A review on TiO2/g-C3N4



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A review on TiO2

Type of heterojunction

Pollutant

Conc. of catalyst (gL−1)

Conc. of pollutant (mgL−1)

Degradation time (minutes)

Light source

% degradation

No. of times greater than g-C3N4

Times greater than TiO2

Reference

Mesoporous

RhB

2.0

4.79

80

350 W xenon arc lamp (λ > 420 nm)

100

3.1

7.2

[124]

Mesoporous

RhB

1.0

10

180

500 W xenon lamp λ > 400nm

100

2.5

negligible

[118]

Mesoporous

Phenol

0.5

10

60

500 W Hg
(Xe) λ < 420 nm

……

8.5

negligible

[212]

Core-Shell

tetracycline

1.0

20

----

300 W xenon lamp

-------

2.3

2

[132]

Core-Shell

Phenol




5

360

500W Xe lamp (λVis ≥ 450 nm

……

7.2

---

[137]

Core-Shell

RhB

1.33

4.79

100

300 W Xe arc lamp λ > 400nm

93.3

1.4

3

[109]

Core-Shell

congo red (CR),

------

--------

120

simulated
sunlight

97

1.5

5

[108]

2D-0D

RhB

0.4

10

240

300 W Xe lamp λ > 400nm

98.5

10

40

[213]

2D-0D

Acid Orange 7 (AO7)

1.0

17.5

60

250 W tungsten-halogen lamp λ ∼380-800 nm.

80

2

1.6

[214]

2D-0D

RhB

1.0

10

300

500W Xenon lamp(λ > 420 nm)

84

2.5

3.95

[215]

2D-0D

methylene
blue (MB)

1.0

10

360

500W Xenon lamp λ > 420 nm)

-------

3.5

8

159

2D-0D

methyl orange (MO)

1.0

5

180

350W Xenon lamp

80.33

2.80

negligible

[156]

2D-0D

RhB

40mg

10

80

30 W LED light

-------

4.56

3.87

[211]

2D-0D

MO

1.0

10

90

300 W Xe lamp (λ > 420 nm).

80

4

3.2

[216]

2D-0D

RhB

0.8

10

420

24 W visible-light lamp

------

1.8

1.66

[217]

2D-0D

Isoniazid

0.2

50

240

UV light

79.5

3.36

1.1

[168]

2D-1D TGCN heterojunction

TiO2 nanobelts/g-C3N4 nanosheets

MO

1.0

10

120

300 W Xe lamp, λ > 420 nm).

95.1

6.12

9.56

[147]

g-C3N4/TiO2 (NT)

RhB

0.4

5

60

65W
CFL lamp

96.7

2.33

negligible

[112]

g-C3N4/TiO2 (NR)

RhB

0.4

5

60

65W
CFL lamp

94.5

2.0

negligible

[112]

g-C3N4/TiO2 nanotube

2-chlorophenol

0.5

30

180

Visible light

96.6

--

--

[173]

g-C3N4/TiO2 nanotube

Isoniazid

0.2

50

240

UV light

90.8

4.04

1.18

[168]

2D-2D

RhB

1.0

20

120

300 W Dy lamp λ > 420 nm).

97

1.2

3.2

[218]

2D-2D

Cr (VI)

1.0

10

120

300 W Dy lamp λ > 420 nm

75

1.92

1.15

[218]

2D-2D

MO

0.3

10

15

300 W, Xe arc lamp

98

3.2

2.33

[100]

2D-2D

NO

20 mg

40

60

500 W commercial tungsten halogen lamp

12.6

5.8

---

[219]

3.2.2.2. Kinetics study of photodegradation
According to Ma et al, the photo decomposition of RhB over TGCN follows pseudo-first-order kinetic model as per the Eq. (17) [109].(17)ln C0/Ct = ktWhere k is the rate constant, C0 equilibrium adsorption concentration of RhB at dark after 2 h and Ct is concentration of RhB after time t mins under visible light irradiation. The k value of photoccatalytic degradation of RhB by TGCN heterojunction was found to be 0.058 min−1 which was quite higher than that of TiO2 (0.00056 min−1) and g- C3N4 nanosheets (0.017 min−1). The heterojunction showed an enhanced efficiency of 103.6 and 3.4 times greater than that of TiO2 and g-C3N4 nanosheets respectively. The result signified that the heterojunction endowed a conducive path for the exodus of photon induced carriers which boosted the photocatalytic activity [154]. The k value also depended on the amount of g-C3N4. The highest k value of TGCN core-shell structure was found to be 2.1 × 10–2 min–1for an optimal g-C3N4 content of 15 %. The value of k was declined to 1.5 × 10–2 min–1 on increasing g-C3N4 content to 20 %. This might be attributed to the diminution of magnitudes and quality of effective interfaces formed between g-C3N4 shell and TiO2 core. Moreover, the increase in thickness of g-C3N4 shell (20 %) on TiO2 core led to weaker reflection of light within the interior parts of sphere and hence, utilization of light was decreased [109].
4. Stability of TGCN heterojunction
The practical applicability of a photocatalytic system depends on its stability and reusability. The recycling tests for hydrogen generation and pollutant degradation provide information to assess the stability and recyclability of TGCN heterostructure system [198,230,231]. Li et al have shown that TGCN heterojunction displayed a steady H2 evolution for five cycles of photocatalytic reaction in 30 h without apparent deactivation, indicating a favourable photo-catalytic stability and excellent reproducibility [197]. Stability of the heterostructure was also confirmed form XRD, FTIR, TEM and SEM studies. Yang et al demonstrated by analysing the XRD pattern [Fig. 9(a)] and TEM image [Fig. 9(b) and (c)] that the crystal structure and morphology of heterojunction were retained after four cycles [154]. Hao and his co-workers confirmed that chemical structures of the heterosturcture photocatalyst would not undergo any change after 4 cycles of photodegradation of RhB as the FT-IR patterns [Fig. 9(d)] of the reused photocatalyst had not changed significantly in comparison to as-prepared one [124]. SEM images [Fig. 9(e) and (f)] revealed that the g-C3N4 on the surface of TiO2 hollow microspheres remained almost unchanged after five cycles suggesting excellent stability and reusability [109]. All such characteristics established that TGCN heterojunction can be a robust photocatalyst with excellent stability and laid the foundation for its industrial application.


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Fig. 9. (a) XRD patterns of TGCN fresh and used (after four cycles) samples, TEM images of (b) fresh, (c) used (after four cycles) TGCN samples (Reproduced from Ref. No. [154]), (d) FTIR spectra of fresh and used (after four cycles) samples of TGCN heterojunctions (Reproduced from Ref. No. [124]), SEM images (e) fresh, (f) used samples (after five cycles) of core-shell TGCN hollow microspheres (Reproduced from Ref. No. [109]).
5. Conclusion and perspectives
TGCN composite can be recognised as a robust, environmentally benign as well as sustainable photocatalyst for generation of renewable H2 energy and degradation of pollutants to curb unpredictably increasing energy crisis vis-a-vis alarmingly rising environmental pollution. Present review briefly summarised the synthesis principles for construction of TGCN heterostructure with systematically highlighting the limitations underlying in type-II and Z-scheme heterojunction. A comprehensive overview was made on designing strategies and advantages of morphology based TGCN heterojunctions such as mesoporous, core-shell, point-to-face (0D/2D), line-to-face (1D/2D) and face to face (2D/2D) architectures. Combination of TiO2 with g-C3N4 enables the heterojunction to absorb radiation from UV and visible region. Morphology based heterojunctions exhibited enriched light absorption range in the visible region due to the presence of g-C3N4, Ti3+ and oxygen vacancy. In particular, the band bending at the interface of 2D/2D heterojunction minimises the local band gap energy and widens the absorption range for visible light absorption. Morphology based TGCN heterostructure provides an intimate interfacial contact that enhanced charge transfer ability to suppress recombination of charge carriers for significantly high photocatalytic activity. For instance, photo-generated carriers migrate efficiently through N O Ti covalent heterojunction and the recombination of charge carriers is comprehensibly prohibited. Overall, morphology based TGCN heterostructure can successfully be applied for efficient photocatalytic/ photoelectrochemical H2 generation and photodegradation of various pollutants by harnessing solar radiation leading to sustainable development. This was pictorially presented in Scheme 4. Despite significant development in photocatalytic performance of morphology based TGCN heterostructure, the efficiency is still less from the expectation, which restricted these photocatalysts from large scale application and commercialisation. Therefore, following efforts should be made to address this challenge.
(i)
Though most of researches have focussed on increasing light absorption range and efficient migration of charge carriers across the interface for enhanced performance, the activity is unsatisfactory because of poor adsorption affinity for pollutants. Ample active adsorption sites on the photocatalyst surface led to substantial contact with the pollutants, which in turn promoted the photocatalytic reaction commendably. The best way to increase the adsorption ability is to conspicuously enhance the surface area which lies far from the expectation. This could be possible by introducing porosity through textural modifications.
(ii)
TGCN heterojunction system exhibited excellent stability and reproducibility up to maximum of five cycles which is needed to be increased. Further, attention should be given for easy and quick recycling without which the technology cannot be implemented for scale up.
(iii)
Although morphology based TGCN heterojunction extends visible-light absorption to longer wavelengths, the absorption range is required to be increased further even up to near infra-red in order to utilize complete solar spectrum.
(iv)
Despite excellent charge separation and migration process occurs through an intimate interfacial contact obtained by means of morphology based TGCN heterojunction, the prime challenge appears before the scientific community to develop a thorough understanding on the mechanism involved in rapid charge transfer process in order to further hasten photocatalytic performance.
(v)
Large number of recent studies has proven that morphology based TGCN heterojunction is a versatile candidate for photocatalytic and photoelectrochemical applications. The exponential growth of this system will undoubtedly continue in future. However, there are enough opportunities and challenges, which will explore further research in improving its photocatalytic /photoelectrochemical performance. Though the present system is extensively investigated for photocatalytic H2 generation and pollutant degradation, there is ample scope for the future to thoroughly study other aspects of photocatalysis particularly CO2 reduction. Some important aspects like charge dynamics, optical absorption and electronic band structure are needed to be deeply studied through density functional theory (DFT) computations along with experimental verifications for further improving photocatalytic activity. Photoelectrochemical activity evaluation with respect to H2 generation and O2 evolution is required to be deeply studied with the help of TGCN heterojunction. Emphasis must be given by the researchers in future to achieve much higher photocurrent densities.
(vi)
By and large, it is indispensable to transform this lab-scale research in to industrial scale in order to make TGCN heterojunction as a next generation pragmatic photocatalytic system.


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Scheme 4. Visible light driven morphology based TGCN heterojunctions towards sustainable development through efficient photocatalytic/ photoelectrochemical energy generation and environmental remediation.

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