Rapid degradation of p-arsanilic acid with simultaneous arsenic removal from aqueous solution using Fenton process

• p-ASA could be easily leached out of animal manure due to its high water solubility.
• Fenton process quickly oxidized p  -ASA, producing As(V), NH4+NH4+ and organic products.
• As(V) formed was also efficiently removed through adsorption on the precipitate.
• The treatment conditions were optimized for various types of water matrices.
• Fenton process is promising for controlling arsenic pollution brought by animal waste.

Although banned in some developed countries, p-arsanilic acid (p-ASA) is still used widely as a feed additive for swine production in many countries. With little uptake and transformation in animal bodies, nearly all the p-ASA administered to animals is excreted chemically unchanged in animal wastes, which can subsequently release the more toxic inorganic arsenic species upon degradation in the environment. For safe disposal of the animal wastes laden with p-ASA, we proposed a method of leaching the highly water-soluble p-ASA out of the manure first, followed by treatment of the leachate using the Fenton process to achieve fast oxidation of p-ASA and removal of the inorganic arsenic species released (predominantly arsenate) from solution simultaneously. The effects of solution pH, dosages of H2O2 and Fe2+, and the presence of dissolved organic matter (DOM) on the treatment efficiency were systematically investigated. Under the optimum treatment conditions (0.53 mmol L−1 Fe2+, 2.12 mmol L−1 H2O2, and initial pH of 3.0), p-ASA (10 mg-As L−1) could be completely oxidized to As(V) within 30 min in pure water and 4 natural water samples, and at the final pH of 4.0, the residual arsenic levels in solution phase were as low as 1.1 and 20.1–43.4 μg L−1 in the two types of water matrixes, respectively. The presence of humic acid significantly retarded the oxidation of p-ASA by scavenging HO, and inhibited the As(V) removal through competitive adsorption on ferric hydroxide. Due to the high contents of DOM in the swine manure leachate samples (TOC at ∼500 mg L−1), much higher dosages of Fe2+ (10.0 mmol L−1) and H2O2 (40.0 mmol L−1) and a longer treatment time (120 min) were required to achieve near complete oxidation of p-ASA (98.0%), while maintaining the levels of residual arsenic in the solution at <70.0 μg L−1. The degradation pathway of p-ASA in the Fenton process was proposed based on the major degradation products detected. Together, the results demonstrate that the Fenton process is promising as an efficient, robust, and low-cost treatment method for controlling the risk of p-ASA in the animal wastes generated at factory farms.

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