A Study of Removing SUVA and Trihalomethanes by Biological Activated Carbon
Authors: Tseng, Wei-Bin., Lou, Jie-Chung, Han, Jia-Yun
Abstract:
SUVA (equivalent to UV254/DOC) value in raw water is a precursor for the formation of trihalomethane during chlorination at a water treatment plant. This study collected rapidly filtered water from an advanced water treatment plant for use in experiments on raw water. The removal rate of treating the trihalomethanes formation potential (THMFP) was conducted by using a biological activated carbon. The hydraulic retention time and SUVA loading were major factors in biological degradation tests. The results showed that biological powder-activated carbon (BPAC) lowered the average concentration of UV254 and value of SUVA in raw water. A removal efficiency of THMFP was present in the treatment of the three primary organic carbon items. These results highlighted the importance of the BPAC had an excellent treatment efficiency on THMFP.
Keywords: Water treatment, BPAC, THMFP, SUVA, correlation analysis.
Digital Object Identifier (DOI): doi.org/10.5281/zenodo.1088362
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[1] Attias, L.; Contu, A.; Loizzo, A.; Massiglia, M.; Valente, P. Trihalomethanes in Drinking Water and Cancer: Risk Assessment and Integrated Evaluation of Available Data in Animals and Humans. Science of the Total Environment. 1995, 171, 61-68.
[2] Johnson, P.D.; Dawson, B.V.; Goldberg, S.J. Cardiac teratogenicity of trichloroethylene metabolites. Journal of the American College of Cardiology. 1998, 32(2), 540-545.
[3] Miller, J.H.; Minard, K.; Wind, R.A.; Orner, G.A.; Sasser, L.B.; Bull, R.J. In vivo MRI measurements of tumor growth induced by dichloroacetate: implications for mode of action. Toxicology. 2000, 145(2-3), 115-125.
[4] Cedergren, M.I.; Selbing, A.J.; Löfman, O.; Källen, B.A.J. Chlorination byproducts and nitrate in drinking water and risk for congenital cardiac defects. Environmental Research. 2002, 89, 124-130.
[5] Dodds, L.; King, W.; Woolcott, C.; Pole, J. Trihalomethanes in public water supplies and adverse birth outcomes. Epidemiology. 1999, 10, 233-237.
[6] Minghua, Li.; Huang, C.P. Stability of oxidized single-walled carbon nanotubes in the presence of simple electrolytes and humic acid. Carbon. 2010, 48, 4527-4534.
[7] Lou J.C .;Chang T.W.; Huang C.E. Effective removal of disinfection by-products and assimilable organic carbon:An advanced water treatment system, Journal of Hazardous Materials, 2009,172, 1365–1371.
[8] Su, D. J. and Gao, N. Y. A study of removing organic matters in slightly-polluted water by an ozone-active carbon combined process. Ind. Water Waste -water. 2005, 32, 26-28.
[9] Singer, P. C. Humic substances as percursors for potentially harmful disinfection by-products. Wat. Sci. Tech. 1999 40(9), 25-30.
[10] Krasner, S. W., W. H. Glaze, H. S. Weinberg, P. A. Daniel, and I. N. Najm. Formation and control of waters containing bromide. J. AWWA. 1993, 85(1), 73-81.
[11] Goel, S. H., M. Raymond, and E. J. Bouwer. Biodegradation of NOM: Effect of NOM source and ozone dose. J.AWWA. 1995, 85(1), 90-105.
[12] Korshin, G. V., C. W. Li, and M. M. Benjamin. The decrease of UV absorbance as an indicator of TOX formation. Water Res. 1997, 31(4), 946-949.