2013
DOI: 10.1007/s10163-012-0079-4
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Biosorption potential and kinetic studies of vegetable waste mixture for the removal of Nickel(II)

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Cited by 17 publications
(8 citation statements)
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“…For sugarcane bagasse, Ezeonuegbu et al (2021) obtained a maximum sorption capacity of 123.46 mgÁg -1 and 1.61 mgÁg -1for nickel and lead, respectively. Gill et al (2013) used vegetable waste, composed of 1:1 mixture of potato and carrot peels for the removal of Ni(II). Under optimal conditions (pH = 4, contact time 75 min, temperature 30 °C) for an initial concentration of 50 mgÁL -1 , the use of 3 g of biosorbent made it possible to achieve the maximum removal of nickel at 79%.…”
Section: Discussionmentioning
confidence: 99%
“…For sugarcane bagasse, Ezeonuegbu et al (2021) obtained a maximum sorption capacity of 123.46 mgÁg -1 and 1.61 mgÁg -1for nickel and lead, respectively. Gill et al (2013) used vegetable waste, composed of 1:1 mixture of potato and carrot peels for the removal of Ni(II). Under optimal conditions (pH = 4, contact time 75 min, temperature 30 °C) for an initial concentration of 50 mgÁL -1 , the use of 3 g of biosorbent made it possible to achieve the maximum removal of nickel at 79%.…”
Section: Discussionmentioning
confidence: 99%
“…Fourier transform infrared spectroscopy (FTIR) is often used to examine the surface functional groups available on the surface of adsorbent and their ability for metal ions adsorption [33][34][35][36]. FTIR spectrums of cedar leaf ash before and after adsorption were recorded ( Fig.…”
Section: Characterization Of the Adsorbentmentioning
confidence: 99%
“…The desorption capacity initially increased and then decreased with increasing HNO 3 concentration ( Figure 10 b), possibly because the accumulated H + concentration increases the concentration gradients of zinc(II) and H + , which constitute the driving force underlying ion exchange and favoring the desorption process [ 39 ]. The desorption capacity first increased and then slightly decreased with increasing desorption temperature ( Figure 10 c); this behavior is likely attributable to the higher temperature, which may enhance the efficiency and activity of the adsorption sites of XSBLAC until equilibrium is reached [ 40 ]. The desorption capacity initially increased and then remained constant with increasing ultrasonic desorption time ( Figure 10 d), consistent with the production of holes, and then reached saturation under ultrasonic conditions [ 41 ].…”
Section: Resultsmentioning
confidence: 99%