The analysis of target compounds was carried via HPLC (
Agilent 1100 Series; Agilent Technologies, Santa Clara, CA, USA) that was coupled with a diode array detector (DAD, G1315A, Agilent Series). Measurements were done at wavelength of 285 and 240 nm for 3,5-DCP and 2,4-DCA, respectively. A
Nova-Pak C18 (3.9 mm × 150 mm, 4 µm, Waters Corporation, Milford, MA, USA) reversed-phase column was used. The mobile phase consisted of 70% methanol and 30% ultrapure water. The flow rate and temperature of the column were set as 1.0 mL/min and 25°C, respectively. The injection volume was 100 µL. Analytical methods were validated for a concentration range of 0.0625–2 mg/L. Six-point calibration curves showed good linearity (R
2) with correlation coefficients of 0.9998 and 0.9996 obtained for 3,5-DCP and 2,4-DCA, respectively. Detection and quantification limits were established as 0.06 and 0.21 mg/L for 3,5-DCP and 0.03 and 0.12 mg/L for 2,4-DCA, respectively. An Orion (USA) 720A+ model pH-meter was used for all pH measurements. A Jenway 6300 model spectrophotometer (Staffordshire, UK) was employed for colorimetric, residual PS analyses [53]. Fe and Al releases were monitored on a Perkin-Elmer
ICP-MS (PerkinElmer, Inc., Waltham, MA, USA) [54].
KOBA UCUN O., MONTAZERI B., ARSLAN ALATON İ, & ÖLMEZ HANCI T. (2021). Treatment of industrial contaminants with zero-valent iron- and zero-valent aluminium-activated persulfate: a case study with 3,5-dichlorophenol and 2,4-dichloroaniline. Turkish Journal of Chemistry, 45(2), 269-281.