2001
DOI: 10.1016/s0008-6223(00)00290-6
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Effect of modification with HNO3 and NaOH on metal adsorption by pitch-based activated carbon fibers

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Cited by 480 publications
(258 citation statements)
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“…Activated carbon has high surface area and porous structure, high adsorption capacity and can be easily functionalized and used as an efficient adsorbent for heavy metal contaminants. 28 The combination of magnetic iron phases with activated carbon offers an attractive and inexpensive option for the removal of different contaminants from water, such as pesticides, phenols and chlorophenols. [29][30][31][32] Magnetic composites of activated carbon/iron oxide were prepared with several weight ratios of 2:1, 1.5:1 and 1:1 and used for the adsorption of volatile organic compounds (VOCs) such as chloroform, phenol, chlorobenzene and dyes from aqueous solution.…”
Section: Application Of Iron Phases To Produce Magnetic Materials As mentioning
confidence: 99%
“…Activated carbon has high surface area and porous structure, high adsorption capacity and can be easily functionalized and used as an efficient adsorbent for heavy metal contaminants. 28 The combination of magnetic iron phases with activated carbon offers an attractive and inexpensive option for the removal of different contaminants from water, such as pesticides, phenols and chlorophenols. [29][30][31][32] Magnetic composites of activated carbon/iron oxide were prepared with several weight ratios of 2:1, 1.5:1 and 1:1 and used for the adsorption of volatile organic compounds (VOCs) such as chloroform, phenol, chlorobenzene and dyes from aqueous solution.…”
Section: Application Of Iron Phases To Produce Magnetic Materials As mentioning
confidence: 99%
“…9,10 [surface] nH + + M n+ (aq) [surface] M n+ + nH + (aq) (1) AC chemical oxidation by nitric acids is one of the most effective means to provide acidic carboxylic and phenolic groups to AC surface. 10,11 However, due to the carbon surface heterogeneity, the carboxylic group introduced exhibits a range of acid dissociation constants (Ka), depending on the neighboring groups and the size of the graphene layer. As a result, the types of acidic groups (Ka) that display ion-exchange properties are insufficiently known.…”
Section: Introductionmentioning
confidence: 99%
“…The amount of Pb(II) adsorbed on oxidized ACF was dependent on the amount of surface acidic functional groups, especially carboxy groups. For the oxidized activated carbon, Pb(II) would adsorb onto carboxy groups on the surface because these oxygen acidic functional groups are widely known to act as effective adsorption sites for heavy metals [11,17]. Nevertheless, the value of Ke for 1500LD-13NOX-6 was slightly higher than that of 1500LD-8NOX-8, which was attributed to the fact that 1500LD-13NOX-6 had more amount of carboxy groups than the others.…”
Section: Pb(ii) Adsorption Isothermsmentioning
confidence: 97%
“…Furthermore, with the increases in nitric acid concentration and oxidation time, the reduction degree of specific surface area, total pore volume and micropore volume gradually increased. These results would be due to the pore entrance blockage by oxygen-containing surface functional groups or electrostatic repulsion between surface acidic functional groups and nitrogen gas, implying that these pores could not be evaluated with BET measurements in spite of the small molecular size of nitrogen gas [11]. Additionally, the decline of specific surface area might be attributed to the enlargement of micropore in the significantly interactive acid erosion.…”
mentioning
confidence: 99%