Study of diclofenac removal by the application of combined zero-valent iron and calcium peroxide nanoparticles in groundwater
-
Abstract: Diclofenac (DCF) is one of the most frequently detected pharmaceuticals in groundwater, posing a great threat to the environment and human health due to its toxicity. To mitigate the DCF contamination, experiments on DCF degradation by the combined process of zero-valent iron nanoparticles (nZVI) and nano calcium peroxide (nCaO2) were performed. A batch experiment was conducted to examine the influence of the adding dosages of both nZVI and nCaO2 nanoparticles and pH value on the DCF removal. In the meantime, the continuous-flow experiment was done to explore the sustainability of the DCF degradation by jointly adding nZVI/nCaO2 nanoparticles in the reaction system. The results show that the nZVI/nCaO2 can effectively remove the DCF in the batch test with only 0.05 g/L nZVI and 0.2 g/L nCaO2 added, resulting in a removal rate of greater than 90% in a 2-hour reaction with an initial pH of 5. The degradation rate of DCF was positively correlated with the dosage of nCaO2, and negatively correlated with both nZVI dosage and the initial pH value. The order of significance of the three factors is identified as pH value > nZVI dosage > nCaO2 dosage. In the continuous-flow reaction system, the DCF removal rates remained above 75% within 150 minutes at the pH of 5, with the applied dosages of 0.5 g/L for nZVI and 1.0 g/L for nCaO2. These results provide a theoretical basis for the nZVI/nCaO2 application to remove DCF in groundwater.
-
Table 1. Crystal plane index of nZVI
Diffraction angle (°) 44.7 65.0 82.3 Crystal plane distance (Å) 2.025 7 1.433 7 1.170 6 Table 2. Crystal plane index of nCaO2
Diffraction
angle (°)30.1 35.6 47.3 51.6 53.2 Crystal plane
distance (Å)2.966 6 2.519 8 1.920 2 1.769 9 1.720 3 Table 3. Dosages of nZVI and nCaO2 in continuous-flow experiments
nZVI (g/L) nCaO2 (g/L) 1 0.05 0.2 2 0.1 1.0 3 0.5 1.0 4 0.75 1.0 Table 4. Analysis of variance of DCF degradation model
Parameter Square sum F value p value Model 23 202.18 153.88 < 0.000 1 A nZVI 468.18 18.63 0.001 5 B nCaO2 33.62 1.34 0.274 3 C pH 14 179.28 564.24 < 0.000 1 A2 1 146.32 45.62 < 0.000 1 B2 934.78 37.20 0.000 1 C2 5 733.09 228.14 < 0.000 1 Table 5. Optimized condition of DCF degradation
nZVI dosage (g/L) nCaO2 dosage (g/L) pH value DCF degradation (%) 0.045-0.055 0.190-0.212 5.0 94.9-95.7 -
Abraham N, Daniel C. 2008. Calcium peroxide (CaO2) for use in modified Fenton chemistry. Journal of Hazardous Materials, 152(3): 1164-1170. doi: 10.1016/j.jhazmat.2007.07.096 Bin W, Shu-bo D, Jun H, et al. 2013. Environmental risk assessment and control of emerging contaminants in China. Environmental Chemistry(7): 1129-1136. doi: 10.7524/j.issn.0254-6108.2013.07.003 Einsiedl F, Radke M, Maloszewski P. 2010. Occurrence and transport of pharmaceuticals in a karst groundwater system affected by domestic wastewater treatment plants. Journal of Contaminant Hydrology, 117(1): 26-36. doi: 10.1016/j.jconhyd.2010.05.008 Forrez I, Carballa M, Verbeken K, et al. 2010. Diclofenac oxidation by biogenic manganese oxides. Environmental Science and Technology, 44(9): 3449-3454. doi: 10.1021/es9027327 Gomes DS, Gando-Ferreira LM, Quinta-Ferreira RM, et al. 2018. Removal of sulfamethoxazole and diclofenac from water: Strategies involving O3 and H2O2. Environmental Technology, 39(13): 1658-1669. doi: 10.1080/09593330.2017.1335351 Joo SH, FEITZ AJ, WAITE TD. 2004. Oxidative degradation of the carbothioate herbicide, molinate, using nanosoale zero-valent iron. Environmental Science and Technology, 38(7): 2242-2247. doi: 10.1021/es035157g Jurado A, Walther M, Díaz-Cruz MS. 2019. Occurrence, fate and environmental risk assessment of the organic microcontaminants included in the Watch Lists set by EU Decisions 2015/495 and 2018/840 in the groundwater of Spain. Science of the Total Environment, 663: 285-296. doi: 10.1016/j.scitotenv.2019.01.270 Li R, Jin X, Megharaj M, et al. 2015. Heterogeneous Fenton oxidation of 2,4-dichlorophenol using iron-based nanoparticles and persulfate system. Chemical Engineering Journal, 264: 587-594. doi: 10.1016/j.cej.2014.11.128 Liang W, Dai CM, Zhou XF, et al. 2014. Application of zero-valent iron nanoparticles for the removal of aqueous zinc ions under various experimental conditions. Plos One, 9(1): e85686. doi: 10.1371/journal.pone.0085686 Liang W, Zhou NQ, Dai C M, et al. 2020. Zero-valent iron nanoparticles and its combined process for diclofenac degradation under various experimental conditions. Polish Journal of Environmental Studies, 30(2): 1279-1288. doi: 10.15244/pjoes/123921 Mikhailov I, Komarov S, Levina V, et al. 2017. Nanosized zero-valent iron as Fenton-like reagent for ultrasonic-assisted leaching of zinc from blast furnace sludge. Journal of Hazardous Materials, 321: 557-565. doi: 10.1016/j.jhazmat.2016.09.046 Muhammad U, Hamidi Abdul A, Mohd Suffian Y. 2010. Trends in the use of Fenton, electro-Fenton and photo-Fenton for the treatment of landfill leachate. Waste Management, 30(11): 2113-2121. doi: 10.1016/j.wasman.2010.07.003 Mutiyar PK, Gupta SK, Mittal AK. 2018. Fate of pharmaceutical active compounds (PhACs) from River Yamuna, India: An ecotoxicological risk assessment approach. Ecotoxicology and Environmental Safety, 150(15): 297-304. doi: 10.1016/j.ecoenv.2017.12.041 Qian Y, Zhou X, Zhang Y, et al. 2013. Performance and properties of nanoscale calcium peroxide for toluene removal. Chemosphere, 91(5): 717-723. doi: 10.1016/j.chemosphere.2013.01.049 Schwaiger J, Ferling H, Mallow U, et al. 2004. Toxic effects of the non-steroidal anti-inflammatory drug diclofenac: Part I: Histopathological alterations and bioaccumulation in rainbow trout. Aquatic Toxicology, 68(2): 141-150. doi: 10.1016/j.aquatox.2004.03.014 Shen J, Ou C, Zhou Z, et al. 2013. Pretreatment of 2,4-dinitroanisole (DNAN) producing wastewater using a combined zero-valent iron (ZVI) reduction and Fenton oxidation process. Journal of Hazardous Materials, 260: 993-1000. doi: 10.1016/j.jhazmat.2013.07.003 Shirazi E, Torabian A, Nabi Bidhendi G. 2013. Carbamazepine removal from groundwater: Effectiveness of the TiO2/UV, nanoparticulate zero-valent iron, and Fenton (nZVI/H2O2) processes. Clean - Soil Air Water, 41(11): 1062-1072. doi: 10.1002/clen.201200222 Singh R, Misra V, Mudiam MKR, et al. 2012. Degradation of γ-HCH spiked soil using stabilized Pd/Fe0 bimetallic nanoparticles: Pathways, kinetics and effect of reaction condition. Journal of Hazardous Materials, 237-238: 355-364. doi: 10.1016/j.jhazmat.2012.08.064 Stefaniuk M, Oleszczuk P, Ok YS. 2016. Review on nano zerovalent iron (nZVI): From synthesis to environmental applications. Chemical Engineering Journal, 287: 618-632. doi: 10.1016/j.cej.2015.11.046 Sun YP, Li XQ, Cao J, et al. 2006. Characterization of zero-valent iron nanoparticles. Advances in Colloid and Interface Science, 120(1-3): 47-56. doi: 10.1016/j.cis.2006.03.001 Vieno N, Sillanpää M. 2014. Fate of diclofenac in municipal wastewater treatment plant – A review. Environment International, 69: 28-39. doi: 10.1016/j.envint.2014.03.021 Vilardi G, Sebastiani D, Miliziano S, et al. 2018. Heterogeneous nZVI-induced Fenton oxidation process to enhance biodegradability of excavation by-products. Chemical Engineering Journal, 335: 309-320. doi: 10.1016/j.cej.2017.10.152 Vymazal J, Dvořáková Březinová T, Koželuh M, et al. 2017. Occurrence and removal of pharmaceuticals in four full-scale constructed wetlands in the Czech Republic–the first year of monitoring. Ecological Engineering, 98: 354-364. doi: 10.1016/j.ecoleng.2016.08.010 Wang HF, Zhao YS, Li TY, et al. 2016. Properties of calcium peroxide for release of hydrogen peroxide and oxygen: A kinetics study. Chemical Engineering Journal, 303: 450-457. doi: 10.1016/j.cej.2016.05.123 Zhang W, Gao H, He J, et al. 2017. Removal of norfloxacin using coupled synthesized nanoscale zero-valent iron (nZVI) with H2O2 system: Optimization of operating conditions and degradation pathway. Separation and Purification Technology, 172: 158-167. doi: 10.1016/j.seppur.2016.08.008