk assessment. The results show that: (1) The width of the EBZ of Hongze Lake ranged from 2 to 60 m, accounting for 85.50% of the total. (2) Following the Technical guide for the protection and restoration of ecological buffer zones of rivers and lakes, the lakeshore was divided into six groups including: well-vegetated type, farmland-dominated type, aquaculture-dominated type, village-dominated type, urban-dominated type and estuarine-dominated type. The optimizing width values of EBZ for the aforementioned type of lakeshore with the goal of non-point sources pollution control were 57.62, 34.05, 32.79, 40.18, 38.99, and 22.99 m, respectively. (3) With the construction of a single landcover type, the non-fixed-width EBZ demonstrated a reducing effect on the ecological risk (ER) of Hongze lakeshore, whereas the ER of the fixed-width was estimated to be increased. The key factors affecting environmental performance of EBZ in Hongze Lake are slope and soil conditions. Therefore, it is essential for further implementation of EBZ that local government should pay attention to appropriate topographic adjustment and improvement in soil condition with the priority of delimiting of non-fixed width buffer zones. Meanwhile, ecological risk assessment should be conducted when delimiting fixed width buffer zone.

       

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