| TiO2–biomass |
Starbon |
Ti |
Phenol photodegradation |
150 mL – 50 ppm |
Re: 75% |
4 h |
Adsorption and photodegradation |
Ultrasound sonication |
77
|
| TiO2–SWP700 |
Soft wood pellets |
Ti |
Phenol photodegradation |
150 mL – 50 ppm |
Re: 64% |
4 h |
Adsorption and UV + Vis light irradiation |
Ultrasound sonication |
28
|
| Rc: (∼59–67%)/5 times |
| TiO2–wood charcoal |
Pine wood |
Ti |
Bisphenol A photodegradation |
50 mL – 20 ppm |
Re: 80% |
18 h |
Adsorption and photodegradation |
Dip-sol-gel method |
38
|
| N–TiO2–C |
Waste plum stones |
Ti |
Methylene blue photodegradation |
125 mL – 25 ppm |
Re: 100% |
3 h |
Adsorption and photodegradation |
Multi-step pyrolysis and slurry method |
29
|
| TiO2–bamboo |
Bamboo |
Ti |
Methylene blue photodegradation |
200 mL – 30 ppm |
Re: 99% |
1.5 h |
Adsorption and UV + Vis light irradiation |
Hydrothermal carbonization and sol–gel methods |
33
|
| Rc: ∼100%/4 times |
| g-C3N4–biochar |
Chestnut leaf biomass |
|
Methylene blue photodegradation |
20 mL – 4.8 ppm |
Re: 38% |
4 h |
Photodegradation |
Multi-step thermal polycondensation |
37
|
| S-activated carbons |
Activated carbon |
|
Methylene blue photodegradation |
125 mL – 25 ppm |
Re: 100% |
4 h |
Adsorption and photodegradation |
Multi-step heating process |
75
|
| N–TiO2–Fe3O4–biochar |
Agar |
Fe, Ti |
Methylene blue photodegradation |
10 mL – 400 ppm |
Re: 100% |
3 h |
Adsorption, photodegradation, and Fenton-like degradation |
Single-step thermal polycondensation |
Our study |
| Rc: (89–100%)/5 times |
| TiO2-coated biochar |
Ramie bar |
Ti |
Safranin T photodegradation |
|
Re: 231.9 mg g−1
|
2 h |
Adsorption and photodegradation |
Sol–gel method |
41
|
| Rc: (167–222 mg g−1)/6 times |
| TiO2–sludge and wheat husks |
Sludge and wheat husks |
Ti |
Reactive Blue 69 photodegradation |
20 ppm/1.5 g L−1 dose |
98% |
1.3 h |
Ultrasound irradiation |
Sol–gel method |
32
|
| TiO2–guanidine–(Ni,Co)–Fe2O4
|
Biomass |
Ti, Ni, Co, Fe |
Malic acid photodegradation |
0.5 mmol/50 mL water |
Re: conversion = 60%, acetic acid = 10%, formic acid = 77%, oxalic acid = 7%, CO2 = 8% |
1.5 h |
Photodegradation |
Hydrothermal process |
59
|
| TiO2–corn cob |
Corn cob |
Ti |
Sulfamethoxazole photodegradation |
100 mL – 10 ppm |
Re: 90% |
3 h |
Adsorption and UV light irradiation |
Sol–gel method |
25
|
| Rc: (90–92%)/3 times |
| TiO2–reed straw |
Reed straw |
Ti |
Sulfamethoxazole photodegradation |
160 mL – 10 ppm |
Re: 91% |
3 h |
Adsorption and UV light irradiation |
Sol–gel method |
34
|
| Rc: (86–91%)/5 times |
| g-C3N4–FeVO4–Fe@NH2–biochar |
Pine needles |
Fe, V |
Methyl paraben (MeP) and 2-chlorophenol (2-CP) photodegradation |
100 mL – 20 ppm |
Re: 98.4% of MeP |
1.5 h |
Adsorption, photocatalysis, and photo-ozonation |
Multi-step thermal treatment, acid treatment, and ammonia treatment |
35
|
| Rc: (97–98%)/6 times |
| Re: 90.7% of 2-CP |
| Rc: (89–91%)/6 times |
| ZrO2–sludge and wheat husks |
Sludge and wheat husks |
Zr |
Reactive Yellow 39 photodegradation |
20 ppm/1.5 g L−1
|
Re: 98% |
1.2 h |
Ultrasound irradiation |
Modified sonochemical and sol–gel method |
36
|
| BiOX (X = Cl or Br)–biochar |
|
Bi |
Methyl orange photodegradation |
50 mL (0.03 mM) |
Re: 10% BiOBr = 81% |
2.5 |
Photodegradation |
Hydrolysis method |
39
|
| Re: 5% BiOCl = 38% |
| TiO2–SWP700 |
Soft wood pellets |
Ti |
Methanol oxidation |
(0.9% + 99.1%) phenol + air-flow rate of 25 cm3 min−1
|
Re: conversion = 88%, CO2 = 20%, methyl formate yield = 88% |
|
UV + Vis light irradiation |
Ultrasound sonication |
28
|
| TiO2–chitosan |
Chitosan |
Ti |
Film electrodes |
|
|
|
|
Solvothermal |
31
|
| Au–TiO2/AC |
Waste plum stones |
Au, Ti |
H2 production |
|
−22.5 mM at visible light, and −33 at UV light |
|
UV light irradiation |
Multi-step heating and slurry method |
78
|