Hybrid Treatment Process of using MIEX and High Performance Composite Coagulant for DOM and Bromide Removal

Dissolved organic matter (DOM) and bromide, two primary precursors of disinfection by-products, cannot be effectively removed by conventional coagulation processes. Alternative methods are required to ensure the safety of drinking water. The effectiveness of using magnetic ion exchange resin (MIEX) and high-performance coagulant (HPAC) in a hybrid process for the removal of turbidity, DOM, and bromide in raw water supplies was investigated. Results showed that a wide range of DOM, with different molecular weights (MWs) con- taining soluble microbial byproduct-like organic matters, aromatic protein, and fulvic/humic acid, was removed by MIEX in the two studied water sources. In addition, up to 91% of bromide was removed in bromide spiked raw waters. In comparison, HPAC coagulation did not effectively eliminate low MW or soluble microbial byproduct-like organic matters in raw water. The combined MIEX and HPAC process more significantly improved the performance of turbidity, DOM, and bromide removal than coagulation alone. With MIEX pretreatment, the requisite HPAC dosage was reduced by at least 67%. DOI: 10.1061/(ASCE)EE.1943-7870.0000622. © 2013 American Society of Civil Engineers. CE Database subject headings: Turbidity; Coagulation; Waste treatment; Abatement and removal; Disinfection; Organic matter. Author keywords: Dissolved organic matter; Bromide; Turbidity; Magnetic ion exchange resin; Enhanced coagulation; Coagulation; Drinking water; Ion exchange; Water quality.

[1]  Treavor H. Boyer,et al.  Magnetic ion exchange treatment of stabilized landfill leachate. , 2011, Chemosphere.

[2]  Treavor H. Boyer,et al.  Long-term performance of bicarbonate-form anion exchange: removal of dissolved organic matter and bromide from the St. Johns River, FL, USA. , 2011, Water research.

[3]  Dongsheng Wang,et al.  Change of genotoxicity for raw and finished water: role of purification processes. , 2011, Chemosphere.

[4]  M. Drikas,et al.  Long term case study of MIEX pre-treatment in drinking water; understanding NOM removal. , 2011, Water research.

[5]  Mika Sillanpää,et al.  Natural organic matter removal by coagulation during drinking water treatment: a review. , 2010, Advances in colloid and interface science.

[6]  P. Singer,et al.  Removal of bromide and natural organic matter by anion exchange. , 2010, Water research.

[7]  A. Schäfer,et al.  Magnetic ion exchange: is there potential for international development? , 2009 .

[8]  Treavor H. Boyer,et al.  Removal of dissolved organic matter by anion exchange: effect of dissolved organic matter properties. , 2008, Environmental science & technology.

[9]  B. Jefferson,et al.  Magnetic ion-exchange resin treatment: impact of water type and resin use. , 2008, Water research.

[10]  J. Croué,et al.  Natural organic matter (NOM) and pesticides removal using a combination of ion exchange resin and powdered activated carbon (PAC). , 2008, Water research.

[11]  B. Jefferson,et al.  Pilot scale comparison of enhanced coagulation with magnetic resin plus coagulation systems. , 2008, Environmental science & technology.

[12]  J. Croué,et al.  Combination of coagulation and ion exchange for the reduction of UF fouling properties of a high DOC content surface water. , 2007, Water research.

[13]  Fei Ge,et al.  Removal of bromide by aluminium chloride coagulant in the presence of humic acid. , 2007, Journal of hazardous materials.

[14]  Treavor H. Boyer,et al.  A pilot-scale evaluation of magnetic ion exchange treatment for removal of natural organic material and inorganic anions. , 2006, Water research.

[15]  J. Croué,et al.  Performance of selected anion exchange resins for the treatment of a high DOC content surface water. , 2005, Water research.

[16]  G. Amy,et al.  Size exclusion chromatography to characterize DOC removal in drinking water treatment. , 2005, Environmental science & technology.

[17]  D. Dixon,et al.  Ion exchange for the removal of natural organic matter , 2004 .

[18]  B. Jefferson,et al.  Combination of ferric and MIEX for the treatment of a humic rich water. , 2004, Water research.

[19]  K. Booksh,et al.  Fluorescence excitation-emission matrix regional integration to quantify spectra for dissolved organic matter. , 2003, Environmental science & technology.

[20]  M. Drikas,et al.  The impact of recalcitrant organic character on disinfection stability, trihalomethane formation and bacterial regrowth: An evaluation of magnetic ion exchange resin (MIEX®) and alum coagulation , 2003 .

[21]  Katya Bilyk,et al.  Enhanced coagulation using a magnetic ion exchange resin. , 2002, Water research.

[22]  P. Chadik,et al.  Effect of Bromide Ion on Haloacetic Acid Formation During Chlorination of Biscayne Aquifer Water , 1998 .

[23]  P. Singer Control of Disinfection By‐Products in Drinking Water , 1994 .

[24]  Benjamin W. Lykins,et al.  Alternative Disinfectants for Drinking Water Treatment , 1994 .

[25]  Treavor H. Boyer,et al.  Bicarbonate-form anion exchange: affinity, regeneration, and stoichiometry. , 2011, Water research.

[26]  Shiwei William Guan,et al.  Long-term performance , 2008 .