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231224s2016 xx |||||o 00| ||eng c |
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|a 10.2166/wst.2016.466
|2 doi
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|a pubmed24n0891.xml
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|a (DE-627)NLM26731261X
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|a (NLM)27997404
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|a DE-627
|b ger
|c DE-627
|e rakwb
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|a eng
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1 |
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|a Wang, Shixiang
|e verfasserin
|4 aut
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|a Removal of Hg(II) from aqueous solution using sodium humate as heavy metal capturing agent
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|c 2016
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|a Text
|b txt
|2 rdacontent
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|a ƒaComputermedien
|b c
|2 rdamedia
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|a ƒa Online-Ressource
|b cr
|2 rdacarrier
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|a Date Completed 22.06.2017
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|a Date Revised 10.12.2019
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|a published: Print
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|a Citation Status MEDLINE
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|a An environmental friendly and economic natural biopolymer-sodium humate (HA-Na) was used to capture Hg(II) from aqueous solutions, and the trapped Hg(II) (HA-Na-Hg) was then removed by aluminium coagulation. The best Hg(II) capturing performance (90.60%) was observed under the following conditions: initial pH of 7.0, coagulation pH of 6.0, HA-Na dosage of 5.0 g L-1, Al2(SO4)3.18H2O dosage of 4.0 g L-1, initial Hg(II) concentration of 50 mg L-1 and capturing time of 30 min. The HA-Na compositions with the molecular weight beyond 70 kDa showed the most intense affinity toward Hg(II). The results showed that the reaction equilibrium was achieved within 10 min (pH 7.0), and could be well fitted by the pseudo-second-order kinetics model. The capturing process could be well described by the Langmuir isotherm model and the maximum capturing capacity of Hg(II) was high up to 9.80 mg g-1 at 298 K (pH 7.0). The Fourier transform infrared spectroscopy (FTIR) and X-ray photoelectron spectroscopy (XPS) analysis showed that the redox reaction between Hg(II) and HA-Na and the coordination reaction of carboxyl and hydroxy groups of HA-Na with Hg(II) were responsible for Hg(II) removal. The successive regeneration experiment showed that the capturing efficiency of humates for Hg(II) was maintained at about 51% after five capture-regeneration recycles
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|a Evaluation Study
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|a Journal Article
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|a Alum Compounds
|2 NLM
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|a Humic Substances
|2 NLM
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|a Metals, Heavy
|2 NLM
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|a Solutions
|2 NLM
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|a Water Pollutants, Chemical
|2 NLM
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|a aluminum sulfate
|2 NLM
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|a 34S289N54E
|2 NLM
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|a Sodium
|2 NLM
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|a 9NEZ333N27
|2 NLM
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| 650 |
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|a Aluminum
|2 NLM
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| 650 |
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|a CPD4NFA903
|2 NLM
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| 650 |
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|a Mercury
|2 NLM
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| 650 |
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|a FXS1BY2PGL
|2 NLM
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| 700 |
1 |
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|a Liu, Yong
|e verfasserin
|4 aut
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1 |
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|a Fan, Qin
|e verfasserin
|4 aut
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| 700 |
1 |
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|a Zhou, Anlan
|e verfasserin
|4 aut
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| 700 |
1 |
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|a Fan, Lu
|e verfasserin
|4 aut
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| 700 |
1 |
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|a Mu, Yulan
|e verfasserin
|4 aut
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| 773 |
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|i Enthalten in
|t Water science and technology : a journal of the International Association on Water Pollution Research
|d 1986
|g 74(2016), 12 vom: 28. Dez., Seite 2946-2957
|w (DE-627)NLM098149431
|x 0273-1223
|7 nnns
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| 773 |
1 |
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|g volume:74
|g year:2016
|g number:12
|g day:28
|g month:12
|g pages:2946-2957
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| 856 |
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|u http://dx.doi.org/10.2166/wst.2016.466
|3 Volltext
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|d 74
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|h 2946-2957
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