TY - JOUR
T1 - Ozonation of the reactive dye intermediate 2-naphthylamine 3,6,8-trisulphonic acid (k-acid)
T2 - Kinetic assessment, ozonation products and ecotoxicity
AU - Arslan-Alaton, Idil
AU - Basar, Gulcan
AU - Olmez-Hanci, Tugba
PY - 2012/10
Y1 - 2012/10
N2 - Ozonation of the commercially important, recalcitrant reactive dye intermediate 2-naphthylamine 3,6,8-trisulphonic acid (K-Acid) was investigated. Ozonation performance was examined by following ozone absorption rates and K-Acid, chemical oxygen demand and total organic carbon removals. Mean oxidation states and unidentified organic products were also determined. At pH3, where direct ozone reactions are dominant, the second-order rate constant between K-Acid and molecular ozone was determined as 20m -1s -1 for steady-state aqueous ozone concentration. The competition kinetics approach was also adopted where a reference compound, phenol, and K-Acid were subjected to ozonation. By applying this method, the second-order reaction rate constant was found to be 76m -1s -1. Common oxidation products formed during ozonation at pH3, pH7 and pH7 with 1mm hydrogen peroxide were identified as methoxy-phenyl-oxime, phenol, benzene, benzaldehyde and oxalic acid via high-performance liquid chromatography and gas chromatography/mass spectrometry analyses. Continuous nitrate and sulphate evolution were observed during K-Acid ozonation as a consequence of the abrupt release and subsequent oxidation of its amino and sulphonate groups. The number and amount of reaction products were most intensive for K-Acid ozonation at pH7 with 1mm hydrogen peroxide. According to the acute toxicity tests conducted with Vibrio fischeri, ozonation products were not less toxic than the original K-Acid solution that caused only 15% inhibition.
AB - Ozonation of the commercially important, recalcitrant reactive dye intermediate 2-naphthylamine 3,6,8-trisulphonic acid (K-Acid) was investigated. Ozonation performance was examined by following ozone absorption rates and K-Acid, chemical oxygen demand and total organic carbon removals. Mean oxidation states and unidentified organic products were also determined. At pH3, where direct ozone reactions are dominant, the second-order rate constant between K-Acid and molecular ozone was determined as 20m -1s -1 for steady-state aqueous ozone concentration. The competition kinetics approach was also adopted where a reference compound, phenol, and K-Acid were subjected to ozonation. By applying this method, the second-order reaction rate constant was found to be 76m -1s -1. Common oxidation products formed during ozonation at pH3, pH7 and pH7 with 1mm hydrogen peroxide were identified as methoxy-phenyl-oxime, phenol, benzene, benzaldehyde and oxalic acid via high-performance liquid chromatography and gas chromatography/mass spectrometry analyses. Continuous nitrate and sulphate evolution were observed during K-Acid ozonation as a consequence of the abrupt release and subsequent oxidation of its amino and sulphonate groups. The number and amount of reaction products were most intensive for K-Acid ozonation at pH7 with 1mm hydrogen peroxide. According to the acute toxicity tests conducted with Vibrio fischeri, ozonation products were not less toxic than the original K-Acid solution that caused only 15% inhibition.
UR - http://www.scopus.com/inward/record.url?scp=84865841239&partnerID=8YFLogxK
U2 - 10.1111/j.1478-4408.2012.00392.x
DO - 10.1111/j.1478-4408.2012.00392.x
M3 - Article
AN - SCOPUS:84865841239
SN - 1472-3581
VL - 128
SP - 387
EP - 394
JO - Coloration Technology
JF - Coloration Technology
IS - 5
ER -