2013
DOI: 10.1016/j.jhazmat.2013.06.023
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Effect of particle size of drinking-water treatment residuals on the sorption of arsenic in the presence of competing ions

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Cited by 67 publications
(40 citation statements)
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“…It was shown that the specific surface area of EDCMSM (6.83 m 2 /g) was about 10 times as that of EDCMM (0.70 m 2 /g). The adsorbent with higher surface area had more high affinity sites for heavy metal ions, which lead to faster adsorption rate and higher adsorption capacity [29]. Meanwhile, the increase of carboxyl groups on adsorbent could also enhance the removal of Pb 2+ by electrostatic interaction and chelation [23].…”
Section: Effect Of Contact Time On the Adsorption And The Kinetic Stumentioning
confidence: 99%
See 1 more Smart Citation
“…It was shown that the specific surface area of EDCMSM (6.83 m 2 /g) was about 10 times as that of EDCMM (0.70 m 2 /g). The adsorbent with higher surface area had more high affinity sites for heavy metal ions, which lead to faster adsorption rate and higher adsorption capacity [29]. Meanwhile, the increase of carboxyl groups on adsorbent could also enhance the removal of Pb 2+ by electrostatic interaction and chelation [23].…”
Section: Effect Of Contact Time On the Adsorption And The Kinetic Stumentioning
confidence: 99%
“…Chitosan particles are widely used in the field of heavy metal removal [28]. The adsorbent with smaller particle is reported to have higher adsorption capacity due to its higher specific surface area [29]. Submicroparticles, with grain sizes ranging from 100 nm to 1.0 m, have shown excellent performance as a potential catalyst for its high surface area [30].…”
Section: Introductionmentioning
confidence: 99%
“…Moreover, conclusive prior studies have demonstrated that the smaller fraction of WTR greatly influences its active surface area and leads to increase its adsorption capacity [12][13][14]. Recently, Elkhatib et al [13] developed a method to produce nanoparticles sorbent from water treatment residues using precision milling.…”
Section: Introductionmentioning
confidence: 99%
“…Biochars pyrolyzed from waste biomass (agricultural residues, animal manure, and forestry waste) and carbonaceous materials (compost, lignite, and humus) were less successful for immobilizing oxyanions such as As(III), As(V), and Cr(VI), in spite of their strong binding affinity toward cationic trace metals [e.g., Cu(II), Pb(II)] via metal complexation with O‐containing functional groups (carboxyl, hydroxyl, and phenol groups) (Ok et al, 2011; Uchimiya et al, 2011; Olds et al, 2013; Jiménez‐Cedillo et al, 2013; Tsang et al, 2014). Previous studies also suggested the addition of Fe‐ and Al‐hydroxide‐containing materials, such as water treatment residuals (Nielsen et al, 2011; Caporale et al, 2013b), industrial wastewater sludge (Iqbal et al, 2012; Tsang et al, 2013b), and coal fly ash (Wang and Tsang, 2013; Tsang et al, 2014). Therefore, sludge‐derived biochar (SDBC) is unique as a potentially effective sorbent for these oxyanions because sewage sludge itself comprises a large amount of mineral colloids and inorganic coagulants from wastewater treatment.…”
mentioning
confidence: 99%