This study investigated if biochar, a low-cost carbon-rich material, can be modified with reactive materials for decolorization of dyeing wastewater. Two types of rice husk biochars were produced by using different processes of gasification and pyrolysis in limited air condition. The biochars were first magnetized and then modified with nano-scale zero-valent iron (nZVI) to achieve the final products of magnetic-nZVI biochars. Batch experiments were conducted to investigate the efficiency of the modified biochars for reducing color of the reactive dyes yellow (RY145), red (RR195), and blue (RB19) from dyeing solutions. Results showed that color removal efficiency of the modified biochars was significantly enhanced, achieving the values of 100% for RY145 and RR195 and ≥65% for RB19, while the effectiveness of the original biochar was significantly lower. In addition, with increasing dose of the modified biochars, the color removal efficiency increased accordingly. In contrast, when the dose of nZVI was increased beyond a certain value then its color removal efficiency decreased accordingly. It is reported that the magnetic-nZVI rice husk biochars effectively removed the reactive dyes. The impregnation of nZVI particles on the biochar surface spatially separates the nZVI particles, prevents its aggregation and therefore enhances the decolorization efficiency.
BACKGROUND: The application of biochar to sandy loam soil to reduce leaching of three representative pollutants (a persistent hydrocarbon (phenanthrene; logKOW 4.46), a herbicide (isoproturon; logKOW 2.50), and an antibiotic (sulfamethazine; logKOW 0.28)) were investigated. The wood-derived biochar evaluated in our laboratory study was the solid co-product of a full-scale gasifier feeding a combined heat and power plant. The research aimed to demonstrate multiple environmental benefits with the innovative use of this biochar as a soil improver. RESULTS: Batch sorption experiments indicated 5% biochar added to soil enhanced the partitioning coefficient (Kd) by factors of 2 for phenanthrene and 20 for both sulfamethazine and isoproturon. Column leaching experiments indicated a reduced porewater flow rate, up to 80% slower in the column amended with 5% biochar, and reduced pollutant leaching risks. Numerical models interlinked batch and column study observations. CONCLUSION: (i) Biochar enhanced sorption for the hydrophobic pollutant phenanthrene, and also the less hydrophobic pollutants sulfamethazine and isoproturon; (ii) reduced porewater flow rates following biochar amendment gave rise to greater opportunity for pollutant-solid interaction; (iii) mixing with soil resulted in biochar fouling affecting pollutant partition, and (iv) irreversible retention of pollutants by the soil was an important mechanism affecting pollutant transport
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