SELECTIVE ADSORPTION OF Fe(II) and Zn(II) FROM PHARMACEUTICAL WASTEWATER

Authors

  • Fatai A. Aderibigbe Department of Chemical Engineering, University of Ilorin, Ilorin, Nigeria
  • Harvis B. Saka 2 Quality Control Department, Segmax Oil Nigeria Limited, Kere-Aje, Ogbondoroko, Kwara State, Nigeria
  • Mutiu K. Amosa Waste Management Unit, HSE Division, Department of Petroleum Resources, 7, Sylvester Ugoh Crescent, Jabi, Abuja-FCT, Nigeria. National Improved Oil Recovery Centre, NOGEC Complex, 7, Kofo Abayomi Street, Victoria Island, Lagos, Nigeria.
  • Mubarak O. Idris Department of Chemical Engineering, University of Ilorin, Ilorin, Nigeria
  • Taibat B. Bello Department of Chemical Engineering, University of Ilorin, Ilorin, Nigeria
  • Fatimah O. Olufowora Department of Chemical Engineering, University of Ilorin, Ilorin, Nigeria
  • Rasheedat O. Adebayo Department of Chemical Engineering, University of Ilorin, Ilorin, Nigeria
  • Shiru Suleiman Department of Chemical Engineering, University of Ilorin, Ilorin, Nigeria

Keywords:

adsorption, Box Behnken design, groundnuts pod, pharmaceutical wastewater, termite mound

Abstract

This work focused on the utilization of termite mound clay and activated carbon prepared from groundnuts pod for the selective removal of Fe(II) and Zn(II) from Pharmaceutical Wastewater. The initial concentration of Fe(II) [0.46 mg/l] and Zn(II) [0.10mg/l] in the pharmaceutical wastewater were determined using Atomic Absorption Spectrophotometer (AAS). Scanning Electron Microscopy (SEM) technique, Fourier transforms infrared (FT-IR) spectroscopy, X-Ray fluorescence (XRF) and X-ray diffraction (XRD) were conducted to investigate the adsorbent features. A preliminary experiment was carried out to determine the suitable adsorbent for optimization studies. Optimization study using Box-Behnken experimental design in Response Surface Methodology were employed. The coded levels selected includes adsorbent loading between 0.05- 0.15 g, temperatures 25 - 45 oC and time 30 - 90 mins. At Optimal condition, 6.6 pH value, the temperature of 25 oC, contact time of 90 mins and adsorbent dosage of 0.1 g, the Fe (II) in the Pharmaceutical Wastewater was removed by 95.72 %. The Langmuir adsorption isotherm model was found to have R2 of 0.9997.  The adsorption capacity of the adsorbent was found to be 0.44 mg/g. Adsorption of Fe (II) onto groundnut pod activated carbon and termite mound clay was best described by the pseudo first order kinetic model (R2 = 1.000). The termite mound clay and the activated carbonized groundnuts pod shows an effective adsorption towards the removal of the targeted pollutants from the pharmaceutical wastewater. 

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Published

2021-11-10