4.7 Article

Comparison of UV and UV/chlorine system on degradation of 2,4-diami-nobutyric acid and formation of disinfection byproducts in subsequent chlorination

Journal

SEPARATION AND PURIFICATION TECHNOLOGY
Volume 284, Issue -, Pages -

Publisher

ELSEVIER
DOI: 10.1016/j.seppur.2021.120264

Keywords

Drinking water; 2,4-diaminobutyric acid (DAB); UV irradiation; UV/chlorine; Transformation pathway; Disinfection by-products (DBPs)

Funding

  1. National Natural Science Foundation [51878257]
  2. Changsha Municipal Natural Science Founda-tion [kq2007028]
  3. State Key Laboratory of Pollution Control and Resource Reuse Foundation [PCRRF20003]

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This study investigated the degradation of 2,4-diaminobutyric acid (DAB) in UV and UV/chlorine system, as well as the formation of disinfection byproducts (DBPs) during post-chlorination. The presence of reactive substances in the UV/chlorine system enhanced the degradation of DAB, but also increased the production of DBPs and their precursors. Factors such as UV irradiation time, pH, and Cl-2/N concentration affected the formation of DBPs during post-chlorination. Carbonaceous DBP precursors were mainly formed during UV irradiation, while nitrogenous DBP precursors were mainly formed during the UV/chlorine system. Brominated DBPs were dominant in the presence of bromide, while the formation of chlorinated DBPs was inhibited.
2,4-diaminobutyric acid (DAB) is a common non-protein amino acid with extremely high neurotoxicity in water environment, posing a serious threat to human health and animal welfare around the world. Therefore, it is necessary to take appropriate measures to remove it. In this paper, degradation of DAB in UV and UV/chlorine system were studied, and transformation pathways of DAB were preliminarily proposed based on the identified transformation products. Moreover, formation of disinfection byproducts (DBPs) during post-chlorination under different conditions were also discussed. The results indicated that the presence of reactive substances in UV/chlorine system significantly promoted the degradation of DAB, but more DBPs and their precursors were produced at the same time. UV irradiation time, pH and Cl-2/N affected the formation of DBPs during post chlorination to various degrees. Notably, precursors of carbonaceous DBPs were mainly formed during UV irradiation, while those of nitrogenous DBPs were mainly formed during UV/chlorine system. In the presence of bromide, brominated DBPs were the absolute dominant species, while formation of chlorinated DBPs were inhibited. Furthermore, total trihalomethane and total haloacetonitrile increased with increasing bromide concentration. Overall, special attention should be paid to DBP formation when selecting UV or UV/chlorine system as pretreatment to eliminate DAB.

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