Fouling of ion exchange membranes used in the electrodialysis reversal advanced water treatment: A review.

Electrodialysis self-reversal (EDR) technology has attracted in the treatment of water for domestic and industrial uses. The self-reversal consists of a frequent reversal of the direction of current between the EDR-cell electrodes to combat fouling of ion exchange membranes (IEMs). Irrespective of the EDR self-cleaning processes, the role of natural organic matter and their complexing ability with metal ions on IEMs fouling is partially understood. The objective of this review is to identify the research gaps present in the elucidation of IEM fouling routes. The common IEMs' foulants are identified, and several fouling mechanisms are briefly discussed. The effectiveness of self-cleaning mechanisms to reduce IEMs fouling is also be discussed. Dissolved organic carbon (DOC) possesses high chelation which forms metal complexes with di and trivalent cations found in water. The role of ternary complexes, e.g. M2+/3+-DOC and membrane surface, on membrane fouling via surface bridging, are also addressed. Finally, mitigation methods of IEMs membrane fouling are also discussed.

Photodegradation of triphenylamino methane (magenta) by photosensitizer in oxygenated solutions.

Reactive oxygen species (ROS), namely superoxide anion (O2*-, singlet oxygen (1O2), are potentially important substances for the mineralization of toxic organic molecules. The utility of hematoporphyrindihydrochloride (HPDHC) as a photosensitizer to generate ROS and their subsequent role in the destruction of magenta (MaG) in aqueous media is the main concern. The light irradiation of oxygenated aqueous solution of HPDHC and 1.5 x 10(-5) mol dm(-3) MaG at pH 3 yielded micromolar levels of NO3(-) ions. A higher rate of photodegradation (1.02 mol dm(-3) min(-1)) at pH 3 was observed compared to that of at pH 6 (0.68 mol dm(-3) min(-1)). Experiments were carried out in the presence of 1,4-diazabicyclo[2.2.2]octane (DABCO) as singlet oxygen (1O2) quencher and bezoquinone (BQ) as superoxide anion (O2*-) quencher. Only BQ was able to stop photodegradation suggesting that the photooxidation of MaG is mainly caused by O2*-, which is generated by an electron transfer from the excited HPDHC to ground-state oxygen. The presence of iron(II) at pH 3.0, compared to that without iron(II), showed a higher rate of photodegradation due to the formation of extremely reactive hydroxyl radicals (HO*) upon dismutation of O2*- anion through H2O2 intermediate. The formation of O2*-, H2O2, and HO* is therefore evident, which may act as active sites for subsequent photodegradation of MaG.