2022
DOI: 10.1007/s13762-022-03928-z
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Adsorption of Cr (VI) on lignocellulosic wastes adsorbents: an overview and further perspective

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Cited by 9 publications
(4 citation statements)
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“…Similarly, Bayuo et al ( 2019) observed that the maximum chromium adsorption on ground nut shell was 5.56 mg g −1 [42]. Recently, Bachmann et al ( 2022) reported an adsorption of 0.32 to 403.23 mg Cr (VI) per gram of lignocellulosic waste adsorbent [43]. Therefore, it is concluded that the struvite-humic acid composite derived herein is an effective adsorbent for chromium.…”
Section: Cr (Vi) Sorption By S-hamentioning
confidence: 69%
“…Similarly, Bayuo et al ( 2019) observed that the maximum chromium adsorption on ground nut shell was 5.56 mg g −1 [42]. Recently, Bachmann et al ( 2022) reported an adsorption of 0.32 to 403.23 mg Cr (VI) per gram of lignocellulosic waste adsorbent [43]. Therefore, it is concluded that the struvite-humic acid composite derived herein is an effective adsorbent for chromium.…”
Section: Cr (Vi) Sorption By S-hamentioning
confidence: 69%
“…The adsorption performance decreases after 40 °C in each of the cases which can be analyzed in Figure 11. This might be due to devastation, decimation, and disintegration of the structure lignocellulosic biomass of each adsorbent [53]. This behavior can be analyzed for PWM at 60 °C which has been shown to have an 80% eradication of CGR, and for PWC, which has shown a decrease in adsorption at 40 to 50 °C from 80% to 73.5%, with an afterward increase in adsorption to 80% again at 50 to 60 °C.…”
Section: Optimization Of Temperature For Adsorptionmentioning
confidence: 99%
“…The Gibbs free energy calculated from Equation ( 17) [53], for the adsorption of CGR on chemically modified adsorbents CPWM (-13.7, -6.67, and -4.95 kJmol -1 ) and CPWC (-8.95, -5.9, and -4.5 kJmol -1 ), as compared to their unmodified forms, PWM (-7.4, -5.3, and -4.1 kJmol -1 ) and PWC (-6.5, -4.8, and -3.7 kJmol -1 ) at 298, 308, and 318 kelvin temperatures, respectively, suggests that the process is spontaneous in standard conditions. [67].…”
Section: Adsorption Kinetic Investigationmentioning
confidence: 99%
“…Until now, a variety of methods have been used to treat Cr(VI) contamination, for example, chemical precipitation [7], ion exchange [8,9], membrane filtration [10], solvent extraction, coagulation and adsorption [11,12]. Among these methods, adsorption technology is more economical than membrane filtration is, easier to operate than coagulation/precipitation is, and more versatile than ion exchange is, which is considered as the most practical technology [13][14][15][16].…”
Section: Introductionmentioning
confidence: 99%