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雨水花园是海绵城市建设中应用较为广泛的技术措施之一。为研究雨水花园对雨水径流热污染的控制效果和影响因素,以典型构造的雨水花园试验装置为研究对象,采用人工模拟雨水径流的方法,系统研究了降雨过程中雨水花园各构造层的温度变化规律,以及雨水径流温度、降雨强度对热污染控制效果的影响。结果表明:雨水花园可以有效控制雨水径流热污染,当重现期从1 a一遇增大到10 a一遇时,雨水径流温度的削减量从17.4℃减小到10.5℃,热量削减率从32.42%减少到14.54%;当雨水径流温度从22℃升高至35℃时,温度的削减量从6.3℃增加到20.5℃,热量削减率从20.67%增大到32.65%。此外,雨水花园出水温度受填料层温度影响较大,靠近出水口附近的填料层温度越低,雨水花园出水温度越低。因此,降雨强度越小、填料层温度越低、雨水径流温度越高时,雨水花园对雨水径流热污染的控制效果越显著。
Abstract:Rain garden is one of the more widely used measures in the construction of sponge cities. In order to study the control effect and influencing factors of rain garden on the thermal pollution of stormwater runoff, the rain garden experimental apparatus with typical structure is taken as the research object, and artificial simulation of stormwater runoff is used to systematically study the characteristics of temperature changing of rain garden during the rainfall process, and the impact of stormwater runoff temperature and rainfall intensity on the control effect of thermal pollution. The results show that the rain garden can effectively control the thermal pollution of stormwater runoff, and when the return period increases from 1 a to 10 a, the reduction value of runoff temperature in rain garden is reduced from 17.4 ℃ to 10.5 ℃, and the heat reduction rate is reduced from 32.42% to 14.54%. When the temperature of stormwater runoff increases from 22 ℃ to 35 ℃, the temperature reduction value increases from 6.3 ℃ to 20.5 ℃, and the heat reduction rate increases from 20.67% to 32.65%. In addition, the effluent temperature of the rain garden is affected by the temperature of the bottom filler layer. The lower the temperature of the media near the outlet, the lower the temperature of effluent. Therefore, the smaller the rainfall intensity, the lower the media temperature and the higher the runoff temperature, the more significant the control effect of the rain garden on the runoff thermal pollution.
[1] 蒋新波,杨昌智,施周.基于防止热污染的湖南地区滞流水体热承载能力研究[J].安全与环境学报,2018,18(2):727- 733.
[2] 姜礼燔.热冲击对鱼类影响的研究[J].中国水产科学,2000,7(2):77- 81.
[3] CHERRY D S,DICKSON K L,JR J C,et al.Preferred,avoided,and lethal temperatures of fish during rising temperature conditions[J].Journal of the Fisheries Research Board of Canada,2011,34(2):239- 246.
[4] 徐镜波.热排放对水库溶解氧的影响[J].环境科学学报,1993(3):339- 346.
[5] 许志良,黄向阳,吴姗姗.水源热泵系统尾水排放对湖泊富营养化的影响[J].长江大学学报(自科版),2014,11(5):57- 61.
[6] 李小静,李俊奇,戚海军,等.城市雨水径流热污染及其缓解措施研究进展[J].水利水电科技进展,2013,33(1):89- 94.
[7] KERTESZ R,SANSALONE J.Hydrologic transport of thermal energy from pavement[J].Journal of Environmental Engineering,2014,140(8):04014028.
[8] 魏新渝,王一川,张琨,等.电厂温排水对水生生物影响评价综述[J].水生态学杂志,2018,39(2):1- 10.
[9] 胡秋明,王景刚,鲍玲玲.湖水源热泵温排水影响研究[J].环境科学与技术,2016,39(8):164- 170.
[10] 刘伯娟,李娜,熊坤杨.低影响开发的措施体系构建及其效果研究[J].水利水电技术,2016,47(8):19- 22.
[11] JONES M P,HUNT W F.Effect of Bioretention on Runoff Temperature in Trout Sensitive Regions[C]//World Environmental & Water Resources Congress,2008.
[12] JONES M P,HUNT W F.Bioretention impact on runoff temperature in trout sensitive waters[J].Journal of Environmental Engineering,2009,135(8):577- 585.
[13] ROSEEN R M,DIGENNARO N,WATTS A,et al.Preliminary results of the examination of thermal impacts from stormwater BMPs.[C]//World Environmental & Water Resources Congress,2010.
[14] 户园凌.低影响开发雨水系统综合效益的分析研究[D].北京:北京建筑工程学院,2012
[15] 郭娉婷.生物滞留设施生态水文效应研究[D].北京:北京建筑大学,2015.
基本信息:
DOI:10.13928/j.cnki.wrahe.2020.09.018
中图分类号:X57
引用信息:
[1]徐玮曈,王建龙,武彦杰,等.雨水花园对雨水径流热污染控制效果试验研究[J],2020,51(09):162-167.DOI:10.13928/j.cnki.wrahe.2020.09.018.
基金信息:
国家水体污染控制与治理科技重大专项(2017ZX07103-002)