REGULATION OPTIMIZATION OF TIDAL RIVER GATES FOR WATER ENVIRONMENT IMPROVEMENT IN THE RIVER BASINS:A CASE STUDY ON INDEPENDENT POLDERS' RIVER NETWORKS
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摘要: 以我国南方某5个相互独立的圩内河网为研究对象,针对感潮河段的特征建立水动力水质耦合模型,比较不同闸门调度策略下的水质改善效果。结果表明:1)圩内河网应在大潮期进行换水,相对小潮期换水最多可缩短7 h的水力停留时间。以示踪剂工况结果为依据,针对进出水闸门距离较短河网,采用单向流调度策略启闭闸门,相对往复流最多可缩短14.18 h的水力停留时间;针对进出水闸门距离较长的河网,采用开启双侧闸门进水从中心排河排水的往复流闸门启闭策略,相对单向流调度策略最多可缩短3.18 h的水力停留时间。2)水质结果表明,应先利用水系连通方式打通断头河,并采用前述的闸门调度策略,最终本片区河网平均水质达到GB 3838-2002《地表水环境质量标准》Ⅳ类水的断面比例增长了7.3%。研究结果为基于水动力水质改善不同地理特征圩内潮汐河网的闸门调度提供了参考。Abstract: This study took five independent polders’ river networks in southern China as the research objects, established a hydrodynamic water quality coupling model according to the characteristics of the tidal reaches, and compared the water quality improvement effects under different gate scheduling strategies. The results showed that: 1) for the polders’ river network, water exchange should be carried out during the spring tide period, and the hydraulic retention time could be shortened by up to 7 hours compared with the neap tide period. Based on the results of the tracer operating condition, for the river network with a short distance between the inlet and outlet gates, the one-way flow scheduling strategy should be used to operate the gate, which could shorten the hydraulic retention time by up to 14.18 hours compared with reciprocal flows. For the river network with a long distance between the inlet and outlet gates, the reciprocal flows operation strategy of opening the gates on both sides to discharge water from the central drainage could shorten the hydraulic retention time by 3.18 hours, compared with the one-way flow scheduling strategy. 2) the results of water quality showed that the deadhead river should be opened up first by water system connection, and then the aforementioned gate scheduling strategy should be adopted. The proportion of the polders’ river network sections whose water quality reached class IV increased by 7.3%. The results of this paper can provide a reference for the improvement of hydrodynamic and water quality for gate scheduling of tidal river networks in different geographical features.
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[1] YAO Y J, YIN H L, LI S. The computation approach for water environmental capacity in tidal river network[J]. Journal of Hydrodynamics, 2006, 18(3):273-277. [2] CHEN L N, HAN L X, LING H, et al. Allocating water environmental capacity to meet water quality control by considering both point and non-point source pollution using a mathematical model:tidal river network case study[J]. Water, 2019, 11(5):1-900. [3] CHEN L N, HAN L X, TAN J Y, et al. Water environmental capacity calculated based on point and non-point source pollution emission intensity under water quality assurance rates in a tidal river network area[J]. International Journal of Environmental Research and Public Health, 2019, 16:1-9. [4] 江涛,朱淑兰,张强,等.潮汐河网闸泵联合调度的水环境效应数值模拟[J].水利学报,2011,42(4):388-395. [5] 尹海龙,林夷媛,徐祖信,等.潮汐河网地区雨天黑臭治理数学模型研究[J].水动力学研究与进展,2020,35(1):113-120. [6] 马克,涂新军,陈晓宏.闸控河网区水闸运行的水流水质相应模拟[J].水文,2021,41(6):66-72. [7] 陈奕,蔡辉艺,蒋艳君.黑臭水体治理形势下的潮汐河网地区纳潮引水调度周期研究[J].给水排水,2018,44(11):40-44. [8] 李丹,曾慧,张明珠,等.潮汐河网区污染排放与水质响应关系的模拟研究[J].中国农村水利水电,2021,1(1):44-49. [9] 曾一川,曾会国,袁伟皓,等.长江口入海通道水质综合分析与模型预测[J].环境工程,2021,39(5):95-102. [10] 李张卿,宋桂杰,李晓.深圳市白花河黑臭水体综合治理技术探讨[J].给水排水,2018,54(7):47-50. [11] 赵也,汤钟,曾胜.基于模型评估的黑臭水体综合治理方案目标可达性分析[J].中国给水排水,2020,36(13):73-82. [12] 马超,唐志波,徐奎,等.平原地区城市河网水环境改善的补水调度策略研究:以天津市中心城区河网为例[J].南水北调与水利科技,2017,15(6):81-87. [13] 宋荣华.上海横沙岛水资源调度方式数值模拟研究[J].中国水运,2020(1):118-120. [14] 陈振宇,周刚,白静.基于HEC_RAS模型的平原河网区水环境容量研究[J].环境保护科学,2021,47(4):30-37. [15] 刘翔,李淼,周方,等.城市水环境综合整治工程原理与系统方法[J]. 环境工程,2019,37(10):1-5. [16] 田凯达,刘晓薇,王慧,等. MIKE11模型在合肥市十五里河水质改善研究中的应用[J].水文,2019,39(4):18-23. [17] 王航.浅谈城市河道水环境综合整治[J].环境工程,2018,36(6):42-46. [18] 刘江,陈国鼎,曾继军,等.基于MIKE对流扩散和生态耦合模型的鸭子荡水库水质模拟研究[J].水利与建筑工程学报,2018,16(1):118-122. [19] 郑国栋,顾立忠,李虎成.浅析明渠非恒定流计算Abbott六点中心格式[J].广东水利水电,2010,1(4):15-18. [20] 崔明荣.活动边界抛物型方程迎风差分格式[J].山东大学学报(自然科学版),1998,33(3):241-247.
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