Facilitated Prediction of Micropollutant Degradation via UV-AOPs in Various Waters by Combining Model Simulation and Portable Measurement

Yanyan Huang, Mengkai Li, Zhe Sun, Wentao Li, James R. Bolton, Zhimin Qiang

Engineering ›› 2024, Vol. 37 ›› Issue (6) : 97-105.

PDF(1277 KB)
PDF(1277 KB)
Engineering ›› 2024, Vol. 37 ›› Issue (6) : 97-105. DOI: 10.1016/j.eng.2023.10.009
Research
Article

Facilitated Prediction of Micropollutant Degradation via UV-AOPs in Various Waters by Combining Model Simulation and Portable Measurement

Author information +
History +

Highlights

• Water matrix scavenging capacities for $ \mathrm{HO}^{·}$, $ \mathrm{SO}_{4}^{·-}$ and $ \mathrm{Cl}^{·}$ were measured portably.

• Model simulation consisted of photochemical, QSAR, and SSA models.

kp,MP values in UV-AOPs were predicted in real waters and verified experimentally.

• The developed method facilitates the selection and optimization of UV-AOPs.

Abstract

The degradation of micropollutants in water via ultraviolet (UV)-based advanced oxidation processes (AOPs) is strongly dependent on the water matrix. Various reactive radicals (RRs) formed in UV-AOPs have different reaction selectivities toward water matrices and degradation efficiencies for target micropollutants. Hence, process selection and optimization are crucial. This study developed a facilitated prediction method for the photon fluence-based rate constant for micropollutant degradation (kp,MP) in various UV-AOPs by combining model simulation with portable measurement. Portable methods for measuring the scavenging capacities of the principal RRs (RRSCs) involved in UV-AOPs (i.e., $ \mathrm{HO}^{·}$, $ \mathrm{SO}_{4}^{·-}$, and $ \mathrm{Cl}^{·}$) using a mini-fluidic photoreaction system were proposed. The simulation models consisted of photochemical, quantitative structure–activity relationship, and radical concentration steady-state approximation models. The RRSCs were determined in eight test waters, and a higher RRSC was found to be associated with a more complex water matrix. Then, by taking sulfamethazine, caffeine, and carbamazepine as model micropollutants, the kp,MP values in various UV-AOPs were predicted and further verified experimentally. A lower kp,MP was found to be associated with a higher RRSC for a stronger RR competition; for example, kp,MP values of 130.9 and 332.5 m2·einstein–1, respectively, were obtained for carbamazepine degradation by UV/H2O2 in the raw water (RRSC = 9.47 × 104 s−1) and sand-filtered effluent (RRSC = 2.87 × 104 s−1) of a drinking water treatment plant. The developed method facilitates process selection and optimization for UV-AOPs, which is essential for increasing the efficiency and cost-effectiveness of water treatment.

Graphical abstract

Keywords

UV-AOPs / Micropollutant degradation / Reactive radicals / Water matrix / Model simulation

Cite this article

Download citation ▾
Yanyan Huang, Mengkai Li, Zhe Sun, Wentao Li, James R. Bolton, Zhimin Qiang. Facilitated Prediction of Micropollutant Degradation via UV-AOPs in Various Waters by Combining Model Simulation and Portable Measurement. Engineering, 2024, 37(6): 97‒105 https://doi.org/10.1016/j.eng.2023.10.009

References

[1]
R.P. Schwarzenbach, B.I. Escher, K. Fenner, T.B. Hofstetter, C.A. Johnson, U. von Gunten, et al. The challenge of micropollutants in aquatic systems. Science, 313 (5790) (2006), pp. 1072-1077.
[2]
N.Z. Arman, S. Salmiati, A. Aris, M.R. Salim, T.H. Nazifa, M.S. Muhamad, et al. A review on emerging pollutants in the water environment: existences, health effects and treatment processes. Water, 13 (22) (2021), p. 3258.
[3]
Y. Huang, M.H. Kong, S. Coffin, K.H. Cochran, D.C. Westerman, D. Schlenk, et al. Degradation of contaminants of emerging concern by UV/H2O2 for water reuse: kinetics, mechanisms, and cytotoxicity analysis. Water Res, 174 (2020), Article 115587.
[4]
K.H. Guo, Z.H. Wu, S.W. Yan, B. Yao, W.H. Song, Z.C. Hua, et al. Comparison of the UV/chlorine and UV/H2O2 processes in the degradation of PPCPs in simulated drinking water and wastewater: kinetics, radical mechanism and energy requirements. Water Res, 147 (2018), pp. 184-194.
[5]
J.E. Grebel, J.J. Pignatello, W.A. Mitch. Effect of halide ions and carbonates on organic contaminant degradation by hydroxyl radical-based advanced oxidation processes in saline waters. Environ Sci Technol, 44 (17) (2010), pp. 6822-6828.
[6]
X.J. Kong, J. Jiang, J. Ma, Y. Yang, W.L. Liu, Y.L. Liu. Degradation of atrazine by UV/chlorine: efficiency, influencing factors, and products. Water Res, 90 (2016), pp. 15-23.
[7]
J. Lee, U. von Gunten, J.H. Kim. Persulfate-based advanced oxidation: critical assessment of opportunities and roadblocks. Environ Sci Technol, 54 (6) (2020), pp. 3064-3081.
[8]
W. Li, T. Jain, K. Ishida, H.Z. Liu. A mechanistic understanding of the degradation of trace organic contaminants by UV/hydrogen peroxide, UV/persulfate and UV/free chlorine for water reuse. Enviro Sci-Wat Res, 3 (1) (2017), pp. 128-138.
[9]
E.J. Rosenfeldt, K.G. Linden. The ROH, UV concept to characterize and the model UV/H2O2 process in natural waters. Environ Sci Technol, 41 (7) (2007), pp. 2548-2553.
[10]
B.A. Wols, D.J.H. Harmsen, J. Wanders-Dijk, E.F. Beerendonk, C.H.M. Hofman-Caris. Degradation of pharmaceuticals in UV (LP)/H2O2 reactors simulated by means of kinetic modeling and computational fluid dynamics (CFD). Water Res, 75 (2015), pp. 11-24.
[11]
P.C. Xie, J. Ma, W. Liu, J. Zou, S.Y. Yue, X.C. Li, et al. Removal of 2-MIB and geosmin using UV/persulfate: contributions of hydroxyl and sulfate radicals. Water Res, 69 (2015), pp. 223-233.
[12]
J.Y. Fang, Y. Fu, C.I. Shang. The roles of reactive species in micropollutant degradation in the UV/free chlorine system. Environ Sci Technol, 48 (3) (2014), pp. 1859-1868.
[13]
Y. Lei, S.S. Cheng, N. Luo, X. Yang, T.C. An. Rate constants and mechanisms of the reactions of Cl· dot and Cl2·- with trace organic contaminants. Environ Sci Technol, 53 (19) (2019), pp. 11170-11182.
[14]
S. Sudhakaran, G.L. Amy. QSAR models for oxidation of organic micropollutants in water based on ozone and hydroxyl radical rate constants and their chemical classification. Water Res, 47 (3) (2013), pp. 1111-1122.
[15]
Y.Y. Huang, Z.M. Qiang, Z. Sun, M.K. Li. Micropollutant degradation by UV/H2O2 in drinking water: facilitated prediction through combination of model simulation and portable measurement. Water Res, 221 (2022), Article 118794.
[16]
S. Sundararaman, J. Aravind Kumar, P. Deivasigamani, Y. Devarajan. Emerging pharma residue contaminants: occurrence, monitoring, risk and fate assessment—a challenge to water resource management. Sci Total Environ, 825 (2022), Article 153897.
[17]
C.C. Wang, Y.L. Lu, C. Wang, C. Xiu, X.H. Cao, M. Zhang, et al. Distribution and ecological risks of pharmaceuticals and personal care products with different anthropogenic stresses in a coastal watershed of China. Chemosphere, 303 (2022), Article 135176.
[18]
M.K. Li, W.T. Li, D. Wen, J.R. Bolton, E.R. Blatchley III, Z.M. Qiang. Micropollutant degradation by the UV/H2O2 process: kinetic comparison among various radiation sources. Environ Sci Technol, 53 (9) (2019), pp. 5241-5248.
[19]
W.H. Glaze, Y. Lay, J.W. Kang. Advanced oxidation processes—a kinetic model for the oxidation of 1,2-dibromo-3-chloropropane in water by the combination of hydrogen peroxide and UV radiation. Ind Eng Chem Res, 34 (7) (1995), pp. 2314-2323.
[20]
J.C. Crittenden, S.M. Hu, D.W. Hand, S.A. Green. A kinetic model for H2O2/UV process in a completely mixed batch reactor. Water Res, 33 (10) (1999), pp. 2315-2328.
[21]
X. Luo, X.H. Yang, X.L. Qiao, Y. Wang, J.W. Chen, X.X. Wei, et al. Development of a QSAR model for predicting aqueous reaction rate constants of organic chemicals with hydroxyl radicals. Environ Sci Process Impacts, 19 (3) (2017), pp. 350-356.
[22]
R.Y. Xiao, T.T. Ye, Z.S. Wei, S. Luo, Z.H. Yang, R. Spinney. Quantitative structure-activity relationship (QSAR) for the oxidation of trace organic contaminants by sulfate radical. Environ Sci Technol, 49 (22) (2015), pp. 13394-13402.
[23]
M.J. Watts, K.G. Linden. Chlorine photolysis and subsequent ·OH radical production during UV treatment of chlorinated water. Water Res, 41 (13) (2007), pp. 2871-2878.
[24]
Y. Yang, J. Jiang, X.L. Lu, J. Ma, Y.Z. Liu. Production of sulfate radical and hydroxyl radical by reaction of ozone with peroxymonosulfate: a novel advanced oxidation process. Environ Sci Technol, 49 (12) (2015), pp. 7330-7339.
[25]
Z.C. Hua, X.J. Kong, S.D. Hou, S.Q. Zou, X.B. Xu, H. Huang, et al. DBP alteration from NOM and model compounds after UV/persulfate treatment with post chlorination. Water Res, 158 (2019), pp. 237-245.
[26]
X. Yang, J.L. Sun, W.J. Fu, C.I. Shang, Y. Li, Y.W. Chen, et al. PPCP degradation by UV/chlorine treatment and its impact on DBP formation potential in real waters. Water Res, 98 (2016), pp. 309-318.
[27]
P. Neta, V. Madhavan, H. Zemel, R.W. Fessenden. Rate constants and mechanism of reaction of SO4·- with aromatic-compounds. J Am Chem Soc, 99 (1) (1977), pp. 163-164.
[28]
G.V. Buxton, M. Bydder, G.A. Salmon, J.E. Williams. The reactivity of chlorine atoms in aqueous solution. Part III. The reactions of Cl·- with solutes. Phys Chem Chem Phys, 2 (2) (2000), pp. 237-245.
[29]
National Institute of Standards and Technology (NIST). NDRL/NIST Solution Kinetcis Database on the [Internet]. c 2023 [cited 2023 Mar 30]. Available online: https://kinetics.nist.gov/solution/.
[30]
A.L. Boreen, W.A. Arnold, K. McNeill. Triplet-sensitized photodegradation of sulfa drugs containing six-membered heterocyclic groups: identification of an SO2 extrusion photoproduct. Environ Sci Technol, 39 (10) (2005), pp. 3630-3638.
[31]
S.P. Mezyk, T.J. Neubauer, W.J. Cooper, J.R. Peller. Free- radical-induced oxidative and reductive degradation of sulfa drugs in water: absolute kinetics and efficiencies of hydroxyl radical and hydrated electron reactions. J Phys Chem A, 111 (37) (2007), pp. 9019-9024.
[32]
G.V. Buxton, C.L. Greenstock, W.P. Helman, A.B. Ross. Critical review of rate constants for reactions of hydrated electrons, hydrogen atoms and hydroxyl radicals (·OH/·O-) in aqueous solution. J Phys Chem Ref Data, 17 (2) (1988), pp. 513-886.
[33]
M. Nihemaiti, D.B. Miklos, U. Huebner, K.G. Linden, J.E. Drewes, J.P. Croué. Removal of trace organic chemicals in wastewater effluent by UV/H2O2 and UV/PDS. Water Res, 145 (2018), pp. 487-497.
[34]
L.S. Lian, B. Yao, S.D. Hou, J.Y. Fang, S.W. Yan, W.H. Song. Kinetic study of hydroxyl and sulfate radical-mediated oxidation of pharmaceuticals in wastewater effluents. Environ Sci Technol, 51 (5) (2017), pp. 2954-2962.
[35]
S.Q. Zhou, W.Q. Zhang, J.L. Sun, S.M. Zhu, K. Li, X.Y. Meng, et al. Oxidation mechanisms of the UV/free chlorine process: kinetic modeling and quantitative structure activity relationships. Environ Sci Technol, 53 (8) (2019), pp. 4335-4345.
[36]
W. Li, H.G. Guo, C.J. Wang, Y.L. Zhang, X. Cheng, J.Q. Wang, et al. ROS reevaluation for degradation of 4-chloro-3,5-dimethylphenol (PCMX) by UV and UV/persulfate processes in the water: kinetics, mechanism, DFT studies and toxicity evolution. Chem Eng J, 390 (2020), Article 124610.
[37]
K.H. Guo, Z.H. Wu, C.I. Shang, B. Yao, S.D. Hou, X. Yang, et al. Radical chemistry and structural relationships of PPCP degradation by UV/chlorine treatment in simulated drinking water. Environ Sci Technol, 51 (18) (2017), pp. 10431-10439.
AI Summary AI Mindmap
PDF(1277 KB)

Accesses

Citations

Detail

Sections
Recommended

/