• Title/Summary/Keyword: Coagulation Diagram

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Pollutant Removal and Characteristic of Floc by Alum Coagulation (응집 현상에 따른 오염물질 제거 및 입자 형태 특성: Alum을 사용한 경우)

  • Moon, Byung-Hyun;Kim, Seung-Hyun;Lee, Hyang-In
    • Journal of Korean Society of Environmental Engineers
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    • v.22 no.7
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    • pp.1263-1271
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    • 2000
  • This study investigated the floc structure and removal of turbidity and organic matter by alum coagulation. Results of this study indicated that sweep floc and charge neutralization area were shifted to more acidic region than that in the Amirtharajah's diagram. This was caused by organic matter present in the raw water. Removal regions of turbidity and organic matter were generally overlapped. However, organic matters was removed better at lower pH than turbidity. Floc structure was characterized by measuring fractal dimension and volume diameter using AIA and SALLS. SALLS method was found to be more reliable than AIA method. Floes in sweep floc region had larger size and fractal dimension than flocs in charge neutralization region. As pollutant removal increased, larger fractal dimension and size of floc were measured.

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Theory of Coagulation(II) -The (Relative) Insignificance of G in Flocculation- (응집의 이론(II) -플록형성에서의 G값의 의의-)

  • Han, Moo Young
    • Journal of Korean Society of Water and Wastewater
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    • v.9 no.4
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    • pp.63-72
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    • 1995
  • The mean velocity gradient, G, has been used as a principal design and operation parameter for flocculation unit. This paper questions that significance. The physical and qualitative meaning of collision efficiency factors of each transport mechanism (Brownian motion, fluid shear, and differential sedimentation) are reviewed. The overall collision frequency function is calculated by summing up the collision frequency function of each mechanism. In the collision of two particles of different size, a diagram showing the dominant region in which each mechanism is important is developed and the meaning of the diagram is discussed. The primary ramification of this curvilinear, heterodisperse approach is that G is found to be not nearly so important. Previous experimental work in which the role of G has been examined is reviewed in light of this finding.

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Morphology of Membranes Formed from Polysulfone/Polyethersulfone/N-methyl-2-pyrrolidone/Water System by Immersion Precipitation

  • Baik, Ki-Jun;Kim, Je-Young;Lee, Jae-Sung;Kim, Sung-Chul;Lee, Hwan-Kwang
    • Macromolecular Research
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    • v.9 no.5
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    • pp.285-291
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    • 2001
  • The polysulfone(PSf)/polyethersulfone(PES) blend membranes were prepared by an immersion precipitation method. N-methyl-2-pyrrolidone(NMP) was used as a solvent and water as a nonsolvent. The composition of the coagulation bath and the dope polymer concentration as well as the blend ratio of two polymers were varied. The membrane morphologies were interpreted on the basis of the phase diagram of the PSf/PES/NMP/water system. As the solvent content in the coagulation bath increased in the single polymer system, the number of macrovoids decreased and the morphology was changed from finger-like to cellular structure. In the given bath condition phase separation occurs earlier for the solutions of PSf/PES blend than for those of single polymer. A horizontally layered structure and horizontal protuberances inside the macrovoid were observed for the membranes formed from PSf/PES blend solutions. This peculiar structure formation can be interpreted by a PSf-rich/PES-rich phase separation followed by a polymer-rich/polymer-lean phase separation during the exchange of solvent and nonsolvent.

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Molecular Size Distributions of NOM in Conventional and Advanced Water Treatment Processes (기존수처리 공정 및 고도정수처리 공정에서 NOM의 분자크기 분포 변화)

  • Choi, Il-Hwan;Jung, Yu-Jin
    • Journal of Korean Society on Water Environment
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    • v.24 no.6
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    • pp.682-689
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    • 2008
  • The purpose of this study was to find out the variation between molecular size distribution (MSD) of natural organic matter (NOM) in raw waters after different water treatment processes like conventional process (coagulation, flocculation, filtration) followed by advanced oxidation process (ozonation, GAC adsorption). The MSD of NOM of Suji pilot plant were determined by Liquid Chromatography-Organic Carbon Detection (LC-OCD) which is a kine of high-performance size-exclusion chromatography (HPSEC) with nondispersive infrared (NDIR) detector and $UV_{254}$ detector. Five distinct fractions were generally separated from water samples with the Toyopearl HW-50S column, using 28 mmol phosphate buffer at pH 6.58 as an eluent. Large and intermediate humic fractions were the most dominant fractions in surface water. High molecular weight (HMW) matter was clearly easier to remove in coagulation and clarification than low molecular weight (LMW) matter. Water treatment processes removed the two largest fractions almost completely shifting the MSD towards smaller molecular size in DW. No more distinct variation of MSD was observed by ozone process after sand filtration but the SUVA value were obviously reduced during increase of the ozone doses. UVD results and HS-Diagram demonstrate that ozone induce not the variation of molecular size of humic substance but change the bond structure from aromatic rings or double bonds to single bond. Granular activated carbon (GAC) filtration removed 8~9% of organic compounds and showed better adsorption property for small MSD than large one.

Principle of Sensor Systems by using a Quartz Crystal and Their Applications (수정진동자를 이용한 센서시스템의 원리와 응용)

  • Kim, Jong-Min;Chang, Sang-Mok;Kim, Woo-Sik
    • Korean Chemical Engineering Research
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    • v.47 no.6
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    • pp.655-668
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    • 2009
  • The principle and applications of quartz crystal sensors based on the three basic concepts for mass, viscosity, and viscoelastic changes are reviewed. In the general discussion the basic principle of quartz crystal and realization of a resonant frequency-resonant resistance diagram are described in detail. As examples of their applications, gas sensing with a carbon-coated quartz crystal, determination of the blood coagulation factor, an electrochemical analysis and crystallization analysis are reported. The possibility of developing new biosensors and chemical sensors is discussed on the basis of these results.