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Insight into UV-LED/PS/Fe(Ⅲ) and UV-LED/PMS/Fe(Ⅲ) for p-arsanilic acid degradation and simultaneous arsenate immobilization.
Cai, Anhong; Ling, Xiao; Wang, Lei; Sun, Qian; Zhou, Shiqing; Chu, Wenhai; Li, Xueyan; Deng, Jing.
Afiliación
  • Cai A; College of Civil Engineering, Zhejiang University of Technology, Hangzhou 310023, China.
  • Ling X; College of Civil Engineering, Zhejiang University of Technology, Hangzhou 310023, China.
  • Wang L; College of Civil Engineering, Zhejiang University of Technology, Hangzhou 310023, China.
  • Sun Q; Afflicated Zhejiang Hospital, Zhejiang University School of Medicine, Hangzhou 310013, China.
  • Zhou S; College of Civil Engineering, Hunan University, Changsha 410082, China.
  • Chu W; State Key Laboratory of Pollution Control and Resource Reuse, College of Environmental Science and Engineering, Tongji University, Shanghai, China.
  • Li X; School of Environmental Science and Engineering, Suzhou University of Science and Technology, Suzhou 215009, China.
  • Deng J; College of Civil Engineering, Zhejiang University of Technology, Hangzhou 310023, China. Electronic address: zjut_djing@163.com.
Water Res ; 223: 118989, 2022 Sep 01.
Article en En | MEDLINE | ID: mdl-35998556
ABSTRACT
As a feed additive, p-arsanilic acid (p-ASA) is hardly metabolized in animal bodies and is excreted chemically unchanged via feces and urine, which can be transformed into more toxic inorganic arsenic species and other organic by-products upon degradation in the aquatic environment. In this study, UV-LED/persulfate (PS)/Fe(Ⅲ) and UV-LED/peroxymonosulfate (PMS)/Fe(Ⅲ) processes were developed to remove p-ASA and immobilize the formed inorganic arsenic via tuning solution pH. UV-LED/PMS/Fe(Ⅲ) (90.8%) presented the best performance for p-ASA degradation at pH 3.0, and the p-ASA degradation in these processes both followed the pseudo-first-order kinetics. The ∙OH played the major role in UV-LED/PS/Fe(Ⅲ) and UV-LED/PMS/Fe(Ⅲ) systems. Solution pH greatly affected the p-ASA degradation and the maximum removal can be achieved at pH 3.0 due to the presence of more Fe(OH)(H2O)52+. The dosages of Fe(III) and PMS (PS), SO42- and HCO3- significantly influenced the performance of p-ASA oxidation, while HA, Cl- and NO3- slightly affected the p-ASA degradation. According to quantum chemical calculation, radical addition on the C atom in the C-As bond of p-ASA was corroborated to be the dominant reaction pathway by SO4∙- and ∙OH. Additionally, the reactive sites and reasonable degradation pathways of p-ASA were proposed based on DFT calculation and HPLC/MS analysis. The release of inorganic arsenic in both processes can be effectively immobilized and the toxicity of the reaction solution dramatically reduced by adjusting solution pH to 6.0. UV-LED/PMS/Fe(Ⅲ) process was found to be more cost-effective than UV-LED/PS/Fe(Ⅲ) process at the low oxidant dosages.
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Texto completo: 1 Colección: 01-internacional Base de datos: MEDLINE Asunto principal: Arsénico / Contaminantes Químicos del Agua Límite: Animals Idioma: En Revista: Water Res Año: 2022 Tipo del documento: Article País de afiliación: China

Texto completo: 1 Colección: 01-internacional Base de datos: MEDLINE Asunto principal: Arsénico / Contaminantes Químicos del Agua Límite: Animals Idioma: En Revista: Water Res Año: 2022 Tipo del documento: Article País de afiliación: China