Degradation of 2,4-dichlorophenoxyacetic acid by UV 253.7 and UV-H2O2: Reaction kinetics and effects of interfering substances
Author/Creator
Author/Creator ORCID
Date
Type of Work
Department
Program
Citation of Original Publication
Asok Adak, et.al, Degradation of 2,4-dichlorophenoxyacetic acid by UV 253.7 and UV-H2O2: Reaction kinetics and effects of interfering substances, Emerging Contaminants Volume 5, 2019, Pages 53-60, https://doi.org/10.1016/j.emcon.2019.02.004
Rights
Attribution-NonCommercial-NoDerivatives 4.0 International (CC BY-NC-ND 4.0)
This item is likely protected under Title 17 of the U.S. Copyright Law. Unless on a Creative Commons license, for uses protected by Copyright Law, contact the copyright holder or the author.
This item is likely protected under Title 17 of the U.S. Copyright Law. Unless on a Creative Commons license, for uses protected by Copyright Law, contact the copyright holder or the author.
Abstract
This work investigates the degradation of 2,4-dichlorophenoxy acetic acid (2,4-D) using UV irradiation and the UV-H₂O₂ advanced oxidation process (AOP). For UV irradiation at 253.7 nm, ∼66% degradation was observed for a fluence of 20 J cm⁻² and the apparent fluence-based, pseudo-first-order rate constant for 2,4-D was 5.77 (±0.66) × 10⁻⁵ cm² mJ⁻¹. With the UV-H₂O₂ AOP, approximately 97% degradation was observed for a fluence of 700 mJ cm⁻². Due to production of hydroxyl radicals, the apparent fluence-based rate constant was 100 times higher than that for direct UV photolysis. The effects of H₂O₂ dose, initial 2,4-D concentration, and water quality parameters, including pH (4–8), alkalinity (0–5 mM HCO3−), nitrate concentration (0–1 mM as NO3−), and ionic strength (0–17 mM as NaCl), were studied. The observed rate constants were dependent on pH, alkalinity, and nitrate concentration. The degradation of 2,4-D by the UV-H₂O₂ system was also examined in a real surface water. The observed fluence-based rate constant in the surface water matrix was 2.6 (±0.3) × 10⁻³ cm² mJ⁻¹, and this value was similar to a distilled water matrix containing the same alkalinity and pH. In addition, the biodegradability of UV and UV-H₂O₂ treated wastewater increased with irradiation time, suggesting that transformation products can be degraded by biological processes. Based on this study, the UV-H₂O₂ process represents a viable treatment method to transform 2,4-D into benign products.
