TY - JOUR
T1 - Cross-redox and simultaneous removal of Cr(VI) and As(III)
T2 - Influences of Fe(II), Fe(III), oxalic acid, and dissolved organic carbon
AU - Ng, Kim Hoong
AU - Hsu, Liang Ching
AU - Liu, Yu Ting
AU - Hsiao, Chuan Yen
AU - Chiang, Po Neng
AU - Teah, Heng Yi
AU - Hung, Jui Ting
AU - Tzou, Yu Min
N1 - Funding Information:
Authors are grateful to Dr. Chih-Wen Pao and Dr. Jeng-Lung Chen for the assistance at the beamline TPS 44 A, NSRRC. Kim Hoong Ng acknowledges the financial supports provided by National Science and Technology Council (NSTC), Taiwan, and Ming Chi University of Technology under the projects of MOST 111-2221-E-131-010- and VK000-1300-111 , respectively. This work is financially supported by the Ministry of Science and Technology , ROC, under project numbers 110-2313-B-005-023-MY3 , 109–2326-B-005–002-MY3 , and 107–2313-B-005–033-MY3 . This work is also supported by the Innovation and Development Center of Sustainable Agriculture from the Featured Areas Research Center Program within the framework of the Higher Education Sprout Project by the Ministry of Education in Taiwan.
Funding Information:
Authors are grateful to Dr. Chih-Wen Pao and Dr. Jeng-Lung Chen for the assistance at the beamline TPS 44 A, NSRRC. Kim Hoong Ng acknowledges the financial supports provided by National Science and Technology Council (NSTC), Taiwan, and Ming Chi University of Technology under the projects of MOST 111-2221-E-131-010- and VK000-1300-111, respectively. This work is financially supported by the Ministry of Science and Technology, ROC, under project numbers 110-2313-B-005-023-MY3, 109–2326-B-005–002-MY3, and 107–2313-B-005–033-MY3. This work is also supported by the Innovation and Development Center of Sustainable Agriculture from the Featured Areas Research Center Program within the framework of the Higher Education Sprout Project by the Ministry of Education in Taiwan.
Publisher Copyright:
© 2022 The Authors
PY - 2022/10/15
Y1 - 2022/10/15
N2 - Hexavalent chromium [Cr(VI)] and arsenite [As(III)] are hazardous to both human and ecosystem. While their cross-redox reaction decreases both their toxicities, the interferences from ubiquitous substances like Fe (Fe(II) and Fe(III)) and organic compounds (oxalic acid and soil-extracted dissolved organic carbon (DOC)) on such interaction are rarely reported; thence, inspires the investigation in this study. Results showed that the cross-redox, in the absence of interfering substances, only occurred at pH≤2.0, with reaction orders of 0.676 and 0.783 in respect to the concentration of Cr(VI) and As(III). The pseudo-reaction constant, k′, of such reaction was recorded at 0.087 m1.377/(mmol0.459 min). With the addition of Fe(II), the rate of Cr(VI) reduction is promoted in conjunction with suppressed As(III) oxidation. Upon neutralizing to pH 6.0, such reduced Cr can be entirely removed via Fe(II)-assisted adsorption and/or co-precipitation. Meanwhile, the elimination of aqueous As is relatively inferior (36 %), attributed to the largely preserved As(III), which is less susceptible to adsorptive/co-precipitative removal. Unlike Fe(II), Fe(III) did not alter Cr(VI)-As(III) cross-redox path, but triggered high adsorptive and/or co-precipitative removals of Cr and As (90 %). In contrast, both organically-altered systems exhibits plummeted As(III) oxidation, under distinctive mechanisms: oxalic acid competes with As(III) in the redox interactions while DOC reduces As(V) into As(III). Also, DOC would undergo complexion with metals and/or blocked the adsorption or co-precipitation sites, leading to even lower Cr and As precipitation. This study unravelled the interference from ubiquitous species in the co-removal of Cr(VI) and As(III), which provides insightful remediation for heavy metal contaminations.
AB - Hexavalent chromium [Cr(VI)] and arsenite [As(III)] are hazardous to both human and ecosystem. While their cross-redox reaction decreases both their toxicities, the interferences from ubiquitous substances like Fe (Fe(II) and Fe(III)) and organic compounds (oxalic acid and soil-extracted dissolved organic carbon (DOC)) on such interaction are rarely reported; thence, inspires the investigation in this study. Results showed that the cross-redox, in the absence of interfering substances, only occurred at pH≤2.0, with reaction orders of 0.676 and 0.783 in respect to the concentration of Cr(VI) and As(III). The pseudo-reaction constant, k′, of such reaction was recorded at 0.087 m1.377/(mmol0.459 min). With the addition of Fe(II), the rate of Cr(VI) reduction is promoted in conjunction with suppressed As(III) oxidation. Upon neutralizing to pH 6.0, such reduced Cr can be entirely removed via Fe(II)-assisted adsorption and/or co-precipitation. Meanwhile, the elimination of aqueous As is relatively inferior (36 %), attributed to the largely preserved As(III), which is less susceptible to adsorptive/co-precipitative removal. Unlike Fe(II), Fe(III) did not alter Cr(VI)-As(III) cross-redox path, but triggered high adsorptive and/or co-precipitative removals of Cr and As (90 %). In contrast, both organically-altered systems exhibits plummeted As(III) oxidation, under distinctive mechanisms: oxalic acid competes with As(III) in the redox interactions while DOC reduces As(V) into As(III). Also, DOC would undergo complexion with metals and/or blocked the adsorption or co-precipitation sites, leading to even lower Cr and As precipitation. This study unravelled the interference from ubiquitous species in the co-removal of Cr(VI) and As(III), which provides insightful remediation for heavy metal contaminations.
KW - As(III) oxidation
KW - Cr(VI) reduction
KW - Cross-redox
KW - X-ray absorption spectroscopy
KW - XAS
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U2 - 10.1016/j.ecoenv.2022.114084
DO - 10.1016/j.ecoenv.2022.114084
M3 - Article
C2 - 36152429
AN - SCOPUS:85138501604
VL - 245
JO - Ecotoxicology and Environmental Safety
JF - Ecotoxicology and Environmental Safety
SN - 0147-6513
M1 - 114084
ER -