Abstract

The dewaterability of sludge from biological sewage treatment plants is extremely poor since the highly hydrophilic biomacromolecules. This work developed a new polyferric sulfate-catalyzed ozonation (PFS/O 3 ) process to disintegrate sludge flocks and extracellular hydrophilic substrates for liberating bound water. With 40 mg/gTS PFS catalyzing 60 mg/gTS O 3 , bound water content declined to 1.42 g/gTS, and water content of dewatered sludge dropped to 59.79%. Meanwhile, microbial cells were inactivated by 47.3%, and extracellular protein-like components were degraded substantially, rendering the neutral potential and low apparent viscosity. PFS/O 3 treatment significant facilitated CHO-compound decomposition, reactions of nitrogenous groups, and P-containing biomolecule release. And more hydrophobic groups were exposed on the bio-matrix surface. Besides, polyhydroxy Fe as skeleton builder reconstructed sludge drainage passages for more water permeation. The predominant mechanism for enhancing sludge dewaterability in PFS/O 3 process was the oxidation role of improved • OH, and the chemical reaction chains were proposed tentatively. Moreover, this process simultaneously removed 26.95%–60.05% heavy metals and 31.18%–80.91% polycyclic aromatic hydrocarbons in dewatered sludge, and its chemical cost was preliminarily estimated as 88.80 USD$/tonTS. Therefore, the PFS/O 3 process was of great prospect and practical value in sludge treatment for dewatering and detoxification. • A new PFS-catalyzed O 3 process assisted sludge deep dewatering and detoxification. • EPS conformation turned to be loosened with more hydrophobic groups exposed. • Molecular composition and transformation of DOM were shown by ESI FT-ICR MS. • Chemical reaction mechanism of PFS-catalyzed O 3 was put forward for the first time. • Polyhydroxy Fe serving as supporting skeleton rebuilt multihole drainage passages.

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