Reverse Osmosis Optimization
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Water Treatment and Reverse Osmosis Systems
Pure Aqua, Inc.® Water© 2012 TreatmentPure Aqua ,and Inc. ReverseAll Right sOsmosis Reserve dSystems. Worldwide Experience Superior Technology About the Company Pure Aqua is a company with a strong philosophy and drive to develop and apply solutions to the world’s water treatment challenges. We believe that both our technology and experience will help resolve the growing shortage of clean water worldwide. Capabilities and Expertise As an ISO 9001:2008 certified company with over a decade of experience, Pure Aqua has secured its position as a leading manufacturer of reverse osmosis systems worldwide. Goals and Motivations Our goal is to provide environmentally sustainable systems and equipment that produce high quality water. We provide packaged systems and technical support for water treatment plants, industrial wastewater reuse, and brackish and seawater reverse osmosis plants. Having strong working relationships with Thus, we ensure our technological our suppliers gives us the capability to contribution to water preservation by provide cost effective and competitive supplying the means and making it highly water and wastewater treatment systems accessible. for a wide range of applications. Seawater Reverse Osmosis Systems System Overview Designed to convert seawater to potable water, desalination systems use high quality reverse osmosis seawater membranes. The process separates dissolved salts by only allowing pure water to pass through the membrane fabric. System Capacities Pure Aqua desalination systems are designed to provide high -
Reverse Osmosis and Nanofiltration, Second Edition
Reverse Osmosis and Nanofiltration AWWA MANUAL M46 Second Edition Science and Technology AWWA unites the entire water community by developing and distributing authoritative scientific and technological knowledge. Through its members, AWWA develops industry standards for products and processes that advance public health and safety. AWWA also provides quality improvement programs for water and wastewater utilities. Copyright © 2007 American Water Works Association. All Rights Reserved. Contents List of Figures, v List of Tables, ix Preface, xi Acknowledgments, xiii Chapter 1 Introduction . 1 Overview, 1 RO and NF Membrane Applications, 7 Membrane Materials and Configurations, 12 References, 18 Chapter 2 Process Design . 21 Source Water Supply, 21 Pretreatment, 26 Membrane Process Theory, 45 Rating RO and NF Elements, 51 Posttreatment, 59 References, 60 Chapter 3 Facility Design and Construction . 63 Raw Water Intake Facilities, 63 Discharge, 77 Suspended Solids and Silt Removal Facilities, 80 RO and NF Systems, 92 Hydraulic Turbochargers, 95 Posttreatment Systems, 101 Ancillary Equipment and Facilities, 107 Instrumentation and Control Systems, 110 Waste Stream Management Facilities, 116 Other Concentrate Management Alternatives, 135 Disposal Alternatives for Waste Pretreatment Filter Backwash Water, 138 General Treatment Plant Design Fundamentals, 139 Plant Site Location and Layout, 139 General Plant Layout Considerations, 139 Membrane System Layout Considerations, 140 Facility Construction and Equipment Installation, 144 General Guidelines for Equipment Installation, 144 Treatment Costs, 151 References, 162 iii Copyright © 2007 American Water Works Association. All Rights Reserved. Chapter 4 Operations and Maintenance . 165 Introduction, 165 Process Monitoring, 168 Biological Monitoring, 182 Chemical Cleaning, 183 Mechanical Integrity, 186 Instrumentation Calibration, 188 Safety, 190 Appendix A SI Equivalent Units Conversion Tables . -
Circle Reverse Osmosis System
CIRCLE REVERSE OSMOSIS SYSTEM KEY FEATURES Water Saving Technology – Patented technology eliminates backpressure The RC100 conforms to common in conventional RO systems making the Circle up to 10 times more NSF/ANSI 42, 53 and efficient than existing products. 58 for the reduction of Saves You Money – Conventional RO systems waste up to 24 gallons of Aesthetic Chlorine, Taste water per every 1 gallon of filtered water produced. The Circle only wastes and Odor, Cyst, VOCs, an average of 2.1 gallons of water per 1 gallon of filtered water produced, Fluoride, Pentavalent Arsenic, Barium, Radium 226/228, Cadmium, Hexavalent saving you water and money over the life of the product!. Chromium, Trivalent Chromium, Lead, RO Filter Auto Flushing – Significantly extends life of RO filter. Copper, Selenium and TDS as verified Chrome Faucet Included – With integrated LED filter change indicator. and substantiated by test data. The RC100 conforms to NSF/ANSI 372 for Space Saving Compact Design – Integrated rapid refill tank means more low lead compliance. space under the sink. SPECIFICATIONS Product Name H2O+ Circle Reverse Osmosis Water Filtration System Model / SKU RC100 Installation Undercounter Sediment Filter, Pre-Carbon Plus Filter, Post Carbon Block Filter (RF-20): 6 months Filters & Lifespan RO Membrane Filter (RF-40): 24 months Tank Capacity 6 Liters (refills fully in less than one hour) Dimensions 9.25” (W) x 16.5” (H) x 13.75” (D) Net weight 14.6 lbs Min/Max Operating Pressure 40 psi – 120 psi (275Kpa – 827Kpa) Min/Max Water Feed Temp 41º F – 95º F (5º C – 35º C) Faucet Flow Rate 0.26 – 0.37 gallons per minute (gpm) at incoming water pressure of 20–100 psi Rated Service Flow 0.07 gallons per minute (gpm) Warranty One Year Warranty PO Box 470085, San Francisco CA, 94147–0085 brondell.com 888-542-3355. -
Troubleshooting Activated Sludge Processes Introduction
Troubleshooting Activated Sludge Processes Introduction Excess Foam High Effluent Suspended Solids High Effluent Soluble BOD or Ammonia Low effluent pH Introduction Review of the literature shows that the activated sludge process has experienced operational problems since its inception. Although they did not experience settling problems with their activated sludge, Ardern and Lockett (Ardern and Lockett, 1914a) did note increased turbidity and reduced nitrification with reduced temperatures. By the early 1920s continuous-flow systems were having to deal with the scourge of activated sludge, bulking (Ardem and Lockett, 1914b, Martin 1927) and effluent suspended solids problems. Martin (1927) also describes effluent quality problems due to toxic and/or high-organic- strength industrial wastes. Oxygen demanding materials would bleedthrough the process. More recently, Jenkins, Richard and Daigger (1993) discussed severe foaming problems in activated sludge systems. Experience shows that controlling the activated sludge process is still difficult for many plants in the United States. However, improved process control can be obtained by systematically looking at the problems and their potential causes. Once the cause is defined, control actions can be initiated to eliminate the problem. Problems associated with the activated sludge process can usually be related to four conditions (Schuyler, 1995). Any of these can occur by themselves or with any of the other conditions. The first is foam. So much foam can accumulate that it becomes a safety problem by spilling out onto walkways. It becomes a regulatory problem as it spills from clarifier surfaces into the effluent. The second, high effluent suspended solids, can be caused by many things. It is the most common problem found in activated sludge systems. -
Chemical Industry Wastewater Treatment
CHEMICAL INDUSTRY WASTEWATER TREATMENT Fayza A. Nasr\ Hala S. Doma\ Hisham S Abdel-Halim", Saber A. El-Shafai* * Water Pollution Research department, National Research Centre, Cairo, Egypt "Faculty of Engineering, Cairo University, Cairo, Egypt Abstract Treatment of chemical industrial wastewater from building and construction chemicals factory and plastic shoes manufacturing factory was investigated. The two factories discharge their wastewater into the public sewerage network. The results showed the wastewater discharged from the building and construction chemicals factory was highly contaminated with organic compounds. The average values of COD and BOD were 2912 and 150 mg02/l. Phenol concentration up to 0.3 mg/l was detected. Chemical treatment using lime aided with ferric chloride proved to be effective and produced an effluent characteristics in compliance with Egyptian permissible limits. With respect to the other factory, industrial wastewater was mixed with domestic wastewater in order to lower the organic load. The COD, BOD values after mixing reached 5239 and 2615 mg02/l. The average concentration of phenol was 0.5 mg/l. Biological treatment using activated sludge or rotating biological contactor (RBC) proved to be an effective treatment system in terms of producing an effluent characteristic within the permissible limits set by the law. Therefore, the characteristics of chemical industrial wastewater determine which treatment system to utilize. Based on laboratory results TESCE, Vol. 30, No.2 <@> December 2004 engineering design of each treatment system was developed and cost estimate prepared. Key words: chemical industry, wastewater, treatment, chemical, biological Introduction The chemical industry is of importance in terms of its impact on the environment. -
Industrial Wastewater Treatment Technologies Fitxategia
INDUSTRIAL WASTEWATER TREATMENT TECHNOLOGIES Image by Frauke Feind from Pixabay licensed under CC0 Estibaliz Saez de Camara Oleaga & Eduardo de la Torre Pascual Faculty of Engineering Bilbao (UPV/EHU) Department of Chemical and Environmental Engineering Industrial Wastewaters (IWW) means the water or liquid that carries waste from industrial or processes, if it is distinct from domestic wastewater. Desalination plant “Rambla Morales desalination plant (Almería - Spain)” by David Martínez Vicente from Flickr licensed under CC BY 2.0 IWW may result from any process or activity of industry which uses water as a reactant or for transportation of heat or materials. 2 Characteristics of wastewater from industrial sources vary with the type and the size of the facility and the on-site treatment methods, if any. Because of this variation, it is often difficult to define typical operating conditions for industrial activities. Options available for the treatment of IWW are summarized briefly in next figure. To introduce in a logical order in the description of treatment techniques, the relationship between pollutants and respective typical treatment technology is taken as reference. 1. Removal of suspended solids and insoluble liquids 2. Removal of inorganic, non-biodegradable or poorly degradable soluble content 3. Removal of biodegradable soluble content 3 Range of wastewater treatments in relation to type of contaminants. Source: BREF http://eippcb.jrc.ec.europa.eu/reference/ 4 3.1. CLASSIFICATION OF INDUSTRIAL EFFLUENTS CLASSIFICATION OF EFFLUENTS -
Reverse Osmosis Treatment, Rejection of Carbon Dioxide, And
Evaluating the Impact of Reverse Osmosis Treatment on Finished Water Carbon Dioxide Concentration and pH WATERCON2012 March 21, 2012 Presented By: Jerry Phipps, P.E. Outline • Purpose • Background • Reverse Osmosis (RO) Fundamentals • Post-Treatment Processes • Pertinent Aquatic Chemistry • Case Studies • Conclusions and Recommendations • Questions Purpose • Review RO and carbonate chemistry fundamentals • Review data from full scale projects to determine change in carbon dioxide and pH from feed to permeate stream Background • The Reverse Osmosis (RO) process uses a semipermeable membrane to separate an influent stream into two streams, a purified permeate stream and a concentrated reject stream • Many references indicate that dissolved gases such as carbon dioxide (CO2) may pass through the membrane with no rejection • The combination of low alkalinity and high carbon dioxide results in an aggressive permeate stream with a lower pH than the influent stream Reverse Osmosis Membranes The most common RO membrane material today is aromatic polyamide, typically in the form of thin-film composites. They consist of a thin film of membrane, bonded to layers of other porous materials that are tightly wound to support and strengthen the membrane. Flow Recovery • Percent recovery is a key design parameter • Defined as permeate flow / influent flow • Recovery is limited by solubility products, Ksp • Typical value for groundwater is ~75%-85%, but varies with application • Example: Influent stream = 100 gpm, 75% recovery. Permeate stream = 75 gpm, -
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. -
Refinery Wastewater Management Using Multiple Angle Oil-Water Separators
REFINERY WASTEWATER MANAGEMENT USING MULTIPLE ANGLE OIL-WATER SEPARATORS Kirby S. Mohr, P.E. Mohr Separations Research, Inc. 1278 FM 407 Suite 109 Lewisville, TX 75077 Phone: 918-299-9290 Cell: 918-269-8710 John N. Veenstra, Ph.D., P.E., Oklahoma State University Dee Ann Sanders, Ph.D., P.E. Oklahoma State University A paper presented at the International Petroleum Environment Conference in Albuquerque, New Mexico, 1998 ABSTRACT In this work, an overview of oil-water separation, as used in the petroleum refining industries, is presented along with case studies. Discussions include: impact of solids, legal aspects, and differing types of systems currently in use, along with their advantages and disadvantages. Performance information on separators is presented with an emphasis on new multiple angle coalescing plate technology for refinery wastewater management. Several studies are presented including a large (20,000 US GPM flow rate) system recently installed at a major US refinery. The separator was constructed by converting two existing API separators into four separators, and adding multiple angle coalescing plates to increase throughput and efficiency. A year of operating experience with this system indicates good performance and few problems. Other examples provide information on separators installed in the United States and other countries. Keywords: Oil-water separator, multiple angle, coalescence, refinery, wastewater management, petroleum, coalescing plate technology BACKGROUND AND INTRODUCTION Oil has been refined for various uses for at least 1000 years. An Arab handbook written by Al-Razi, in approximately 865 A.D., describes distillation of “naft” (naphtha) for use in lamps and thus the beginning of oil refining (Forbes). -
Reverse Osmosis As a Pretreatment of Ion Exchange Equipment at PSE
Copyright Warning & Restrictions The copyright law of the United States (Title 17, United States Code) governs the making of photocopies or other reproductions of copyrighted material. Under certain conditions specified in the law, libraries and archives are authorized to furnish a photocopy or other reproduction. One of these specified conditions is that the photocopy or reproduction is not to be “used for any purpose other than private study, scholarship, or research.” If a, user makes a request for, or later uses, a photocopy or reproduction for purposes in excess of “fair use” that user may be liable for copyright infringement, This institution reserves the right to refuse to accept a copying order if, in its judgment, fulfillment of the order would involve violation of copyright law. Please Note: The author retains the copyright while the New Jersey Institute of Technology reserves the right to distribute this thesis or dissertation Printing note: If you do not wish to print this page, then select “Pages from: first page # to: last page #” on the print dialog screen The Van Houten library has removed some of the personal information and all signatures from the approval page and biographical sketches of theses and dissertations in order to protect the identity of NJIT graduates and faculty. ABSTRACT REVERSE OSMOSIS AS A PRETREATMENT FOR ION EXCHANGE AT PSE&G'S HUDSON GENERATING STATION by Steven Leon Public Service Electric and Gas Company's Hudson Generating Station has historically had problems providing sufficient high quality water for its two once through, supercritical design boilers. The station requires over 60 million gallons annually to compensate for system losses. -
Selective Salt Recovery from Reverse Osmosis Concentrate Using Inter-Stage Ion Exchange Joshua E
University of New Mexico UNM Digital Repository Civil Engineering ETDs Engineering ETDs 7-3-2012 Selective salt recovery from reverse osmosis concentrate using inter-stage ion exchange Joshua E. Goldman Follow this and additional works at: https://digitalrepository.unm.edu/ce_etds Recommended Citation Goldman, Joshua E.. "Selective salt recovery from reverse osmosis concentrate using inter-stage ion exchange." (2012). https://digitalrepository.unm.edu/ce_etds/8 This Dissertation is brought to you for free and open access by the Engineering ETDs at UNM Digital Repository. It has been accepted for inclusion in Civil Engineering ETDs by an authorized administrator of UNM Digital Repository. For more information, please contact [email protected]. Joshua E. Goldman Candidate CIVIL ENGINEERING Department This dissertation is approved, and it is acceptable in quality and form for publication: Approved by the Dissertation Committee: Dr. Kerry J. Howe , Chairperson Dr. Bruce M. Thomson Dr. Stephen E. Cabaniss Dr. Jerry Lowry i Selective Salt Recovery from Reverse Osmosis Concentrate Using Inter-stage Ion Exchange BY Joshua E. Goldman B.A., Anthropology, State University of New York at Stony Brook, 2000 M.S, Environmental Science, University of South Florida, 2007 DISSERTATION Submitted in Partial Fulfillment of the Requirements for the Degree of Doctor of Philosophy Engineering The University of New Mexico Albuquerque, New Mexico May, 2012 ii DEDICATION This dissertation is dedicated to the loving memory of my grandmother, Henriette Stein. iii ACKNOWLEDGMENTS This project was funded by the WateReuse Research Foundation. Resins were donated by ResinTech and Purolite. Francis Boodoo of ResinTech provided technical consultation for the pilot design. -
Membrane Technology and Applications, 2Nd Edition
MEMBRANE TECHNOLOGY AND APPLICATIONS SECOND EDITION Richard W. Baker Membrane Technology and Research, Inc. Menlo Park, California MEMBRANE TECHNOLOGY AND APPLICATIONS MEMBRANE TECHNOLOGY AND APPLICATIONS SECOND EDITION Richard W. Baker Membrane Technology and Research, Inc. Menlo Park, California First Edition published by McGraw-Hill, 2000. ISBN: 0 07 135440 9 Copyright 2004 John Wiley & Sons Ltd, The Atrium, Southern Gate, Chichester, West Sussex PO19 8SQ, England Telephone (+44) 1243 779777 Email (for orders and customer service enquiries): [email protected] Visit our Home Page on www.wileyeurope.com or www.wiley.com All Rights Reserved. No part of this publication may be reproduced, stored in a retrieval system or transmitted in any form or by any means, electronic, mechanical, photocopying, recording, scanning or otherwise, except under the terms of the Copyright, Designs and Patents Act 1988 or under the terms of a licence issued by the Copyright Licensing Agency Ltd, 90 Tottenham Court Road, London W1T 4LP, UK, without the permission in writing of the Publisher. Requests to the Publisher should be addressed to the Permissions Department, John Wiley & Sons Ltd, The Atrium, Southern Gate, Chichester, West Sussex PO19 8SQ, England, or emailed to [email protected], or faxed to (+44) 1243 770620. This publication is designed to provide accurate and authoritative information in regard to the subject matter covered. It is sold on the understanding that the Publisher is not engaged in rendering professional services. If professional advice or other expert assistance is required, the services of a competent professional should be sought. Other Wiley Editorial Offices John Wiley & Sons Inc., 111 River Street, Hoboken, NJ 07030, USA Jossey-Bass, 989 Market Street, San Francisco, CA 94103-1741, USA Wiley-VCH Verlag GmbH, Boschstr.