A Review on Fluoride: Treatment Strategies and Scope for Further Research
Total Page:16
File Type:pdf, Size:1020Kb
Load more
Recommended publications
-
Development of New Low Cost Defluoridation Technology (Krass)
257 99DE Pergamon Wai Sci. Tech. Vol. 40, No. 2, pp. 167-173, 1999 © 1999 IAWQ Published by Elsevicr Science Ltd Printed in Great Britain. All rights reserved «273-1223/99 S20.00 + 000 PII: S0273-1223(99)00440-0 DEVELOPMENT OF NEW LOW COST DEFLUORIDATION TECHNOLOGY (KRASS) Kailash C. Agarwal*, Sunil K. Gupta** and Akhilendra B. Gupta* * Department of Civil Engineering. Malavjya Regional Engineering College, Jaipur 302 017, India ** Satellite Hospital, Bani Park. Jaipur 302 001, India ABSTRACT Systemic tluorosis is an endemic problem in several developing countries. In India 15 states are endemic for fluorosis, of which 5 have indicated hyperendemicity for fluorosts in all districts. WHO standards permit only 1 mg/1 as a safe limit for human consumption. People in several districts of Rajasthan are forced to consume water with fluoride concentrations of up to 44 mg/1 which has resulted in permanent deformities, joint pains, general debility and misery. About 60% of fluoride intake is through water. Considerable work on fluoride removal from water has been done all over the world. However a safe, efficient, free from residual aluminium in treated water, and cost effective defluoridation technique/process is not available and needs to be developed in order to prevent the occurrence of fluorosis. This paper describes the development of a defluoridation process which differs from the known processes in its simplicity, cost effectiveness and results in traces of residual aluminium in treated water. The parameters like fluoride concentration, temperature, pH, alkalinity, humidity and total dissolved solids of input water do not affect this process. -
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 . -
Experiences with Domestic Defluoridation in India
DAW 30th WEDC International Conference, Vientiane, Lao PDR, 2004 PEOPLE-CENTRED APPROACHES TO WATER AND ENVIRONMENTAL SANITATION Experiences with domestic defl uoridation in India R.K. Daw During the International Drinking Water Supply and Sanitation Decade 1980-1990 in India, there was a marked preference in rural drinking water supply programmes, to seek community based water treatment solutions, attached to handpumps where such problems existed. This was true for iron removal and defl uoridation. However, over the next few years most of these treatments systems became inoperative, primarily attributed to a lack of a sense of ownership by user communities, resulting in an attitude of indifference towards the operation and maintenance of these plants. It is also possible that the complexities of O&M by user communities, in the rural Indian socio-political context, had not been institutionally under- stood. Since 1990s there has been an increasing trend to seek household based water quality treatment solution within rural drinking water supply programmes in India. This paper summarises the experiences of UNICEF in India in tackling the problem of high fl uoride content in rural drinking water supply sources, using household-based defl uoridation fi lter using activated alumina. Since 1991, UNICEF supported the research work for development of the technology by the Depart- ment of Chemistry, Indian Institute of Technology (IIT), Kanpur. This resulted in pilot projects on Domestic Defl uoridation Units in the states of Andhra Pradesh and Rajasthan during 1996-2002. Gradually a demand for these fi lters has grown and the private sector is gradually becoming interested. -
Technologies for Fluoride Removal
22 Technologies for fluoride removal Leela Lyengar 22 Tec hnologies for fluoride removal 22.1. Introduction Fluoride is a normal constituent of natural water samples. Its concentration, though, varies significantly depending on the water source. Although both geological and man- made sources contribute to the occurrence of fluoride in water, the major contribution comes from geological resources. Except in isolated cases, surface waters seldom have fluoride levels exceeding 0.3 mg/l. Examples are streams flowing over granite rich in fluoride minerals and rivers that receive untreated fluoride-rich industrial wastewater. There are several fluoride bearing minerals in the earth's crust. They occur in sedimentary (limestone and sandstone) and igneous (granite) rocks. Weathering of these minerals along with volcanic and fumarolic processes lead to higher fluoride levels in groundwater. Dissolution of these barely soluble minerals depends on the water composition and the time of contact between the source minerals and the water. Over the years groundwater has generally been considered to be a protected and safe source of water, fit for drinking without treatment, as the main focus has been on the bacteriological quality of potable water. Little consideration used to be given to the risks of chemical pollution, particularly to the presence of elevated levels of fluoride, arsenic and nitrate in groundwater. This chapter deals with only fluoride. Consumption of water having excess fluoride over a prolonged period leads to a chronic ailment known as fluorosis. Incidence of high-fluoride groundwater has been reported from 23 nations around the globe. It has led to endemic fluorosis, which has become a major geo- environmental health issue in many developing countries. -
Wastewater Treatment by Electrodialysis System and Fouling Problems
The Online Journal of Science and Technology - January 2016 Volume 6, Issue 1 WASTEWATER TREATMENT BY ELECTRODIALYSIS SYSTEM AND FOULING PROBLEMS Elif OZTEKIN, Sureyya ALTIN Bulent Ecevit University, Department of Environmental Engineering, Zonguldak-Turkey [email protected], VDOWÕQ#NDUDHOPDVHGXWU Abstract: Electrodialysis ED is a separation process commercially used on a large scale for production of drinking water from water bodies and treatment of industrial effluents (Ruiz and et al., 2007). ED system contains ion exchange membranes and ions are transported through ion selective membranes from one solution to another under the influence of electrical potential difference used as a driving force. ED has been widely used in the desalination process and recovery of useful matters from effluents. The performance of ED, depends on the operating conditions and device structures such as ion content of raw water, current density, flow rate, membrane properties, feed concentration, geometry of cell compartments (Chang and et al., 2009, Mohammadi and et al., 2004). The efficiency of ED systems consist in a large part on the properties of the ion exchange membranes. Fouling of ion exchange membranes is one of the common problems in ED processes (Lee and et al., 2009, Ruiz and et al., 2007). Fouling is basically caused by the precipitation of foulants such as organics, colloids and biomass on the membrane surface or inside the membrane and fouling problem reduces the transport of ions. The fouling problems are occasion to increase membrane resistance, loss in selectivity of the membranes and affect negatively to membrane performance (Lee and et al., 2002, Lindstrand and et al., 2000a, Lindstrand and et al., 2000b). -
Demineralization Treatment Technologies for the Seawater Demineralization Feasibility Investigation
Special Publication SJ2004-SP7 Demineralization Treatment Technologies for the Seawater Demineralization Feasibility Investigation Technical Memorandum B.7 Demineralization Treatment Technologies For the Seawater Demineralization Feasibility Investigation Contract #SE459AA by R. W. Beck, Inc. 800 North Magnolia Avenue, Suite 300 Orlando, Florida 32803-3274 FINAL St. Johns River Water Management District P.O. Box 1429 Highway 100 West Palatka, Florida December 31, 2002 Contents Contents 1.0 INTRODUCTION 1.1 General ............................................................................................................. 1 1.2 Purpose............................................................................................................. 1 1.3 Early Desalination Technologies.................................................................... 2 2.0 THERMAL DESALINATION PROCESSES.................................................... 3 2.1 History.............................................................................................................. 3 2.2 Multi-stage Flash Distillation ......................................................................... 4 2.3 Multi-effect Distillation................................................................................... 4 2.4 Vapor Compression......................................................................................... 5 2.5 Thermal Plant Performance Enhancements................................................. 5 3.0 MEMBRANE TECHNOLOGY.......................................................................... -
UNIVERSITY of CALIFORNIA Los Angeles Onsite Defluoridation
UNIVERSITY OF CALIFORNIA Los Angeles Onsite Defluoridation Systems for Drinking Water Production A dissertation submitted in partial satisfaction of the requirements for the degree Doctor of Philosophy in Civil Engineering by Elaine Ying Ying Wong 2017 © Copyright by Elaine Ying Ying Wong 2017 ABSTRACT OF THE DISSERTATION Onsite Defluoridation Systems for Drinking Water Production by Elaine Ying Ying Wong Doctor of Philosophy in Civil Engineering University of California, Los Angeles, 2017 Professor Michael K. Stenstrom, Chair Fluoride in drinking water has several effects on the teeth and bones. At concentrations of 1-1.5 mg/L, fluoride can strengthen enamel, improving dental health, but at concentrations above 1.5 to 4 mg/L can cause dental fluorosis. At concentrations of 4 -10 mg/L, skeletal fluorosis can occur. There are many areas of the world that have excessive fluoride in drinking water, such as China, India, Sri Lanka, and the Rift Valley countries in Africa. Treatment solutions are needed, especially in poor areas where drinking water treatment plants are not available. On-site or individual treatment alternatives can be attractive if constructed from common materials and if simple enough to be constructed and maintained by users. This dissertation investigates using calcium carbonate as a cost effective sorbent for an onsite defluoridation drinking water system. Batch and column experiments were performed to characterize F- removal properties. Fluoride sorption was described by Freundlich, Langmuir and Dubinin- Radushkevich isotherm models, ii and it was found that the equilibrium time was approximately 3 hours, with approximately 77% of equilibrium concentration reached within 1 hour. -
Application of Electrodialysis in Waste Water Treatment and Impact Of
ne Scien ra ce b & m T Akhter and Habib, J Membr Sci Technol 2018, 8:2 e e M c h f n o DOI: 10.4172/2155-9589.1000182 o l l a o Journal of Membrane n g r y u ISSN: 2155-9589 o J Science & Technology Review Article Open Access Application of Electrodialysis in Waste Water Treatment and Impact of Fouling on Process Performance Mohsan Akhter, Ghulam Habib* and Sana Ullah Qamar Department of Chemical Engineering, National University of Science and Technology, Islamabad, Pakistan Abstract Electrodialysis (ED) is a new advanced separation process that is commonly utilized for producing drinking water from water bodies as well as for the treatment of industrial effluents. ED process is applied on commercial scale. Basically, an ED process consists of an ion exchange membrane and the diving force necessary for applicability of the process is electric potential. Due to the presence of electric potential ions from one solution after passing through ion selective membrane barrier are transferred to another solution. The main factors on which ED process performance depends on concentration of ion in raw water, flow rate, concentration of feed, current density, membrane properties and cell compartments geometry. Fouling which is produced by foulants including organics, colloids and biomass on the inside membrane internal structure or on the outside surface results in reduction of process separation efficiency and energy consumption is enhanced. Fouling increases the membrane resistance and selectivity of membrane is reduced by fouling. Therefore, some methods are proposed to reduce fouling in ED system such as pre-treatment of feed solution, zeta potential control, membrane properties modification and flowrate optimization. -
Treatment of Fluoride-Contaminated Water. a Review
Treatment of fluoride-contaminated water. A review P Senthil Kumar, S Suganya, S Srinivas, S Priyadharshini, M Karthika, R Karishma Sri, V Swetha, Mu Naushad, Eric Lichtfouse To cite this version: P Senthil Kumar, S Suganya, S Srinivas, S Priyadharshini, M Karthika, et al.. Treatment of fluoride- contaminated water. A review. Environmental Chemistry Letters, Springer Verlag, 2019, 17 (4), pp.1707 - 1726. 10.1007/s10311-019-00906-9. hal-02403012 HAL Id: hal-02403012 https://hal.archives-ouvertes.fr/hal-02403012 Submitted on 10 Dec 2019 HAL is a multi-disciplinary open access L’archive ouverte pluridisciplinaire HAL, est archive for the deposit and dissemination of sci- destinée au dépôt et à la diffusion de documents entific research documents, whether they are pub- scientifiques de niveau recherche, publiés ou non, lished or not. The documents may come from émanant des établissements d’enseignement et de teaching and research institutions in France or recherche français ou étrangers, des laboratoires abroad, or from public or private research centers. publics ou privés. Environmental Chemistry Letters (2019) 17:1707–1726 https://doi.org/10.1007/s10311-019-00906-9 Revised version REVIEW Treatment of fuoride‑contaminated water. A review P. Senthil Kumar1 · S. Suganya1 · S. Srinivas1 · S. Priyadharshini1 · M. Karthika1 · R. Karishma Sri1 · V. Swetha1 · Mu. Naushad2 · Eric Lichtfouse3 Abstract Delivering the right amount of fuoride to drinking water protects the teeth from decay and reduces the risk of cavities. Nonetheless, fuorosis has been diagnosed as the result of excessive exposure of fuoride, which induces brain impairment, muscle disorders and hyperactivity. Fluoride ingestion during the formation of the tooth enamel is the main reason for fuo- rosis, which is characterized by hypomineralization. -
Florida Brackish Water and Seawater Desalination: Challenges and Opportunities
FWRJ Florida Brackish Water and Seawater Desalination: Challenges and Opportunities Christopher P. Hill lorida has historically been the pioneer in face water. As the population of Florida has desalination in the United States. As a grown and the availability of fresh groundwa - Christopher P. Hill, P.E., BCEE, is drinking matter of necessity, it was one of the first ter has diminished, there has been a move - F water technical leader with Brown and states to embrace desalinated groundwater as a ment towards alternative water supplies, Caldwell in Tampa. source of drinking water. Florida installed its including brackish groundwater, surface water, first desalination facility in 1969, which was a and seawater. small electrodialysis (ED) facility in Siesta Key. Today, Florida boasts more than 150 desalina - Desalination and In the mid-2000s, much of Florida was fac - tion facilities, with a combined capacity of more Water Supply Planning ing looming water shortages and the need for al - than 515 million gallons per day (mgd) and ac - ternative water supplies was imminent. As a counting for nearly 25 percent of Florida’s total Florida’s five water management districts result, many water providers maximized exist - water supply (Figure 1). are responsible for sustainable management of ing supplies and began developing alternative From groundwater to seawater, no state its water resources. Each of the districts devel - supplies. Now, in the midst of the national hous - has more operating desalination capacity. ops a regional water supply plan (RWSP) every ing and economic crises, many of these same Florida accounts for more than 50 percent of five years that evaluates the adequacy of exist - water suppliers find themselves flush with un - the U.S. -
An Overview of Industrial Desalination Technologies ASME Industrial Demineralization (Desalination): Best Practices & Future Directions Workshop
An Overview of Industrial Desalination Technologies ASME Industrial Demineralization (Desalination): Best Practices & Future Directions Workshop Washington, D.C. Shahid Chaudhry January 28-29, 2013 1 • The Challenge: Increasing Demand of Water & Energy Resources; Decreasing Supplies of Conventional Water & Energy Resources. Sustainable Management of Water & Energy Resources 2 • Eight Major Water Using Industries Oil & Gas Refining & Petrochemicals Power Generation Food and Beverage Pharmaceutical Microelectronics Pulp & Paper, and Mining GWI: Industrial Desalination & Water Reuse: Ultrapure water, challenging waste streams and improved efficiency, 3 Strategies: Water Conservation / Water Use Efficiency Unaccounted / Water Losses Water Recycling Desalination - Most Energy Intensive / Expensive Water? 4 • Desalination An Energy Intensive Process, An Integral Part of the Future Water Supply Portfolio Source Waters – Generally Four Types Brackish Ground Water, Surface Water, Municipal WW, Agricultural Runoff, Industrial Effluents, Sea Water, etc. Main Processes Categories: Thermal 4 - 6 kWh / m3 + Steam Heating of Contaminated Water under Vacuum Conditions to Create Pure Water Vapors) Membranes 1 - 6 kWh / m3 Energy Requirements - Function of: Plant Capacity, Feed Water Quality, Pretreatment, Desalination Process/Technology, and Level of Treatment Desalination Technology of Most Interest Today Reverse Osmosis 5 • Desalination Methods Distillation Multi-Stage Flash Distillation (MSF) Multiple-Effect Distillation (MED / ME) Vapor-Compression -
Electrodialysis Reversal (EDR)
GE Power & Water Water & Process Technologies Electrodialysis Reversal (EDR) What GE offers GE offers the broadest water and process technologies solutions portfolio—we focus on difficult-to-treat water and wastewater, and implementing water reuse solutions to provide customers with the quantity and quality of water they need for their applications. GE’s $2 billion-plus water division has 8,000 employees worldwide dedicated to solving every kind of water problem and making GE one of the most admired and respected companies operating today. With over 50 years of ED-EDR technology experience, we have the technical knowledge and process expertise to design solutions that are reliable and cost effective for your water purification needs. With 900+ EDR installations globally, GE offers a depth of experience for the design, manufacturing, installation, operation and maintenance of your EDR system. Customer Benefits • Simplified operation and lower capital costs with the GE carbon electrode • Up to 95% TDS reduction on brackish water • Up to 94% water recovery • Requires less pretreatment for suspended solids • High silica levels do not impact performance or water recovery • Handles high organic waters • Up to 0.5 mg/l continuous chlorine feed and capable of shock treatments New Developments in EDR Technology Carbon Electrode AR908 Membrane GE has developed a new electrode which will become the GE has developed a new caustic-stable ion exchange standard electrode for all new GE EDR systems and can also membrane for ED that allows for more aggressive CIP be used in upgrades to existing EDR systems. of EDR stacks. • The Carbon Electrode • AR908 membranes surface is coated allow EDR stacks to be with the same ion cleaned up to pH 13, to exchange resin that keep stacks clean while is contained in GE’s processing higher turbidity membranes.