Table 1.
Activation approaches | Main reaction for sulfate radicals production | Mechanism | Key parameters | References | |
---|---|---|---|---|---|
Physical activation | Heating |
(PS) (PMS) |
Fission of O–O bond | (i) Higher temperature can cleave O–O bond, whereas excessive temperature may cause side effects (ii) Owing to huge energy demand, not suitable for large-scale sewage treatment |
Zhao et al., 2013; Wang and Wang, 2018 |
UV |
(PS) (PMS) |
Fission of O–O bond | Usually under 254 nm wavelength, depending on dissolved oxygen concentration | Yang Q. et al., 2019 | |
Ultrasound |
(PS) |
Fission of O–O bond Hydrolysis of water molecules |
Similar to heating activation | Nasseri et al., 2017 | |
Chemical activation | Alkaline activation |
(PS) H2O2 → 2OH· (PMS) |
Hydrolysis of PS and PMS to hydrogen peroxide | Often pH > 11 For PMS activation, 1O2 is the predominant radical specie, whereas SO/OH·/1O2 for PS |
Fernandes et al., 2018 |
Transition metal ions |
(PS) (PMS) |
Single electron transfer | Preparation of catalysts is more economical for a homogeneous system than that of a heterogeneous system | Liu L. et al., 2019 | |
Carbon-based materials |
(PS) (PMS) |
Single electron transfer | Activated carbon is relatively economical | Zhao et al., 2017 |