DOCSLIB.ORG

Water Chemistry and Pretreatment Colloidal and Particulate Tech

Total Page：16

File Type：pdf, Size：1020Kb

Download full-text PDF Read full-text
Water Chemistry and Pretreatment Colloidal and Particulate Tech Tech Manual Excerpt Water Chemistry and Pretreatment Colloidal and Particulate Other Methods Methods to prevent colloidal fouling are discussed in the following documents: l Colloidal and Particulate (Form No. 45-D01559-en) l Media Filtration (Form No. 45-D01560-en) l Oxidation–Filtration (Form No. 45-D01561-en) l In-Line Filtration (Form No. 45-D01562-en) l Microfiltration/Ultrafiltration (Form No. 45-D01563-en) l Cartridge Microfiltration (Form No. 45-D01564-en) In addition, the following methods are available: Lime softening has already been described as a method for silica removal (Scale Control-Lime Softening (Form No. 45-D01549-en) ). Removal of iron and colloidal matter are further benefits. Strong acid cation exchange resin softening not only removes hardness, but it also removes low concentrations of iron and aluminum that otherwise could foul the membrane. Softened water is also known to exhibit a lower fouling tendency than unsoftened (hard) water because multivalent cations promote the adhesion of naturally occurring colloids, which are usually negatively charged. The ability to minimize iron depends on the Fe species present. Fe2+ and Fe3+ are substantially removed by the SAC resin and, if in excess of 0.05 ppm, have a tendency to foul the membrane and catalyze its degradation. Colloidal or organo-Fe-complexes are usually not removed at all and will pass through into the product water. Insoluble iron-oxides are, depending on their size, filtered out depending on the flowrate and bed-depth used. When dealing with higher concentration of ferrous iron, one needs special care to avoid ferric iron fouling. It was reported that addition of SMBS was able to prevent membrane fouling Antifoulants: certain scaling inhibitors, also called antifoulants, can handle iron. This pretreatment process can be used for relatively low concentrations of iron. Page 1 of 2 Form No. 45-D01565-en, Rev. 4 April 2020 Excerpt from FilmTec™ Reverse Osmosis Membranes Technical Manual (Form No. 45-D01504-en), Chapter 2, "Water Chemistry and Pretreatment." Have a question? Contact us at: All information set forth herein is for informational purposes only. This information is general information and may differ from that based on actual conditions. Customer is responsible for determining whether products and the information in this document are www.dupont.com/water/contact-us appropriate for Customer's use and for ensuring that Customer's workplace and disposal practices are in compliance with applicable laws and other government enactments. The product shown in this literature may not be available for sale and/or available in all geographies where DuPont is represented. The claims made may not have been approved for use in all countries. Please note that physical properties may vary depending on certain conditions and while operating conditions stated in this document are intended to lengthen product lifespan and/or improve product performance, it will ultimately depend on actual circumstances and is in no event a guarantee of achieving any specific results. DuPont assumes no obligation or liability for the information in this document. References to “DuPont” or the “Company” mean the DuPont legal entity selling the products to Customer unless otherwise expressly noted. NO WARRANTIES ARE GIVEN; ALL IMPLIED WARRANTIES OF MERCHANTABILITY OR FITNESS FOR A PARTICULAR PURPOSE ARE EXPRESSLY EXCLUDED. No freedom from infringement of any patent or trademark owned by DuPont or others is to be inferred. DuPont™, the DuPont Oval Logo, and all trademarks and service marks denoted with ™, ℠ or ® are owned by affiliates of DuPont de Nemours Inc. unless otherwise noted. © 2020 DuPont. Page 2 of 2 Form No. 45-D01565-en, Rev. 4 April 2020.
Load more

Recommended publications
  • Particle Separation and Fractionation by Microfiltration
    Particle separation and fractionation by microfiltration Promotor: Prof. Dr. Ir. R.M. Boom Hoogleraar Levensmiddelenproceskunde, Wageningen Universiteit Copromotoren: Dr. Ir. C.G.P.H. Schro¨en Universitair docent, sectie Proceskunde, Wageningen Universiteit Dr. Ir. R.G.M. van der Sman Universitair docent, sectie Proceskunde, Wageningen Universiteit Promotiecommissie: Prof. Dr. Ir. J.A.M. Kuipers Universiteit Twente Prof. Dr. Ir. M. Wessling Universiteit Twente Dr. Ir. A. van der Padt Royal Friesland Foods Prof. Dr. M.A. Cohen Stuart Wageningen Universiteit Janneke Kromkamp Particle separation and fractionation by microfiltration Scheiding en fractionering van deeltjes middels microfiltratie Proefschrift Ter verkrijging van de graad van doctor op gezag van de rector magnificus van Wageningen Universiteit, Prof.dr. M.J. Kropff, in het openbaar te verdedigen op dinsdag 6 september 2005 des namiddags te vier uur in de Aula. Particle separation and fractionation by microfiltration Janneke Kromkamp Thesis Wageningen University, The Netherlands, 2005 - with Dutch summary ISBN: 90-8504-239-9 Contents 1 Introduction 1 1.1 Membrane filtration 2 1.2 Microfiltration 2 1.3 Mass transport 5 1.4 Shear-induced diffusion 7 1.5 Research aim and outline 9 2 Lattice Boltzmann simulation of 2D and 3D non-Brownian suspensions in Couette flow 13 2.1 Introduction 14 2.2 Computer simulation method 15 2.2.1 Simulation of the fluid 15 2.2.2 Fluid-particle interactions 17 2.2.3 Accuracy of particle representation and particle-particle interactions 18 2.3 Single and pair particles
    [Show full text]
  • Mitigation of Membrane Fouling in Microfiltration
    MITIGATION OF MEMBRANE FOULING IN MICROFILTRATION & ULTRAFILTRATION OF ACTIVATED SLUDGE EFFLUENT FOR WATER REUSE A thesis submitted in fulfilment of the requirement for the degree of Doctor of Philosophy (PhD) Sy Thuy Nguyen Bachelor of Engineering (Chemical), RMIT University, Melbourne School of Civil, Environmental & Chemical Engineering Department of Chemical Engineering RMIT University, Melbourne, Australia December 2012 i DECLARATION I hereby declare that: the work presented in this thesis is my own work except where due acknowledgement has been made; the work has not been submitted previously, in whole or in part, to qualify for any other academic award; the content of the thesis is the result of work which has been carried out since the official commencement date of the approved research program Signed by Sy T. Nguyen ii ACKNOWLEDGEMENTS Firstly, I would like to thank Prof. Felicity Roddick, my senior supervisor, for giving me the opportunity to do a PhD in water science and technology and her scientific input in every stage of this work. I am also grateful to Dr John Harris and Dr Linhua Fan, my co-supervisors, for their ponderable advice and positive criticisms. The Australian Research Council (ARC) and RMIT University are acknowledged for providing the funding and research facilities to make this project and thesis possible. I also wish to thank the staff of the School of Civil, Environmental and Chemical Engineering, the Department of Applied Physics and the Department of Applied Chemistry, RMIT University, for the valuable academic, administrative and technical assistance. Lastly, my parents are thanked for the encouragement and support I most needed during the time this research was carried out.
    [Show full text]
  • Determination of Fouling Mechanisms for Ultrafiltration of Oily Wastewater
    DETERMINATION OF FOULING MECHANISMS FOR ULTRAFILTRATION OF OILY WASTEWATER A thesis submitted to the Division of Graduate Studies and Research of the University of Cincinnati in partial fulfillment of the requirements of the degree of MASTER OF SCIENCE (M.S.) in the Department of Chemical Engineering of the College of Engineering and Applied Science 2011 By Leila Safazadeh Haghighi BS Chemical Engineering, University Of Tehran, Tehran, Iran, 2008 Thesis Advisor and Committee Chair: Professor Rakesh Govind Abstract The use of Membrane technology is extensively increasing in water and wastewater treatment, food processing, chemical, biotechnological, and pharmaceutical industries because of their versatility, effectiveness, high removal capacity and ability to meet multiple treatment objectives. A common problem with using membranes is fouling, which results in increasing operating costs due to higher operating pressure losses, membrane downtime needed for cleaning, with associated production loss and manpower costs. In the literature, four different mechanisms for membrane fouling have been studied, which are complete pore blocking, internal pore blinding, partial pore bridging and cake filtration. Mathematical models have been developed for each of these fouling mechanisms. The objective of this thesis was to investigate the membrane fouling mechanisms for one porous and one dense membrane, during ultrafiltration of an emulsified industrial oily wastewater. An experimental system was designed, assembled and operated at the Ford Transmission Plant in Sharonville, Ohio, wherein ultrasonic baths were used for cleaning transmission parts before assembly. The oil wastewater, containing emulsified oils and cleaning chemicals was collected in a batch vessel and then pumped through a porous polyethersulfone, monolithic membrane, and through a dense cuproammonium cellulose membrane unit.
    [Show full text]
  • Application of Inorganic Ceramic Membrane in Wastewater Treatment: Membrane Fouling Control and Cleaning Procedure
    International Symposium on Material, Energy and Environment Engineering (ISM3E 2015) Application of Inorganic Ceramic Membrane in Wastewater Treatment: Membrane Fouling Control and Cleaning Procedure Yanjie Wei Key Laboratory of Environmental Protection in Water Transport Engineering Ministry of Communications, Tianjin Research Institute of Water Transport Engineering, Tianjin 300456, China Abstract. Using the inorganic ceramic membrane equipment for wastewater treatment, the transit membrane pressure (TMP) raises with membrane fouling, interception efficiency declines, and operation energy consumption increases. These issues have been the main problems to be solved in the technology development of inorganic ceramic membrane. Thus, it is necessary to analyze the membrane fouling process and formation mechanism, as well as propose strategy for retarding membrane fouling. Formation mechanism, control measures and cleaning procedure of membrane fouling were discussed in this paper, so as to provide evidence or reference for further popularization and application of inorganic ceramic membrane in wastewater treatment 1 Introduction bridging and become oil layer covering the membrane, resulting in severe blocking. Inorganic ceramic membrane has the advantages of high temperature resistance, high acid and alkali resistance, homogenous pore-size distribution, steady chemical 3 Research on Membrane Fouling property, high strength, large flux, long lifetime, anti- Control pollution, simple structure, small floor area, few matching equipment, easy installation, no chemical 3.1. Improvement of membrane properties additives, high operating efficiency, high management and automation, and so on. Thus, this technology has With the prefection of chemical compositon, stability and been applied in the wastewater treatment of food industry, hydrophilicity of membrane can be improved, filtration biochemical engineering, petrochemical industry, performance could be optimized, and operation energy mechanical metallurgy.
    [Show full text]
  • Membrane Filtration
    Membrane Filtration A membrane is a thin layer of semi-permeable material that separates substances when a driving force is applied across the membrane. Membrane processes are increasingly used for removal of bacteria, microorganisms, particulates, and natural organic material, which can impart color, tastes, and odors to water and react with disinfectants to form disinfection byproducts. As advancements are made in membrane production and module design, capital and operating costs continue to decline. The membrane processes discussed here are microfiltration (MF), ultrafiltration (UF), nanofiltration (NF), and reverse osmosis (RO). MICROFILTRATION Microfiltration is loosely defined as a membrane separation process using membranes with a pore size of approximately 0.03 to 10 micronas (1 micron = 0.0001 millimeter), a molecular weight cut-off (MWCO) of greater than 1000,000 daltons and a relatively low feed water operating pressure of approximately 100 to 400 kPa (15 to 60psi) Materials removed by MF include sand, silt, clays, Giardia lamblia and Crypotosporidium cysts, algae, and some bacterial species. MF is not an absolute barrier to viruses. However, when used in combination with disinfection, MF appears to control these microorganisms in water. There is a growing emphasis on limiting the concentrations and number of chemicals that are applied during water treatment. By physically removing the pathogens, membrane filtration can significantly reduce chemical addition, such as chlorination. Another application for the technology is for removal of natural synthetic organic matter to reduce fouling potential. In its normal operation, MF removes little or no organic matter; however, when pretreatment is applied, increased removal of organic material can occur.
    [Show full text]
  • The Safe Use of Cationic Flocculants with Reverse Osmosis Membranes
    Desalination and Water Treatment 6 (2009) 144–151 www.deswater.com 111 # 2009 Desalination Publications. All rights reserved The safe use of cationic flocculants with reverse osmosis membranes S.P. ChestersÃ, E.G. Darton, Silvia Gallego, F.D. Vigo Genesys International Limited, Unit 4, Ion Path, Road One, Winsford Industrial Estate, Winsford, Cheshire CW7 3RG, UK Tel. þ44 1372 741881; Fax þ44 1606 557440; emails: [email protected], [email protected], [email protected] Received 15 September 2008; accepted 20 April 2009 ABSTRACT Flocculants are used in combination with coagulants to agglomerate suspended particles for removal by filtration. This technique is used extensively in all types of surface waters to reduce the silt density index (SDI) and minimise membrane fouling. Although organic cationic floccu- lants are particularly effective, their widespread use in membrane applications is limited because of perceived problems with flocculant fouling at the membrane surface causing irreparable damage. Reference material from some of the major membrane manufacturers on the use of floc- culants is given. Autopsies show that more than 50% of membrane fouling is caused by inadequate, deficient or poorly operated pre-treatment systems. The Authors suggest that if the correct chemistry is con- sidered, the addition of an effective flocculant can be simple and safe. The paper discusses the use of cationic flocculants and the fouling process that occur at the membrane surface. The paper explains the types of coagulants and flocculants used and considers cationic flocculants and the way they function. Operational results when using a soluble polyquaternary amine flocculant (Genefloc GPF) developed by Genesys International Limited is presented.
    [Show full text]
  • A Review of Reverse Osmosis Membrane Fouling and Control Strategies Shanxue Jiang1, Yuening Li2, Bradley P
    A review of reverse osmosis membrane fouling and control strategies Shanxue Jiang1, Yuening Li2, Bradley P. Ladewig1* 1Barrer Centre, Department of Chemical Engineering, Imperial College London 2Department of Environmental Engineering, Nankai University *Corresponding author: Bradley P. Ladewig [email protected] Abstract Reverse osmosis (RO) membrane technology is one of the most important technologies for water treatment. However, membrane fouling is an inevitable issue. Membrane fouling leads to higher operating pressure, flux decline, frequent chemical cleaning and shorter membrane life. This paper reviews membrane fouling types and fouling control strategies, with a focus on the latest developments. The fundamentals of fouling are discussed in detail, including biofouling, organic fouling, inorganic fouling and colloidal fouling. Furthermore, fouling mitigation technologies are also discussed comprehensively. Pretreatment is widely used in practice to reduce the burden for the following RO operation while real time monitoring of RO has the advantage and potential of providing support for effective and efficient cleaning. Surface modification could slow down membrane fouling by changing surface properties such as surface smoothness and hydrophilicity, while novel membrane materials and synthesis processes build a promising future for the next generation of RO membranes with big advancements in fouling resistance. Especially in this review paper, statistical analysis is conducted where appropriate to reveal the research interests
    [Show full text]
  • Antifouling Membranes for Oily Wastewater Treatment: Interplay Between Wetting and Membrane Fouling
    Antifouling membranes for oily wastewater treatment: interplay between wetting and membrane fouling Shilin Huang1, Robin H. A. Ras2,3*, Xuelin Tian1* 1School of Materials Science and Engineering, Key Laboratory for Polymeric Composite & Functional Materials of Ministry of Education, Sun Yat-sen University, Guangzhou 510006, China 2Aalto University, School of Science, Department of Applied Physics, Puumiehenkuja 2, 02150 Espoo, Finland 3Aalto University, School of Chemical Engineering, Department of Bioproducts and Biosystems, Kemistintie 1, 02150 Espoo, Finland Email: [email protected], [email protected] Abstract Oily wastewater is an extensive source of pollution to soil and water, and its harmless treatment is of great importance for the protection of our aquatic ecosystems. Membrane filtration is highly desirable for removing oil from oily water because it has the advantages of energy efficiency, easy processing and low maintenance cost. However, membrane fouling during filtration leads to severe flux decline and impedes long-term operation of membranes in practical wastewater treatment. Membrane fouling includes reversible fouling and irreversible fouling. The fouling mechanisms have been explored based on classical fouling models, and on oil droplet behaviors (such as droplet deposition, accumulation, coalescence and wetting) on the membranes. Membrane fouling is dominated by droplet-membrane interaction, which is influenced by the properties of the membrane (e.g., surface chemistry, structure and charge) and the wastewater (e.g., compositions and concentrations) as well as the operation conditions. Typical membrane antifouling strategies, such as surface hydrophilization, zwitterionic polymer coating, photocatalytic decomposition and electrically enhanced antifouling are reviewed, and their cons and pros for practical applications are discussed.
    [Show full text]
  • Fouling Identification for Nanofiltration Membrane and the Potential
    sustainability Article Fouling Identification for Nanofiltration Membrane and the Potential Reduction of Pollutants in the Leachate by Using Fe/Al/PAC Coagulation Chang-wei He 1, Hui Wang 2,*, Luo-chun Wang 1,*, Zi-yang Lou 2, Li Bai 3, Hai-feng Zong 3 and Zhen Zhou 1 1 College of Environmental and Chemical Engineering, Shanghai University of Electric Power, Shanghai 200090, China; [email protected] (C.-w.H.); [email protected] (Z.Z.) 2 School of Environmental Science and Engineering, Shanghai Jiao Tong University, Shanghai 200240, China; [email protected] 3 Shanghai SUS Environment Co. Ltd., No. 9, Songqiu Road, Shanghai 201703, China; [email protected] (L.B.); [email protected] (H.-f.Z.) * Correspondence: [email protected] (H.W.); [email protected] (L.-c.W.); Tel.: +86-21-5474-1065 (H.W.); +86-213-530-3242 (L.-c.W.) Abstract: The reduction in the fouling is an important way to maintain the steady operation for the nanofiltration (NF) process in leachate treatment. The fouling components from the real leachate treatment process were identified using a scanning electron microscope equipped with X-ray microanalysis (SEM- EDS), infrared spectroscopy (FTIR), atomic analysis and three-dimensional fluorescence (EEM) analysis, and the coagulation of Fe/Al/PAC was selected to reduce the potential pollutants in the leachate, to reduce the potential fouling. It was found that organic humic acid and calcium-magnesium precipitates were the main pollutants in NF fouling. The foulant layer was the result of the combination of organic matter, inorganic precipitation, colloids and microorganisms, and the colloids precipitation is more Citation: He, C.-w.; Wang, H.; Wang, important, and should be removed in advance.
    [Show full text]
  • Changes in Surface Properties and Separation Efficiency of A
    University of Wollongong Research Online Faculty of Engineering and Information Sciences - Faculty of Engineering and Information Sciences Papers: Part A 2013 Changes in surface properties and separation efficiency of a nanofiltration membrane after repeated fouling and chemical cleaning cycles Alexander Simon University of Wollongong, [email protected] William E. Price University of Wollongong, [email protected] Long D. Nghiem University of Wollongong, [email protected] Publication Details Simon, A., Price, W. E. & Nghiem, L. D. (2013). Changes in surface properties and separation efficiency of a nanofiltration membrane after repeated fouling and chemical cleaning cycles. Separation and Purification Technology, 113 42-50. Research Online is the open access institutional repository for the University of Wollongong. For further information contact the UOW Library: [email protected] Changes in surface properties and separation efficiency of a nanofiltration membrane after repeated fouling and chemical cleaning cycles Abstract The aim of this study was to evaluate the changes in membrane surface properties and solute separation by a nanofiltration membrane during repetitive membrane fouling and chemical cleaning. Secondary treated effluent and model fouling solutions containing humic acids, sodium alginate, or silica colloids were used to simulate membrane fouling. Chemical cleaning was carried out using a commercially available caustic cleaning formulation. Carbamazepine and sulfamethoxazole were selected to examine the filtration behaviour of neutral and negatively charged organic compounds, respectively. Results show that the impact of membrane fouling on solute rejection is governed by pore blocking, modification of the membrane surface charge, and cake enhanced concentration polarisation. Caustic cleaning was effective at controlling membrane fouling and membrane permeability recovery was slightly more than 100%.
    [Show full text]
  • Mechanisms of Nanofilter Fouling and Treatment Alternatives for Surface Water Supplies
    University of Central Florida STARS Electronic Theses and Dissertations, 2004-2019 2005 Mechanisms Of Nanofilter oulingF And Treatment Alternatives For Surface Water Supplies Charles Robert Reiss University of Central Florida Part of the Environmental Engineering Commons Find similar works at: https://stars.library.ucf.edu/etd University of Central Florida Libraries http://library.ucf.edu This Doctoral Dissertation (Open Access) is brought to you for free and open access by STARS. It has been accepted for inclusion in Electronic Theses and Dissertations, 2004-2019 by an authorized administrator of STARS. For more information, please contact [email protected]. STARS Citation Reiss, Charles Robert, "Mechanisms Of Nanofilter oulingF And Treatment Alternatives For Surface Water Supplies" (2005). Electronic Theses and Dissertations, 2004-2019. 495. https://stars.library.ucf.edu/etd/495 MECHANISMS OF NANOFILTER FOULING AND TREATMENT ALTERNATIVES FOR SURFACE WATER SUPPLIES by CHARLES ROBERT REISS B.S. University of Central Florida, 1990 M.S. University of Central Florida, 1994 A dissertation submitted in partial fulfillment of the requirements for the degree of Doctor of Environmental Engineering in the Department of Civil and Environmental Engineering in the College of Engineering at the University of Central Florida Orlando, Florida Summer Term 2005 Major Professor: James S. Taylor ABSTRACT This dissertation addresses the role of individual fouling mechanisms on productivity decline and solute mass transport in nanofiltration (NF) of surface waters. Fouling mechanisms as well as solute mass transport mechanisms and capabilities must be understood if NF of surface waters is to be successful. Nanofiltration of surface waters was evaluated at pilot-scale in conjunction with advanced pretreatment processes selected for minimization of nanofilter fouling, which constituted several integrated membrane systems (IMSs).
    [Show full text]
  • A Comprehensive Review on Membrane Fouling: Mathematical Modelling, Prediction, Diagnosis, and Mitigation
    water Review A Comprehensive Review on Membrane Fouling: Mathematical Modelling, Prediction, Diagnosis, and Mitigation Nour AlSawaftah , Waad Abuwatfa , Naif Darwish and Ghaleb Husseini * Department of Chemical Engineering, American University of Sharjah, Sharjah 26666, United Arab Emirates; [email protected] (N.A.); [email protected] (W.A.); [email protected] (N.D.) * Correspondence: [email protected] Abstract: Membrane-based separation has gained increased popularity over the past few decades, particularly reverse osmosis (RO). A major impediment to the improved performance of membrane separation processes, in general, is membrane fouling. Fouling has detrimental effects on the membrane’s performance and integrity, as the deposition and accumulation of foulants on its surface and/or within its pores leads to a decline in the permeate flux, deterioration of selectivity, and permeability, as well as a significantly reduced lifespan. Several factors influence the fouling- propensity of a membrane, such as surface morphology, roughness, hydrophobicity, and material of fabrication. Generally, fouling can be categorized into particulate, organic, inorganic, and biofouling. Efficient prediction techniques and diagnostics are integral for strategizing control, management, and mitigation interventions to minimize the damage of fouling occurrences in the membranes. To improve the antifouling characteristics of RO membranes, surface enhancements by different chemical and physical means have been extensively sought after. Moreover, research efforts have been directed towards synthesizing membranes using novel materials that would improve their antifouling performance. This paper presents a review of the different membrane fouling types, Citation: AlSawaftah, N.; Abuwatfa, fouling-inducing factors, predictive methods, diagnostic techniques, and mitigation strategies, with a W.; Darwish, N.; Husseini, G.
    [Show full text]