Abstract

The search for alternatives to fossil-based commercial activated carbon (AC) continues to reveal new eco-friendly potential precursors, among which is agricultural waste. The key research aspect in all these endeavors is empirical ascertainment of the core properties of the resultant AC to suit a particular purpose. These properties include: yield, surface area, pore volume, and the active surface groups. It is therefore pertinent to have process conditions controlled and tailored towards these properties for the required resultant AC. Pre-leaching cassava peels with NaOH followed by KOH activation and carbonization at holding temperatures (780 °C) above the melting point of K (760 °C) yielded mesoporous activated carbon with the highest surface area ever reported for cassava peel-based AC. The carbonization temperatures were between 480 and 780 °C in an activation–carbonization stepwise process using KOH as the activator at a KOH:peel ratio of 5:2 (mass basis). A 42% maximum yield of AC was realized along with a total pore volume of 0.756 cm3g−1 and BET surface area of 1684 m2g−1. The AC was dominantly microporous for carbonization temperatures below 780 °C, but a remarkable increase in mesopore volume (0.471 cm3g−1) relative to the micropore volume (0.281 cm3g−1) was observed at 780 °C. The Fourier transform infrared (FTIR) spectroscopy for the pre-treated cassava peels showed distortion in the C–H bonding depicting possible elaboration of more lignin from cellulose disruption by NaOH. A carboxylate stretch was also observed owing to the reaction of Na+ ions with the carboxyl group in the raw peels. FTIR showed possible absorption bands for the AC between 1425 and 1712 cm−1 wave numbers. Besides the botanical qualities of the cassava peel genotype used, pre-leaching the peels and also increasing holding activation temperature above the boiling point of potassium enabled the modified process of producing highly porous AC from cassava peel. The scanning electron microscope (SEM) and transmission electron microscope (TEM) imaging showed well-developed hexagonal pores in the resultant AC and intercalated K profile in the carbon matrices, respectively.

Highlights

  • Activated carbon (AC) continues to find application in both domestic and industrial processes predominantly in adsorption

  • It was held at the respective carbonization temperatures for 2 h after which the resultant ACs were washed with hydrochloric acid

  • Bulk density The bulk density for the resultant activated carbon was in the range 0.31–0.39 ­gcm−3 which corroborates well with that reported by Parvathi et al (2018), but lower than 0.410–0.415 ­gcm−3 reported by Omotosho and Sangodoyin (2013)

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Summary

Introduction

Activated carbon (AC) continues to find application in both domestic and industrial processes predominantly in adsorption. The activated carbons available on market are very costly. Besides the general considerations for an AC precursor, the choice of a particular lignocellulosic residue for AC production depends on its chemical and physical properties (Menya et al 2018). These include; moisture content, volatile matter, carbon composition, ash content, and dry matter content. The resultant quality of the produced AC from a lignocellulosic precursor depends on the reactions and interactions of the different components of the precursor, mainly cellulose, hemicellulose, and lignin (Gani and Naruse 2007)

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