RESEARCH ON ENHANCED COAGULATION TECHNOLOGY BASED ON DYNAMIC MIXING FOR WATERWORKS
-
摘要: 为探究动态混合的强化混凝效果及影响因素,借助在某给水处理厂设置的动态混合、静态混合和管式混合中试试验装置,开展了混凝效果对比试验。结果表明:综合混凝效果顺序为动态混合>静态混合>管式混合,其中动态混合的浑浊度及色度去除率分别可达91%、95%,絮体形态较大且密实,利于沉降,静态混合和管式混合的絮体相对较松散;动态混合及其他混合方式对CODMn、TOC的去除率仅为20%~35%;动态混合在较低PAC投加量(20 mg/L)条件下,对低温低浊水的处理效果较另两类混合方式更好,浊度去除率仍可达90%。流量、转速、涡轮转角、管道-涡轮直径比、安装距离等因素对动态混合影响研究表明,应用动态混合方式处理小流量工况时应搭配小转速且距絮凝池较近的安装距离,大流量则相反;建议选择较小涡轮转角(30°~45°),涡轮直径比对混凝效果无显著影响。Abstract: To explore the effect of dynamic mixing on strengthening coagulation and its influencing factors, a comparative test of the coagulation effect was carried out with the assistance of dynamic mixing, static mixing, and tube mixing pilot test equipment in a water supply plant. The results showed that the comprehensive flocculation effect was ranked as dynamic mixing>static mixing>tube mixing. The removal rates of turbidity and chroma of dynamic mixing could reach 91% and 95%, respectively. The floc form was large and dense, which was conducive to sedimentation. The floc of static mixing and tube mixing was relatively loose. The removal rate of CODMn and TOC by dynamic mixing and other mixing methods was only in a range of 20% to 35%. Dynamic mixing had a better treatment effect on low temperature and turbidity water at a lower PAC dosage (20 mg/L), and the turbidity removal rate can still reach 90%. The study on the influence of flow rate, speed, turbine angle, pipe-turbine diameter ratio, installation distance, and other factors on dynamic mixing showed that the application of the dynamic mixing method should be combined with a low speed and a short installation distance from the flocculation tank in the treatment of small flow rate, while the opposite is true for a large flow rate. It is recommended to choose a smaller turbine angle (30° to 45°), and the turbine diameter ratio has no significant influence on the coagulation effect.
-
[1] 郭文娟. 西安某净水厂一期工程混凝:沉淀工艺设计[J]. 给水排水, 2016, 52(1): 22-25. [2] 赵安瑜, 沈晓锋. 机械搅拌频率对混凝的影响研究[J]. 给水排水, 2013, 49(1): 41-43. [3] 陈燚, 笪跃武, 袁君, 等. 水厂处理工艺中不同设计的实践效果评估:以锡东水厂为例[J]. 净水技术, 2021, 40(10): 167-172. [4] 苏芸. 乌鲁木齐市南郊净水厂工程设计[D].长春:吉林大学, 2016. [5] 甄忠元. 可调式混凝管混凝涡旋水动力学研究[D].杭州:杭州电子科技大学, 2015. [6] JIANG J Q. The role of coagulation in water treatment[J]. Current Opinion in Chemical Engineering, 2015(8):36-44. [7] 苏俊峰, 邱治国, 朱侃苏. 机械搅拌频率对混凝效果的影响研究[J]. 中国给水排水, 2017, 33(1): 68-70. [8] 乔海兵, 李兰西, 朱慧杰, 等. 新生态铁处理低温低浊水静态和连续絮凝工艺研究[J]. 环境工程, 2018, 36(7): 67-70,106. [9] 包雨云, 黄雄斌, 施力田, 等. 机械搅拌用于水处理中混凝过程的研究[J]. 水处理技术, 2003(1): 28-31. [10] 刘百仓, 黄尔, 鲁金凤, 等. 混凝工艺水力条件的优化与絮体尺寸特性的研究[J]. 环境工程学报, 2010, 4(9): 1968-1972. [11] 徐佩. 四种混凝剂混凝性能曲线图谱测绘及其性能分析[D].合肥:安徽工业大学, 2019. [12] 肖刚, 袁本松, 贺晓娟, 等. 地表水厂絮凝池改造及运行优化研究[J]. 给水排水, 2018, 54(10): 19-22. [13] 国家市场监督管理总局,国家标准化管理委员会.生活饮用水卫生标准: GB 5749—2022[S]. 北京:中国标准出版社,2022. [14] 梁梓庆, 柯水洲, 袁辉洲, 等. 三种典型混凝剂处理带正电胶粒絮体性能的影响因素[J]. 环境工程, 2018, 36(9): 36-40. [15] 梁娟, 杨青, 丁然, 等. 混凝剂投加量对水质及絮体尺寸变化特性的影响[J]. 给水排水, 2012, 48(增刊1): 5-9. [16] KAN C C, HUANG C P, PAN J R S. Time requirement for rapid-mixing in coagulation[J]. Colloids and Surfaces A-Physicochemical and Engineering Aspects, 2002, 203(1/2/3): 1-9. [17] 黄廷林, 赵阳, 文刚. 西北地区低温低浊地表水气浮工艺中试研究[J]. 给水排水, 2015, 51(11): 41-45. [18] 彭雨瑶, 李攀武, 高晓波, 等. 黄土絮凝剂对沙湖水质净化及溶解性有机质的去除[J]. 环境工程, 2023, 41(5): 140-146. [19] 王雪松, 黄继国, 李绪谦, 等. 高效混凝处理浑江微污染水的中试试验[J]. 吉林大学学报(工学版), 2008(3): 662-665.
点击查看大图
计量
- 文章访问数: 46
- HTML全文浏览量: 3
- PDF下载量: 1
- 被引次数: 0