Abstract

Contamination of underground water with fluoride (F) is a tremendous health hazard. Excessive F (> 1.5 mg/L) in drinking water can cause both dental and skeletal fluorosis. A fixed-bed column experiments were carried out with the operating variables such as different initial F concentrations, bed depths, pH and flow rates. Results revealed that the breakthrough time and exhaustion time decrease with increasing flow rate, decreasing bed depth and increasing influent fluoride concentration. The optimized conditions are: 10 mg/L initial fluoride concentration; flow rate 3.4 mL/min, bed depth 3.5 and pH 5. The bed depth service time model and the Thomas model were applied to the experimental results. Both the models were in good agreement with the experimental data for all the process parameters studied except flow rate, indicating that the models were appropriate for removal of F by natural banana peel dust in fix-bed design. Moreover, column adsorption was reversible and the regeneration was accomplished by pumping of 0.1 M NaOH through the loaded banana peel dust column. On the other hand, field water sample analysis data revealed that 86.5% fluoride can be removed under such optimized conditions. From the experimental results, it may be inferred that natural banana peel dust is an effective adsorbent for defluoridation of water.

Highlights

  • Due to rapid industrialization, huge quantity of pollutants discharges in to the environment

  • Preparation of banana peel dust was subjected to p­ HZPC and SEM study for understanding the zero point charge and surface morphology (HITACHI-S-530, Scanning Electron Microscope and ELKO Engineering, accelerating voltage of 20.0 kV) and surface chemistry of the banana peel was assessed by FTIR (BRUKER, Tensor 27)

  • The zero point charge of the banana peel was recorded as 5.63 (Fig. 1), and from the scanning micrograph it is clear that the surface of the banana peel dust is absolutely rough in nature and huge heterogeneity (Fig. 2a)

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Summary

Introduction

Huge quantity of pollutants discharges in to the environment. Fluorine is one such pollutant that threatens living organisms, in particular humans (Koilraj and Kannan 2013). Fluoride is a strongly electronegative element, and its presence in drinking water is essential for human health (Chen et al 2012). Excess consumption of fluoride can lead to both dental and skeletal fluorosis (Kierdorf et al 2016; Death et al 2015). Previous literature (Mohan et al 2012) demonstrated that more than 200 million people worldwide are affected by fluoridecontaminated drinking water with very high concentration. As per the guideline adopted by WHO (2011) and Bureau of Indian standard (BIS 1991), the concentration of fluoride

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