期刊文献+

藻类絮凝体形态学特征及其与气浮的关系研究 被引量:9

Morphological Characteristics of Algae Floc and Its Relation with Flotation
下载PDF
导出
摘要 采用聚合氯化铝(PAC)作为混凝药剂,利用混凝-气浮技术去除水中铜绿微囊藻(MA),用图像法对絮凝体的分形维数进行测定,分析不同混凝条件下的气浮除藻效果以及PAC-MA絮凝体的形态学特征,并探讨两者的关系.结果表明,在快速混合搅拌强度和时间分别为500 s^-1和1 min,回流比为10%条件下,PAC最佳投药量范围为5.6-9.8 mg/L Al2O3,最佳点为8.4 mg/LAl2O3;最佳的絮凝反应搅拌强度范围为50-80 s^-1,最佳点为50 s^-1;最佳的絮凝时间范围为5-8 min;投药量、絮凝反应搅拌强度及时间对PAC-MA絮凝体形态有着显著影响,在最佳混凝条件下,絮凝体的二维分形维数D2较小,在1.168 8-1.235 7之间,相对应的絮凝体的平均粒径较大,在300- 00μm之间;在适当的混凝条件下,结构疏松,枝杈较多,尺寸较大的PAC-MA絮凝体与气泡粘附效果好,容易气浮去除. Microcysits aeruginosa (MA) was removed by polyaluminium chloride (PAC) in the coagulation-flotation process. The test studied removing effect and morphological characteristics of PAC-MA flocs in the different coagulation conditions and discussed the correlation of them. Fractal dimension was measured by image analysis. The results indicate that the best range in dosage, stirring strength and time of flocculation reaction are respectively 5.6 - 9.8 mg/L AlE 03, 50 - 80 s ^-1 and 5 - 8 min in the condition of mixing stirring strength of 500 s ^-1 , mixing time of 1 min, circulate ratio of 10%. The dosage, stirring strength and time of flocculation reaction influenced the form of flocs remarkably. Moreover the range of fractal dimension D2 is between 1.168 8 and 1.235 7, and average diameters vary between 300 μm and 500 μm with the best flocculation condition. The flocs with the looser structure, the bigger diameter variation and more branches can adhere to bubbles more easily.
出处 《环境科学》 EI CAS CSCD 北大核心 2008年第3期688-695,共8页 Environmental Science
基金 国家高技术研究发展计划(863)项目(2002AA601140)
关键词 混凝-气浮 PAC-MA絮凝体 图像法 形态学 分形维数 coagulation-flotation PAC-MA floc image analysis morphology fractal dimension
  • 相关文献

参考文献17

  • 1Lee D G, Bonnet J S, Garton L S, et al. Modeling coagulation kinetics ineorporating fractal theories: comparison with observed data [J]. Water Research, 2002, 36(4) : 1056-1066. 被引量:1
  • 2Bushell G C, Yan Y D, Woodfield D, et al. On techniques for the measurement of the mass fractal dimension of aggregates [ J ]. Advances in Colloid Interface Science, 2002, 95( 1 ) : 1-50. 被引量:1
  • 3Wu R M, Lee D J, Waite T D, et al. Multilevel structure of sludge flocs[J]. Journal of Colloid and Interface Science, 2002,252 (2) : 383-392. 被引量:1
  • 4Waite T D, Cleaver J K, Beattie J K. Aggregation kinetics and fractal structure of γ-alumina assemblages[J]. Journal of Colloid and Interface Science, 2001, 241(2): 333-339. 被引量:1
  • 5金鹏康,王晓昌.腐殖酸絮凝体的形态学特征和混凝化学条件[J].环境科学学报,2001,21(S1):23-29. 被引量:41
  • 6Li D, Ganczarczyk J. Fractal geometry of particle aggregates generated in water and wastewater treatment processes [ J ]. Environmental Science and Technology, 1989,23 ( 11 ) : 1385-1389. 被引量:1
  • 7Jiang Q, Logan B E. Fractal dimensions determined from steady - state size distribution [J ]. Environmental Science and Technology, 1991, 25(12) : 2031-2038. 被引量:1
  • 8王晓昌,丹保宪仁.絮凝体形态学和密度的探讨——Ⅰ.从絮凝体分形构造谈起[J].环境科学学报,2000,20(3):257-262. 被引量:85
  • 9王毅力,李大鹏,解明曙.絮凝形态学研究及进展[J].环境污染治理技术与设备,2003,4(10):1-9. 被引量:17
  • 10Chakraborti R K, Atknson J F, Van Benschoten J E. Characterization of alum floc by image analysis[ J]. Environmental Science and Technology, 2000, 34(18) : 3969-3976. 被引量:1

二级参考文献23

共引文献137

同被引文献89

引证文献9

二级引证文献19

相关作者

内容加载中请稍等...

相关机构

内容加载中请稍等...

相关主题

内容加载中请稍等...

浏览历史

内容加载中请稍等...
;
使用帮助 返回顶部