Abstract

Water pollution is increasing due to urbanization and industrialization. Waste water pollution raised concern because of its influence on plants and humans. Water hyacinth (Eichhornia crassipes) is used for the removal of pollutants because of its phytoremediation efficiency. In this study, water hyacinth (Eichhornia crassipes) has been tested for simultaneous elimination of phenol and cyanide from mono and binary component aqueous solution in batch systems. The plant was grown at six concentrations of phenol and cyanide in the ratio of (10:1), i.e. 100:10, 200:20, 300:30, 500:50, 700:70 and 1000:100 mg/L in aqueous solution. The effect of process parameters such as initial concentration of phenol and cyanide and pH was evaluated. The plant was found capable of eliminating up to 96.42% of phenol (300 mg/L) and 92.66% of cyanide (30 mg/L) during the 13 days cultivation time at pH 8. The calculated Km of the root length elongation for phenol was 5.20 mm and the Vmax was 12.52 μg phenol/g root/h. However, the calculated Km of the root length elongation for cyanide was 0.39 mm and the Vmax was 14.99 μg cyanide/ g root/h. In the Eichhornia crassipes plant, the biochemical parameters such as chlorophyll, protein and sugar content have been indicated a decreasing trend due to uptake of phenol and cyanide throughout cultivation. Toxicity to 100–1000 mg/L of phenol and 10–100 mg/L of cyanide was measured by measuring the relative transpiration over 13 days. At 100 mg/L of phenol and 10 mg/L of cyanide, only a small reduction in transpiration but no morphological changes were noticed. Both pollutants are absorbed through the root of the Eichhornia crassipes plant by plasmalemma and become accumulated into the root cells and stem of a plant. Thus, this study will be beneficial for the decontamination of highly polluted waste water.

Highlights

  • Water is one of the furthermost significant natural resources, necessary for all forms of life

  • FTIR analysis of Eichhornia crassipes plant was carried out for leaves, stem and roots, before and after treatment of phenol and cyanide to determine the occurrence of functional groups on the surface of the plant as shown in Fig. 1a, b and c, for leaves, stem and roots, respectively

  • It was observed from figures that the strong band is found around 3411.67 ­cm−1 in FTIR spectrum of leaves, root, and shoot of the Eichhornia crassipes, before uptake of phenol

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Summary

Introduction

Water is one of the furthermost significant natural resources, necessary for all forms of life This water resource is being polluted by several anthropogenic actions such as rapid growth of urbanization, industrialization and populations that make the environment polluted (Singh and Balomajumder 2016). US Environmental Protection Agency (US EPA) and minimal national standard (MINAS) of central pollution control board (CPCB) limit for cyanide in effluent as 0.2 mg/L and for phenol as 0.5 mg/L (Busca et al 2008; Dash et al 2014). It is important the removal of both compounds

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