2020
DOI: 10.1016/j.jenvman.2019.109866
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Enhancing Cd(II) sorption by red mud with heat treatment: Performance and mechanisms of sorption

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Cited by 55 publications
(18 citation statements)
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“…However, the final removal effect could not reach the specified concentration limit due to the low adsorption capacity and strength structure of red mud. To further enhance the adsorption performance of red mud, scholars have adopted different activation methods, such as acidification 14 , 15 , heating 16 , soaking in sea water 17 . For example, some researchers have adopted simple acid activation and then precipitated red mud with ammonia to explore the possibility and adsorption rate of Cd 2+ removal in water 18 .…”
Section: Introductionmentioning
confidence: 99%
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“…However, the final removal effect could not reach the specified concentration limit due to the low adsorption capacity and strength structure of red mud. To further enhance the adsorption performance of red mud, scholars have adopted different activation methods, such as acidification 14 , 15 , heating 16 , soaking in sea water 17 . For example, some researchers have adopted simple acid activation and then precipitated red mud with ammonia to explore the possibility and adsorption rate of Cd 2+ removal in water 18 .…”
Section: Introductionmentioning
confidence: 99%
“…For example, some researchers have adopted simple acid activation and then precipitated red mud with ammonia to explore the possibility and adsorption rate of Cd 2+ removal in water 18 . In addition, it is found that the adsorption stability of red mud for Cd 2+ treated at 500 °C is almost twice that of the original red mud via studying the effect of heat treatment temperature on the adsorption capacity of Red mud for Cd 2+ 16 . However, the aforementioned modification methods are either costly to modify or have other problems, such as consuming too much thermal energy, difficult to perform, or low adsorption efficiency.…”
Section: Introductionmentioning
confidence: 99%
“…This technology is designed to reduce the mobility and biological impact of toxic heavy metals (THM S ) in soils through the addition of exogenous soil amendments and a series of physical and chemical reactions affecting the speciation of THM S . Commonly used immobilization amendments of heavy metal contaminated soil mainly include lime substances [13], modified coal fly ash [14], red mud [15,16], clay minerals, biochar [9], phosphates, iron, and iron oxides. In addition, as an important research direction in the field of environmental science, iron-based materials and biochar have great application potential in improving soil remediation.…”
Section: Introductionmentioning
confidence: 99%
“…Também foi constatado nesse mesmo material um aumento na cristalinidade de hematita com o aquecimento até 900 o C e a transformação de uma pequena quantidade de hematita em magnetita a 827 o C (YANG et al, 2020). Temperatura entre 400 e 600 °C também provoca uma perda de massa associada ao processo de desidroxilação da caulinita (KÄMPF, CURI, 2003).…”
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“…O tratamento térmico realizado entre 200 a 900 o C em um subproduto da indústria de alumínio rico em óxido de ferro contribuiu para elevar a retenção de cadmio com substancial aumento na área superficial específica e na quantidade adsorvida a 500 o C (YANG et al, 2020). A alteração no subproduto da indústria de alumínio também foi comprovada para a adsorção de cádmio e chumbo, cujo tratamento térmico até 600 o C não elevou as porcentagens adsorvidas desses elementos, mas contribuiu para reduzir as suas porcentagens dessorvidas (COSTA et.…”
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