Skip to main content
. 2022 Oct 4;12(44):28318–28340. doi: 10.1039/d2ra04713f

Advanced oxidation treatment methods for microplastic removal from wastewater.

AOP MP targeted Monitoring methods AOP performance Other parameters Ref.
C,N–TiO2 photocatalysis Polyethylene (PE) beads Mass loss, FTIR measured carbonyl index (CI), microscopy 50 h, mass loss 72% and large increase in CI Visible light LED (400–800 nm), temperature 0–40 °C, pH 3–11, lamp distance 25 cm, 4 L−1 MPs, 4 g L−1 catalyst (optimum removal at pH 3, 0 °C) 219
N–TiO2 photocatalysis PE beads and flakes Mass loss, CI 50 h, mass loss < 5% for all (4.6% HDPE and 1.8% LDPE) Visible light LED (400–800 nm), pH 3, room temperature, 4 g L−1 MPs, lamp distance 21.5 cm 220
ZnO nanorod photocatalysis PE film Microscopy (SEM), mechanical change, CI 175 h, CI increase of 30% Visible light 50 W dichroic halogen ambient air. Deionised water 224
N–TiO2 photocatalysis PE beads Mass loss, SEM, CI 8 h, mass loss < 3% in aqueous solution 27 W visible fluorescent lamp (400–800 nm), room temperature, lamp distance 12 cm, 2 g L−1 MPs 223
PMS/carbon nanospring photocatalysis PE Mass loss, CI, SEM 8 h, 40% mass loss pH 3–11, MPs 5–12 g L−1, temperature 25–160 °C (>150 °C optimum) 227
ZnO photocatalyst supported on glass fibre Polypropylene (PP) Size change, CI, SEM 456 h, 65% reduction in volume Visible light 60 mW cm2, 300 mL min−1 continuous flow treatment of 104 particles per L 225
TiO2 nanoparticle photocatalyst film Polystyrene (PS) Diameter change, DRIFTS, GC-MS 24 h required for removal of 400 nm starting diameter particles 254 nm UV irradiation 221
ZnO nanorod photocatalysis with Pt modification PE film CI, SEM 175 h Visible light 50 W, room temperature, lamp distance 10 cm 222
TiO2 Polyamide (PA) fibre Mass loss, CI, total organic carbon (TOC), SEM 48 h, 94% mass loss UVA irradiation, room temperature, 5 lamp photo reactor 226
Modified TiO2 photocatalysis Poly(methyl methacrylate) (PMMA), PS TOC 7 h, flow reactor UVA irradiation 112 W m2 229
Hydroxy-rich ultrathin BiOCl photocatalysis PE Mass loss 5 h, 6% mass loss 250 W of 420 nm irradiation; MP and catalyst 1 g L−1 228
Photo-Fenton PS SEM, CI, HPLC/MS, contact angle, C : O atomic ratio (XPS) 108 h, CI increase 500 W mercury lamp, 12 g L−1 MPs 231
Fenton PS and high density PE Size distribution, CI, C : O ratio by XPS 1–30 days pH 4, 3 mM Fe, 4.5 mg mL−1 H2O2 232
Fenton PE, PP, polyvinyl chloride (PVC), nylon Microscopy 10 min, minor surface area decrease Room temperature, pH 5, 7 g L−1 MPs, 3–10 mg mL−1 Fe 233
Thermal Fenton PE, PS, PP and polyethylene terephthalate (PET) Mass loss, CI, DSC to determine crystallinity, XRD, SEM, Raman spectroscopy, particle sizing by zetasizer 16 h, 96% mass loss 4 mM Fe2+, 300 mM H2O2 234
Heterogeneous photo Fenton/photocatalysis PP, PVC FTIR, particle diameter by microscopy 7 days, 94–96% size reduction Nano zero valent iron and combined with ZnO/SnOx photocatalysis, 60 mW cm2 visible light 235
Ozonation PE FTIR, XPS 60–180 min, increase in CI Ozone 4–7 mg L−1 236
Ozonation Mixed MPs obtained from real wastewater Particle counting 99.2% removal after tertiary treatment (this includes removal via other methods during the treatment process) Ozone 12.6 mg L−1 for 1 min during tertiary treatment 237
Ozonation, H2O2/ozone PE, PP, PS Adsorption, XRD, SEM, FTIR 10 min, ozone dose of 88 mg L−1 O3 : H2O2 molar ratio of 0.5 238