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
|