Modacrylic anion-exchange fibers for Cr(VI) removal from chromium-plating rinse water in batch and flow-through column experiments
被引:7
作者:
Lee, Seung-Chan
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Seoul Natl Univ, Environm Funct Mat & Water Treatment Lab, Seoul, South KoreaSeoul Natl Univ, Environm Funct Mat & Water Treatment Lab, Seoul, South Korea
Lee, Seung-Chan
[1
]
Kang, Jin-Kyu
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Seoul Natl Univ, Environm Funct Mat & Water Treatment Lab, Seoul, South KoreaSeoul Natl Univ, Environm Funct Mat & Water Treatment Lab, Seoul, South Korea
Kang, Jin-Kyu
[1
]
Sim, Eun-Hye
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Seoul Natl Univ, Environm Funct Mat & Water Treatment Lab, Seoul, South KoreaSeoul Natl Univ, Environm Funct Mat & Water Treatment Lab, Seoul, South Korea
Sim, Eun-Hye
[1
]
Choi, Nag-Choul
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Seoul Natl Univ, Environm Funct Mat & Water Treatment Lab, Seoul, South KoreaSeoul Natl Univ, Environm Funct Mat & Water Treatment Lab, Seoul, South Korea
Choi, Nag-Choul
[1
]
Kim, Song-Bae
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Seoul Natl Univ, Environm Funct Mat & Water Treatment Lab, Seoul, South Korea
Seoul Natl Univ, Dept Rural Syst Engn, Seoul, South Korea
Seoul Natl Univ, Res Inst Agr & Life Sci, Seoul, South KoreaSeoul Natl Univ, Environm Funct Mat & Water Treatment Lab, Seoul, South Korea
Kim, Song-Bae
[1
,2
,3
]
机构:
[1] Seoul Natl Univ, Environm Funct Mat & Water Treatment Lab, Seoul, South Korea
[2] Seoul Natl Univ, Dept Rural Syst Engn, Seoul, South Korea
[3] Seoul Natl Univ, Res Inst Agr & Life Sci, Seoul, South Korea
来源:
JOURNAL OF ENVIRONMENTAL SCIENCE AND HEALTH PART A-TOXIC/HAZARDOUS SUBSTANCES & ENVIRONMENTAL ENGINEERING
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2017年
/
52卷
/
13期
The aim of this study was to investigate Cr(VI) removal from chromium-plating rinse water using modacrylic anion-exchange fibers (KaracaronTM KC31). Batch experiments were performed with synthetic Cr(VI) solutions to characterize the KC31 fibers in Cr(VI) removal. Cr(VI) removal by the fibers was affected by solution pH; the Cr(VI) removal capacity was the highest at pH 2 and decreased gradually with a pH increase from 2 to 12. In regeneration and reuse experiments, the Cr(VI) removal capacity remained above 37.0mg g(-1) over five adsorption-desorption cycles, demonstrating that the fibers could be successfully regenerated with NaCl solution and reused. The maximum Cr(VI) removal capacity was determined to be 250.3mg g(-1) from the Langmuir model. In Fourier-transform infrared spectra, a Cr = O peak newly appeared at 897cm(-1) after Cr(VI) removal, whereas a Cr-O peak was detected at 772cm(-1) due to the association of Cr(VI) ions with ion-exchange sites. X-ray photoelectron spectroscopy analyses demonstrated that Cr(VI) was partially reduced to Cr(III) after the ion exchange on the surfaces of the fibers. Batch experiments with chromium-plating rinse water (Cr(VI) concentration = 1178.8mg L-1) showed that the fibers had a Cr(VI) removal capacity of 28.1-186.4mg g(-1) under the given conditions (fiber dose = 1-10g L-1). Column experiments (column length = 10cm, inner diameter = 2.5cm) were conducted to examine Cr(VI) removal from chromium-plating rinse water by the fibers under flow-through column conditions. The Cr(VI) removal capacities for the fibers at flow rates of 0.5 and 1.0mL min(-1) were 214.8 and 171.5mg g(-1), respectively. This study demonstrates that KC31 fibers are effective in the removal of Cr(VI) ions from chromium-plating rinse water.