Application of Reverse Osmosis in Purifying Drinking Water
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Total Organic Carbon (TOC) Guidance Manual
September 2002 RG-379 (Revised) Total Organic Carbon (TOC) Guidance Manual Water Supply Division printed on recycled paper TEXAS COMMISSION ON ENVIRONMENTAL QUALITY Total Organic Carbon (TOC) Guidance Manual Prepared by Water Supply Division RG-379 (Revised) September 2002 Robert J. Huston, Chairman R. B. “Ralph” Marquez, Commissioner Kathleen Hartnett White, Commissioner Jeffrey A. Saitas, Executive Director Authorization to use or reproduce any original material contained in this publication—that is, not obtained from other sources—is freely granted. The commission would appreciate acknowledgment. Copies of this publication are available for public use through the Texas State Library, other state depository libraries, and the TCEQ Library, in compli- ance with state depository law. For more information on TCEQ publications call 512/239-0028 or visit our Web site at: www.tceq.state.tx.us/publications Published and distributed by the Texas Commission on Environmental Quality PO Box 13087 Austin TX 78711-3087 The Texas Commission on Environmental Quality was formerly called the Texas Natural Resource Conservation Commission. The TCEQ is an equal opportunity/affirmative action employer. The agency does not allow discrimination on the basis of race, color, religion, national origin, sex, disability, age, sexual orientation or veteran status. In compliance with the Americans with Disabilities Act, this document may be requested in alternate formats by contacting the TCEQ at 512/239-0028, Fax 239-4488, or 1-800-RELAY-TX (TDD), or by writing -
Measuring and Moderating the Water Resource Impact of Biofuel Production and Trade
Measuring and moderating the water resource impact of biofuel production and trade By Kevin Robert Fingerman A dissertation submitted in partial satisfaction of the requirements for the degree of Doctor of Philosophy in Energy and Resources in the Graduate Division of the University of California, Berkeley Committee in charge: Professor Daniel M. Kammen, Co-chair Associate Professor Margaret S. Torn, Co-chair Professor Michael H. O’Hare Professor David J. Vogel Spring, 2012 Measuring and moderating the water resource impact of biofuel production and trade © 2012 by Kevin Robert Fingerman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
A Critical Review of Water Purification Technology Appropriate for Developing Countries
Desalination and Water Treatment 54 (2015) 3487–3493 www.deswater.com June doi: 10.1080/19443994.2014.922309 A critical review of water purification technology appropriate for developing countries: Northern Ghana as a case study Michelle Thompson Institute of the Environment and Sustainability, University of California, 300 La Kretz Hall, Suite 300, Box 951496, Los Angeles, CA 90095, USA, email: [email protected] Received 15 January 2014; Accepted 14 March 2014 ABSTRACT A wide range of technologies are commercially available for water purification. However, not all of these technologies are suitable for use in rural, underdeveloped regions. Here, I present a systematic method for selecting the most appropriate technology for a particular community, using rural Ghana as a case study. In Ghana, over half of the population lives in rural areas, and two-thirds of these residents lack access to safe drinking water. Ghana has made significant strides using innovative water treatment techniques; however, there are still many hurdles. Simple and inexpensive, on-site water filtration technologies are a promising method for removing protozoans and other micro-organisms that pose significant health risks in underdeveloped, rural areas. In this review, several of these commercially available on-site water filtration technologies are assessed based on the following factors: effectiveness, cost, energy consumption, environmental impacts, and waste generated. This ® analysis suggests that for rural communities in Ghana, LifeStraw and ceramic clay pots are the most appropriate technologies. Implementation of these technologies poses potential benefits in terms of cost effectiveness and economic growth. Although this paper focuses on northern Ghana as a case study, the methodology presented here can be readily extended to specific scenarios in other developing countries. -
Engineered Nanomaterials for Water Treatment and Remediation: Costs, Benefits, and Applicability
UC Santa Barbara UC Santa Barbara Previously Published Works Title Engineered nanomaterials for water treatment and remediation: Costs, benefits, and applicability Permalink https://escholarship.org/uc/item/50r1b9sg Authors Adeleye, AS Conway, JR Garner, K et al. Publication Date 2016-02-15 DOI 10.1016/j.cej.2015.10.105 Peer reviewed eScholarship.org Powered by the California Digital Library University of California Chemical Engineering Journal 286 (2016) 640–662 Contents lists available at ScienceDirect Chemical Engineering Journal journal homepage: www.elsevier.com/locate/cej Review Engineered nanomaterials for water treatment and remediation: Costs, benefits, and applicability ⇑ Adeyemi S. Adeleye, Jon R. Conway, Kendra Garner, Yuxiong Huang, Yiming Su 1, Arturo A. Keller Bren School of Environmental Science & Management, and University of California Center for Environmental Implications of Nanotechnology, University of California, Santa Barbara, CA 93106-5131, USA highlights graphical abstract Nanotechnology is a promising alternative to traditional water treatment methods. Nanotechnology is more effective for removing emerging contaminants. Treatment cost of some nanotechnology is comparable to that of conventional methods. Risk assessment of nanotechnology is needed in order to advance the technology. article info abstract Article history: The application of nanotechnology in drinking water treatment and pollution cleanup is promising, as Received 21 April 2015 demonstrated by a number of field-based (pilot and full scale) and bench scale studies. A number of Received in revised form 17 September reviews exist for these nanotechnology-based applications; but to better illustrate its importance and 2015 guide its development, a direct comparison between traditional treatment technologies and emerging Accepted 21 October 2015 approaches using nanotechnology is needed. -
Recommended Standards for Water Works 2007 Edition
Recommended Standards for Water Works 2007 Edition Policies for the Review and Approval of Plans and Specifications for Public Water Supplies A Report of the Water Supply Committee of the Great Lakes--Upper Mississippi River Board of State and Provincial Public Health and Environmental Managers MEMBER STATES AND PROVINCE Illinois Indiana Iowa Michigan Minnesota Missouri New York Ohio Ontario Pennsylvania Wisconsin Published by: Health Research Inc., Health Education Services Division, P.O. Box 7126, Albany, NY 12224 (518)439-7286 www.hes.org Copyright © 2007 by the Great Lakes - Upper Mississippi River Board of State and Provincial Public Health and Environmental Managers This book, or portions thereof, may be reproduced without permission from the author if proper credit is given. TABLE OF CONTENTS FOREWORD POLICY STATEMENT ON PRE-ENGINEERED WATER TREATMENT PLANTS POLICY STATEMENT ON AUTOMATED/UNATTENDED OPERATION OF SURFACE WATER TREATMENT PLANTS POLICY STATEMENT ON BAG AND CARTRIDGE FILTERS FOR PUBLIC WATER SUPPLIES POLICY STATEMENT ON ULTRA VIOLET LIGHT FOR TREATMENT OF PUBLIC WATER SUPPLIES POLICY STATEMENT ON INFRASTRUCTURE SECURITY FOR PUBLIC WATER SUPPLIES POLICY STATEMENT ON ARSENIC REMOVAL INTERIM STANDARD - NITRATE REMOVAL USING SULFATE SELECTIVE ANION EXCHANGE RESIN INTERIM STANDARD - USE OF CHLORAMINE DISINFECTANT FOR PUBLIC WATER SUPPLIES INTERIM STANDARD ON MEMBRANE TECHNOLOGIES FOR PUBLIC WATER SUPPLIES PART 1 - SUBMISSION OF PLANS 1.0 GENERAL 1.1 ENGINEER’S REPORT 1.1.1 General Information 1.1.2 Extent of water works -
Dissolved Organic Carbon (DOC) (For Private Water and Health Regulated Public Water Supplies)
Dissolved Organic Carbon (DOC) (For Private Water and Health Regulated Public Water Supplies) What Is Dissolved Organic Carbon? Dissolved organic carbon (DOC) is a general description of the organic material dissolved in water. Organic carbon occurs as the result of decomposition of plant or animal material. Organic carbon present in soil or water bodies may then dissolve when contacted by water. This dissolved organic carbon moves with both surface water and ground water. Acknowledgement: How Does Dissolved Organic Carbon Get Into Water? Organic material (including carbon) results from decomposition of plants or animals. This Fact Sheet is one of a Once this decomposed organic material contacts water it may partially dissolve. series developed by an Interagency Committee with representatives from How Does Dissolved Organic Carbon Affect My Health? Saskatchewan Ministry of DOC does not pose health risk itself but may become potentially harmful when in Health, Regional Health combination with other aspects of your water. When water with high DOC is Authorities, Saskatchewan chlorinated, harmful byproducts called trihalomethanes may be produced (see Watershed Authority, SaskH2O factsheet on trihalomethanes). Trihalomethanes may have long-term Saskatchewan Ministry of effects on health and they should be considered when chlorinating drinking water Environment, Saskatchewan Ministry of Agriculture, high in DOC. According to Health Canada, the benefits of chlorinating drinking Agriculture and Agri-Food water are much greater than the health risks associated with chlorination by- Canada – PFRA and Health products such as trihalomethanes Canada. DOC can interfere with the effectiveness of disinfection processes such as Responsibility for chlorination, ultraviolet and ozone sterilization. DOC can also promote the growth of interpretation of the content of microorganisms by providing a food source. -
Turbidity Analysis for Oregon Public Water Systems Water Quality in Coast Range Drinking Water Source Areas June 2010
Report Turbidity Analysis for Oregon Public Water Systems Water Quality in Coast Range Drinking Water Source Areas June 2010 Last Updated: 06/29/10 By: Joshua Seeds DEQ 09-WQ-024 This report prepared by: Oregon Department of Environmental Quality 811 SW 6th Avenue Portland, OR 97204 1-800-452-4011 Contact: Joshua Seeds (503) 229-5081 [email protected] Turbidity Analysis for Oregon Public Water Systems Table of Contents Table of Contents .......................................................................................... i List of Figures .............................................................................................. iii List of Tables ............................................................................................... iiv List of Maps ................................................................................................. iiv Executive Summary ..................................................................................... 1 Introduction .................................................................................................. 2 Applicable Turbidity Standards for Water Quality ............................................... 2 Public Water System Evaluations....................................................................... 3 Methods .......................................................................................................................... 5 Definitions of terms........................................................................................................ -
Publication No. 17: Ozone Treatment of Private Drinking Water Systems
PRIVATE DRINKING WATER IN CONNECTICUT Publication Date: April 2009 Publication No. 17: Ozone Treatment of Private Drinking Water Systems Effective Against: Pathogenic (disease-causing) organisms including bacteria and viruses, phenols (aromatic organic compounds), some color, taste and odor problems, iron, manganese, and turbidity. Not Effective Against: Large cysts and some other large organisms resulting from possible or probable sewage contamination, inorganic chemicals, and heavy metals. How Ozone (O3) Treatment Works Ozone is a chemical form of pure oxygen. Like chlorine, ozone is a strong oxidizing agent and is used in much the same way to kill disease-causing bacteria and viruses. It is effective against most amoebic cysts, and destroys bacteria and some aromatic organic compounds (such as phenols). Ozone may not kill large cysts and some other large organisms, so these should be eliminated by filtration or other procedures prior to ozone treatment. Ozone is effective in eliminating or controlling color, taste, and odor problems. It also oxidizes iron and manganese. Ozone treatment units are installed as point-of-use treatment systems. Raw water enters one opening and treated water emerges from another. Inside the treatment unit, ozone is produced by an electrical corona discharge or ultraviolet irradiation of dry air or oxygen. The ozone is mixed with the water whenever the water pump is running. Ozone generation units require a system to clean and remove the humidity from the air. For proper disinfection the water to be treated must have negligible color and turbidity levels. The system requires routine maintenance and an ozone treatment system can be very energy consumptive. -
Raw Water Irrigation System Master Plan
TOWN OF FIRESTONE RAW WATER IRRIGATION SYSTEM MASTER PLAN MARCH 2010 COLORADO CIVIL GROUP, INC. Raw Water Irrigation System Master Plan March 2010 Table of Contents 1 Introduction ............................................................................................................................................................................................. 1 1.1 Project Goals ................................................................................................................................................................................... 1 1.2 Scope of Work ................................................................................................................................................................................ 1 1.2.1 Existing Master Plan Evaluation ............................................................................................................... 1 1.2.2 Identifying Potential Areas for Raw Water Irrigation ............................................................................... 1 1.2.3 Irrigation Ditch Evaluation ........................................................................................................................ 1 1.2.4 Hydraulic Analysis and Calculations ......................................................................................................... 2 1.2.5 Raw Water System Modeling ................................................................................................................... 2 1.2.6 Raw Water Irrigation System Master -
A Review on Uttilization of Agriculture Waste for Wastewater Treatment
© FEB 2019 | IRE Journals | Volume 2 Issue 8 | ISSN: 2456-8880 A Review on Uttilization of Agriculture Waste for Wastewater Treatment HARSHIT KHUNT 1, HARDIK DHOLAKIYA 2, SUNIL VALAND 3 1 Dept. of Chemical Engineering, Chhotubhai Gopalbhai Patel Institute of Technology, UTU-Bardoli, Surat, India Abstract -- The objective of this work is to study generation between metal ions and the functional sustainable process which benefit environment by using groups present on the cell surface. agricultural waste as adsorbent to remove organic pollutants from water. As the current worldwide trend towards more precise environmental standards, technical Pore structures and surface characteristics of aptness and cost-effectiveness became key factors in the adsorbents are the main properties in directing selection of adsorbents for water and wastewater adsorption equilibrium and rate properties which are treatment. Recently, various low-cost adsorbents procure from agricultural waste, industrial by-products or natural needed for plant design. New adsorbents are materials, have been rigorously investigated. In this we continuously being evolved, introducing new utilize the agriculture waste i.e. Alisma plantago aquatic, applications for adsorption technology. Adsorption rice husk[1], saw dust[2], tea and coffee waste[3], orange peel[4] , peanut shells[5], activated carbon[6] ,dry tree equilibrium is the fundamental factor in designing leaves and barks[7], bagasse[8], fibre, leaves and peels are adsorption operations. use as adsorbent which can offer an economical solution for wastewater treatment. Three adsorption isotherm Adsorption can be a potential alternative to models namely Freundlich, Langmuir and Dubinin- Radushkevich were apply to analyse the equilibrium data. traditional treatment processes of metal ions removal Equilibrium is best described by Langmuir isotherm [9]. -
21 Reverse Osmosis Treatment of PDWS 03-09
PRIVATE DRINKING WATER IN CONNECTICUT Publication Date: March 2009 Publication No. 21: Reverse Osmosis Treatment of Private Drinking Water Systems Effective Against: inorganic contaminants such as: dissolved salts of sodium, dissolved (ferrous) iron, nitrate, lead, fluoride, sulfate, potassium, manganese, aluminum, silica, chloride, total dissolved solids, chromium, and orthophosphate. Also effective in removing some detergents, some taste, color and odor-producing chemicals, certain organic contaminants, uranium, and some pesticides. Not Effective Against: dissolved gases, most volatile and semi-volatile organic contaminants including some pesticides and solvents. Alone, reverse osmosis (RO) units are not recommended for treatment of bacteria and other microscopic organisms. How Reverse Osmosis Works A complete reverse osmosis system consists of a RO module, a storage tank, and a separate faucet. The module contains a semi-permeable membrane that allows water to selectively pass through and collect in the storage tank. The contaminants being treated by the RO unit are rejected and then washed off the membrane into a waste stream. It is not practical to treat all water entering a home with an RO system because about 75 percent of the water introduced is wasted. Thus, four gallons of raw water into the system produce about one gallon of treated water. This treated water comes out much slower than water from a regular tap, so a tank is used to store the treated water. The treated water is often used only for drinking and cooking. Each manufacturer’s RO units differ, but the time needed to produce one gallon of water ranges from 2-78 hours. The volume of wastewater produced by RO systems varies by make and model. -
REVIEW of TURBIDITY: Information for Regulators and Water Suppliers
WHO/FWC/WSH/17.01 WATER QUALITY AND HEALTH - TECHNICAL BRIEF TECHNICAL REVIEW OF TURBIDITY: Information for regulators and water suppliers 1. Summary This technical brief provides information on the uses and significance of turbidity in drinking-water and is intended for regulators and operators of drinking-water supplies. Turbidity is an extremely useful indicator that can yield valuable information quickly, relatively cheaply and on an ongoing basis. Measurement of turbidity is applicable in a variety of settings, from low-resource small systems all the way through to large and sophisticated water treatment plants. Turbidity, which is caused by suspended chemical and biological particles, can have both water safety and aesthetic implications for drinking-water supplies. Turbidity itself does not always represent a direct risk to public health; however, it can indicate the presence of pathogenic microorganisms and be an effective indicator of hazardous events throughout the water supply system, from catchment to point of use. For example, high turbidity in source waters can harbour microbial pathogens, which can be attached to particles and impair disinfection; high turbidity in filtered water can indicate poor removal of pathogens; and an increase in turbidity in distribution systems can indicate sloughing of biofilms and oxide scales or ingress of contaminants through faults such as mains breaks. Turbidity can be easily, accurately and rapidly measured, and is commonly used for operational monitoring of control measures included in water safety plans (WSPs), the recommended approach to managing drinking-water quality in the WHO Guidelines for Drinking-water Quality (WHO, 2017). It can be used as a basis for choosing between alternative source waters and for assessing the performance of a number of control measures, including coagulation and clarification, filtration, disinfection and management of distribution systems.