Volume 46, Issue 6 pp. 1059-1077
Review Article
Open Access

Radiation Models for Computational Fluid Dynamics Simulations of Photocatalytic Reactors

Isabel S. O. Barbosa

Isabel S. O. Barbosa

University of Porto, Laboratory of Separation and Reaction Engineering – Laboratory of Catalysis and Materials (LSRE-LCM), Faculty of Engineering, Rua Dr. Roberto Frias, 4200-465 Porto, Portugal

University of Porto, ALiCE-Associate Laboratory in Chemical Engineering, Faculty of Engineering, Rua Dr. Roberto Frias, 4200-465 Porto, Portugal

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Ricardo J. Santos

Ricardo J. Santos

University of Porto, Laboratory of Separation and Reaction Engineering – Laboratory of Catalysis and Materials (LSRE-LCM), Faculty of Engineering, Rua Dr. Roberto Frias, 4200-465 Porto, Portugal

University of Porto, ALiCE-Associate Laboratory in Chemical Engineering, Faculty of Engineering, Rua Dr. Roberto Frias, 4200-465 Porto, Portugal

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Madalena M. Dias

Madalena M. Dias

University of Porto, Laboratory of Separation and Reaction Engineering – Laboratory of Catalysis and Materials (LSRE-LCM), Faculty of Engineering, Rua Dr. Roberto Frias, 4200-465 Porto, Portugal

University of Porto, ALiCE-Associate Laboratory in Chemical Engineering, Faculty of Engineering, Rua Dr. Roberto Frias, 4200-465 Porto, Portugal

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Joaquim L. Faria

Joaquim L. Faria

University of Porto, Laboratory of Separation and Reaction Engineering – Laboratory of Catalysis and Materials (LSRE-LCM), Faculty of Engineering, Rua Dr. Roberto Frias, 4200-465 Porto, Portugal

University of Porto, ALiCE-Associate Laboratory in Chemical Engineering, Faculty of Engineering, Rua Dr. Roberto Frias, 4200-465 Porto, Portugal

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Prof. Cláudia G. Silva

Corresponding Author

Prof. Cláudia G. Silva

University of Porto, Laboratory of Separation and Reaction Engineering – Laboratory of Catalysis and Materials (LSRE-LCM), Faculty of Engineering, Rua Dr. Roberto Frias, 4200-465 Porto, Portugal

University of Porto, ALiCE-Associate Laboratory in Chemical Engineering, Faculty of Engineering, Rua Dr. Roberto Frias, 4200-465 Porto, Portugal

Correspondence: Prof. Cláudia G. Silva ([email protected]), , Faculty of Engineering, University of Porto, Rua Dr. Roberto Frias, 4200-465 Porto, Portugal.Search for more papers by this author
First published: 09 March 2023
Citations: 1

Abstract

The literature on computational fluid dynamics (CFD) simulations applied to photocatalytic systems is reviewed. CFD simulations referring to three models, namely, P-1, discrete ordinates (DO), and Monte Carlo (MC) models, for simulating radiation distribution in annular photoreactors are addressed and previous works using these models are reviewed. The cases are a three-dimensional (3D) annular photoreactor and a two-dimensional (2D) rectangular enclosure with black walls and the results are compared with the literature. The DO model was selected to solve the radiation transfer equation (RTE) as the most reliable model to fit the radiation distribution inside the reactor. The setting-up of mesh, angular discretization, and boundary conditions for CFD simulation of photocatalytic reactors are addressed. When correctly set, the CFD models show an excellent agreement with the literature results.

1 Introduction

In recent years, photo-assisted technologies have received increasing attention primarily due to the possibility of using the sun as light source, a renewable and economical source of energy that can be used for the photo-activation of several processes, including water treatment 1, 2, chemical synthesis 3, 4, energy production 5, 6, and air treatment 7, 8. The optimization of the photoreactor configuration is crucial for the applicability of this technology. Computational fluid dynamics (CFD) is an efficient design tool to predict and enhance the performance of photocatalytic reactors because it enables the integration of hydrodynamics, mass transfer, reaction kinetics, and photon flux distribution. The models used in the simulations can affect the results obtained. So, the selection of the models is critical in the computational design or numerical studies of photocatalytic reactors 9.

The first works on photocatalysis are dated back to the 20th century 10. Although, only from the 1990s onward the field experienced a boom in the number of publications. Yet, the first research using “CFD” dates to the end of the last year of the 1990s. Fig. 1 shows the annual number of papers until 2022, retrieved from Scopus with the term photocatalysis and CFD in the title, abstract or keywords.

Details are in the caption following the image
Distribution of 451 scientific articles published yearly combining “Photocatalysis” and “CFD” terms. Data queried from Scopus as of October 31, 2022.

Tab. 1 summarizes the CFD models used for the simulation of radiation in different types of photoreactors. Most works consider annular, pipe or plate reactors. Regarding the simulation of radiation, the discrete ordinates (DO) method is the most used. This survey shows the relative novelty of the radiation simulation in the study of photocatalytic reactors with the first work dating from 2003. The number of papers worldwide on this topic is still below 500 (Scopus, data), although presenting a steady yearly increase. The novelty of the field justifies a short tutorial on the implementation of the radiation models along with their review.

Table 1. Review of CFD models for radiation simulation in photoreactors.

Photocatalytic reactor type

Application

CFD models

Radiation source

Ref.

Hydrodynamics

Radiation

Reaction

Pilot-scale annular bubble column

Photodegradation of Bayer liquor

Three-phase flow

DO

UV

11

Turbulent k-ε

Annular slurry pilot-plant photoreactor

Photoxidation of pollutants

Analytical solution of RTE

UV

12

Annular photoreactor

Gas phase vinyl chloride (VC) oxidation

Laminar

Surface reaction

13

Annular photoreactor

Photochemical reactions (no application specifically)

DO

14

Annular dual-lamp photoreactor

No application specifically

DO

UV

15

Annular

Air treatment

Laminar

Surface reaction for trichloroethylene (TCE) oxidation

UV

16

Plate

Photocatalytic oxidation (PCO) of indoor air pollutants

Laminar

LSSE

Oxidation of trichloroethylene

UV-A

17

Photo-CREC-air reactor

Air purification

Turbulent k-ω based Shear Stress Transport (SST)

Mineralization of acetone to carbon dioxide and water

UV

18

Multi-annular reactor

Air Ttreatment

Laminar

Perchloroethylene (PCE) degradation

UV

19

Externally irradiated bubble tank

Pollutant decomposition

Turbulent k-ε

DO

UV-A

20

Multiphase system

Flat plate

Degradation of TCE in a serpentine flow field

Laminar

Degradation of TCE

21

Externally illuminated immobilized catalyst photoreactor

Water treatment

Multiphase

Benzoic acid dissolution

22

Turbulent k-ε

Tubular optical fibers

Water Treatment

Laminar

DO

Photodegradation of oxalic acid

Optical fibers

23

Annular

Photocatalytic treatment of bioaerosols

Turbulent k-ω

UV-A

24

Annular

Air Treatment

Laminar

Acetaldehyde photocatalytic oxidation

UV

25

Plate

Photocatalytic inactivation of spores of Bacillus subtilis

DO

Photocatalytic inactivation of spores of Bacillus subtilis

UV-A

26

Plate

Air treatment

Turbulent k-ε

RTE solution in SPEOS

Acetaldehyde removal

UV

27

Annular

Study of radiation models

ESVE

28

ESDE

LSSE

LSDE

ESVEA

ESVERA

Tubular (immobilized catalyst)

Water treatment

Laminar

DO

Degradation of formic acid

UV

29

Turbulent RSM

Turbulent

Realizable k-ε

Annular

Water treatment

Turbulent AKN

Degradation of benzoic acid

UV

30

Turbulent RSM

Turbulent R k-ε

Turbulent S k-ε

Laminar

Annular slurry

Wastewater treatment

Turbulent k-ε

DT model (discrete transfer)

Degradation of pollutants in CO2 and H2O

UV

31

Multiphase-flow

Corrugated reactor

Air treatment

Laminar

Degradation of formaldehyde

UV

32

CPC (continuous flow reactor with compound parabolic collectors)

Water disinfection

Turbulent S k-ε

Inactivation of E. coli particles

UV

33

Flat plate

Air pollution remediation

Laminar

Degradation of a target pollutant HCOC

UV

34

Arrow-slit, plat-plate flow-through

Photocatalytic deodorization process

Laminar

Radiation field model of LED

Photocatalytic degradation of dimethyl sulfide (DMS)

UV-LED

35

Microchannel reactor

Photocatalytic degradation of salicylic acid (SA)

Laminar

Photocatalytic degradation of salicylic acid (SA)

UV

36

Multiplate reactor

Air/water purification

Monte Carlo model

37

Fluidized-bed reactor

Degradation of pollutants

Photon modeling

38

Annular photocatalytic reactor

Water treatment

Laminar

Mineralization of Rhodamine B

UV

39

Photo-CREC water II annular reactor

Wastewater treatment

MC model

UV

40

Annular photocatalytic reactor

Water purification

Laminar

Mineralization of Rhodamine B

UV

41

Slit-shaped flat-bed photocatalytic reactor

Air treatment

Laminar

Photocatalytic degradation of gaseous acetaldehyde

UVA

42

Circular flow cell

Water treatment

Laminar

Degradation of phenol

UV LEDs

43

RVE (representative volume element) of textile

Degradation of pollutants

Laminar

UV

44

Turbulent

Multitube photoreactor

Air treatment

Laminar

Photocatalytic degradation of gaseous acetaldehyde

UV

45

New reactor based on a stagnation point geometry

VOCs removal applications

Turbulent k-ε

Photocatalytic degradation of acetaldehyde

UV

46

Stacked frame photocatalysis reactor (with impeller)

Production of biofuels from cellulose

Turbulent k-ε

UV

47

Cascade disc Reactor

Environmental purification

Laminar

Benzoic acid dissolution

48

Turbulent

Bubbling twin Reactor

Production of valued-added fuels

Turbulent

CO2 reduction

UV

49

Two-phase

Silicone microreactors

Photocatalytic production of hydrogen

Laminar

Mixture of water-ethanol to produce hydrogen

UV

50

Internal air lift circulating photoreactor

Pollutants degradation

Turbulent S k-ε

51

Three-phase flow

Annular slurry bubble column reactor

Wastewater Treatment

Monte Carlo

UV

52

Annular

Degradation of organic pollutants

Laminar

Mineralization of toluene

UV

53

Gas-phase photocatalytic multitube reactor

Indoor air treatment

Laminar

Ray optics module of Comsol v5.3a

Acetaldehyde degradation

UV-A

54

Turbulent S k-ε

Lab-scale multitube reactor

Air VOCs treatment

Laminar

Ray optics module of Comsol v5.3a

Acetaldehyde degradation

UV

55

Continuous flat-plate photoreactor

Air purification

Laminar

DO

Photocatalytic NOx removal

UV

56

Flat plate

NOx abatement

Laminar

NO2 consumption

57

CPC-PR

Water and air treatment

Turbulent S k-ε

DO

Formaldehyde formation

Solar radiation

58

Production of fine chemicals

Lamellae

Air purification

Laminar

VOCs degradation

UV

59

Photocatalytic multitube reactor

Air pollution remediation

Turbulent k-ε

Ray optics module of Comsol v5.3a

Acetaldehyde degradation

UV

60

Self-made airtight reactor

Air treatment

Turbulent RNG k-ε

Degradation of formaldehyde

UV

61

PCO (photocatlytic oxidation) reactor

Air purification applications

Turbulent k-ω

UV

62

1. Annular reactor

Advanced oxidation processes

DO

UV-A (isotropic emission)

63

2. Tubular with CPC

3. Tubular with LEDs

CPC (parallel emission)

UV-A LEDs (cone-shaped and power-cosine emission)

Photocatalytic microreactor

(Waste)water treatment

Laminar

Photodegradation of 4-nitrophenol

UV-visible

64

Urban Street Canyon

Air pollution treatment

Turbulent RNG k-ω

Photocatalytic oxidation of NOx

UV

65

Flat-plate photocatalytic reactor

Air treatment

Laminar

DO

NOx abatement

8

Annular photoreactor

Water treatment

P-1

MO (methyl orange) dye degradation

UV

66

Parallel-channel microreactor

Water treatment

Laminar

Photodegradation of 4-nitrophenol

UV

67

An urban area

Air treatment

Turbulen Realizable k-ε

Degradation of NOx

UV

68

NETmix reactor

Water/air treatment

MC

LEDs

69

The modeling of photoreactors requires the study of (i) hydrodynamics of the reactor, (ii) radiation transfer equation (RTE), (iii) reaction kinetics, and (iv) mass balance in the light and dark zones of the photoreactors. At first, the hydrodynamics of the system is modeled and simulated, enabling the full spatial description of the flow inside the reactor. The characterization of the radiation field of a photochemical or photocatalytic reactor involves the incorporation of optical phenomena (reflection, refraction, and shadow zones), lamp characteristics, and its position in the photoreactor configuration 70.

The kinetics of the reaction is incorporated in the simulation, which also depends on the radiation distribution inside the reactor. Finally, the mass balance is the heart of the model, integrating the hydrodynamics model, radiation model (emission and scattering-absorption), and kinetic model which includes a quantum yield model. The sequential steps for the modeling of photocatalytic systems are presented in Fig. 2 71, 72. Some studies in Tab. 1 consider only one or two of these components; e.g., some use the CFD to simulate the RTE, while others focus only on the flow in the photoreactor.

Details are in the caption following the image
Sequential steps to model a photocatalytic reactor.

The steps (i) and (ii) can be simulated separately. If the thermal contribution from radiation causes a negligible impact on the flow, the radiation field can be simulated over the hydrodynamics. If the medium is homogeneous regarding light absorption and refraction index, the flow field will have no impact on radiation. The latter is generally not the case in chemical reactors where the concentration distribution of chemical species evolves in space or time 9, 73. The final step is the simulation of mass balance, which requires all the previous steps.

Radiation distribution is a crucial parameter in the simulation of photochemical and photocatalytic systems 74-76. The light intensity distribution inside the reactor is simulated by solving the RTE and it depends on parameters such as type and position of the lamp, reactor geometry, radiation wavelength, the optical properties of the medium, specifications of reactor walls, and operating conditions (inflow and outflow rate, catalyst type and concentrations) 77, 78.

The RTE is an integro-differential equation based on the conservation principle applied to a ray along a path through a medium 79 and can be expressed as:
urn:x-wiley:09307516:media:ceat202200551-math-0001(1)

where urn:x-wiley:09307516:media:ceat202200551-math-0002 is the position vector, urn:x-wiley:09307516:media:ceat202200551-math-0003 is the direction vector, urn:x-wiley:09307516:media:ceat202200551-math-0004 is the scattering direction vector, s (m) is the path length, α (m−1) is the absorption coefficient, n is the refractive index, σs (m−1) is the scattering coefficient, σ (5.669 × 10−8 W m−2K−4) is the Stefan-Boltzmann constant, I (W m−2sr−1) is the radiation intensity which depends on position (urn:x-wiley:09307516:media:ceat202200551-math-0005) and direction (urn:x-wiley:09307516:media:ceat202200551-math-0006), T (K) is the local temperature, ϕ is the phase function, and urn:x-wiley:09307516:media:ceat202200551-math-0007 (sr) is the solid angle. (α + σs) is the optical thickness or opacity of the medium 80.

Therefore, the RTE describes the radiation transport phenomena: the attenuation by absorption (urn:x-wiley:09307516:media:ceat202200551-math-0008), the scattering (out scattering) (urn:x-wiley:09307516:media:ceat202200551-math-0009), and source terms by emission (urn:x-wiley:09307516:media:ceat202200551-math-0010) and by radiation in-scattered from other directions along a path (urn:x-wiley:09307516:media:ceat202200551-math-0011), as shown in Fig. 3 79.

Details are in the caption following the image
Process of radiative transfer for a control volume of a photoreactor.

An exact analytical solution of the RTE is only possible for one-dimension ideal situations, after simplifying assumptions such as uniform radiative properties of the medium and homogeneous boundary conditions 79, 81.

Radiation is present in many engineering problems such as photocatalysis for water treatment and fine chemicals production and most of these systems are multidimensional, the media is heterogeneous, and radiative properties are spectral. The solution of RTE requires the evaluation of scattering and absorption coefficients of the media and of the phase function, which depends on wavelength, fluid composition, type and content of suspended particles, temperature, and pressure 79.

The radiative transfer models can also be applied for immobilized coatings. The immobilized catalyst system presents some advantages when compared with the suspension systems, since at the end of the reaction a separation process is not needed and is particularly useful for scale-up efforts. Claes et al. report the study of a translucent structured photocatalytic reactor, presenting the results of the influence of the base structure on absorption efficiency and mass transfer limitations 82. These reactors are an effective design to scale up photocatalytic processes, enabling the increase of the catalyst loading without increasing the catalyst layer thickness, leading to fewer diffusion limitations 83.

It is assumed that scattering of light and radiation absorption in the catalyst coating can be neglected for some immobilized systems such as optical fibers, coated plates, and monoliths. For photochemical systems carried out at low or medium temperatures, the energy gain due to emission in reaction media can be also neglected 84. The scattering effects can be ignored in homogeneous reaction mixtures because they are rather weak 84. In these cases, the RTE reduces to the Beer-Lambert law 71.

Numerical simulation has gradually become a powerful technique to study the radiative heat transfer in absorbing, emitting, and scattering media because radiation models are capable of simplifying the integro-differential equations and predicting the radiation properties of the media with accuracy 79, 81. CFD is an efficient design tool for photoreactors because it enables the integration of hydrodynamics, reaction kinetics, and photon flux distribution 28, 75. The knowledge of the radiant energy distribution, particularly of the UV fraction, is fundamental in designing and optimizing photoreactors.

Annular geometry is the most commonly used in photoreactors for high-throughput and continuous operation 71. In this configuration, one or more UV lamps are placed in the middle of a cylindrical vessel. Each lamp is enclosed in its quartz sleeve to isolate it from the reacting medium. This photoreactor promotes a non-uniform distribution of radiation, characterized by higher radiation intensities close to the source and lower intensities near the reactor wall, because of the increased photon flux area and the optical thickness. This problem can be minimized if the annular region is reduced or if highly reflective reactor walls are employed instead 71.

The present critical review of radiation modeling in a CFD package is based on a case with an annular geometry proposed by Quan et al. 85.

2 State-of-the-Art

The modeling of photoreactors involves the simulation of fluid flows and the solution of the RTE within the medium. Several methods have been developed to solve the RTE, such as the P-1 model, the discrete ordinates model (DOM), which are approximations of the solution of the RTE, and the Monte Carlo (MC) model, which involves a statistical treatment 50.

In addition to accurately accounting for catalyst activity, the primary motivation for modeling flow and radiation in photocatalytic reactors is to identify regions of poor catalyst illumination 83. The rate of reaction in an immobilized system is related to incident radiation. In this paper, the incident radiation is simulated to evaluate the light intensity distribution in an annular photocatalytic reactor and assess the reliability and accuracy of radiation models. This showcase takes a tutorial approach to show the implementation of radiation modeling, in the present case using ANSYS/Fluent that is a widespread commercial CFD package distributed with built-in radiation models.

2.1 Radiation Models for CFD

The Radiation Models described in this work are those implemented in the commercial software package ANSYS/Fluent. Table 2 summarizes the advantages and limitations of the radiation models.

Table 2. Advantages and disadvantages of P-1, DO, and MC models 80.

Advantages

Disadvantages

P-1 Model

Simple diffusion equation for the incident radiation (G)

All surfaces are considered diffuse

Low computational effort

Loss of accuracy depending on the complexity of geometry

Accurate for large optical thickness cases (αL > 1)

Loss of accuracy if participating media are optically thin

Includes particulate (and anisotropic) scattering

Loss of accuracy at localized heat sources/sinks (overprediction of the radiative heat flux).

Non-gray radiation modeled using a gray-band model

Assumes gray gases

Easily applied to complex geometries with curvilinear coordinates

DO Model

Applicable to all optical thicknesses

High computational effort

Includes particulate and anisotropic scattering

Finite number of radiation directions causes numerical smearing

Radiation in semi-transparent media

Diffuse and specular reflection

High accuracy

MC Model

Wide range of optical thicknesses

High computational cost

Allows quasi-exact solutions

The physical quantities are calculated as surface or volume averages

Some cases are not supported by this model.

Fluent only supports Monte Carlo Model for 3D geometries

2.1.1 P-1 Model

The P-1 radiation model is a widely used numerical method to solve the RTE in heat transfer. The P-1 approximation is the simplest case of the more general P-N model, which is based on the expansion of the radiation intensity into an orthogonal series of spherical harmonics 79, 80, 86. The direction dependence in RTE is integrated out, transforming the RTE into a diffusion equation, which is easy to solve and compatible with the finite volume method 80, 87.

In the P-1 method, for gray radiation the transport equation for the incident radiation (G) (W m−2) is 80:
urn:x-wiley:09307516:media:ceat202200551-math-0012(2)
where n is the refractive index of the medium, α (m−1) is the absorption coefficient, σ (5.67 × 10−8 W m−2K−4) is the Stefan-Boltzmann constant, T (K) is the local temperature, SG (W m−3) is a user-defined radiation source, and Γ (m) is the diffusivity of the incident radiation, which incorporates the effect of absorption, scattering, and phase function, and can be expressed by:
urn:x-wiley:09307516:media:ceat202200551-math-0013(3)

Where σs is the scattering coefficient and C is the linear-anisotropic phase function.

The radiation flux (qr) is obtained by the following expression:
urn:x-wiley:09307516:media:ceat202200551-math-0014(4)
Combining Eqs. 3 and 5, the expression for urn:x-wiley:09307516:media:ceat202200551-math-0015 is obtained and it can be directly substituted into the energy equation to account for heat sources (or sinks) due to radiation 80.
urn:x-wiley:09307516:media:ceat202200551-math-0016(5)

Therefore, incident radiation can be obtained by solving the simpler diffusion equation 87. The non-gray radiation can be modeled using the P-1 model, with a gray-band model.

The first reported work of P-1 model was in 1996, when Sazhin et al. presented the advantages and limitations of the P-1 model for thermal radiation, demonstrating that the P-1 model is expected to make reliable predictions in optically thick and thin media in a simple geometry 86. The P-1 approximation was used to model radiative transfer in a rectangular enclosure in participating media 88, in an annular photoreactor 77, 87, and a closed-conduit reactor 89.

2.1.2 Discrete Ordinates (DO) Model

The DO model transforms the integro-differential form of the RTE into a system of algebraic equations 72. The RTE is solved for a finite number of discrete solid angles, each associated with a vector direction (urn:x-wiley:09307516:media:ceat202200551-math-0017) 80. Thus, the DOM solves the RTE through directional and spatial discretization, giving a set of linear simultaneous equations for the radiation intensity at various points 78. The DO model solves for as many transport equations as there are directions (urn:x-wiley:09307516:media:ceat202200551-math-0018) 79, 80.

The DO model does not involve any simplified assumption other than the discretization of pertinent partial differential equations 78. Therefore, this model is widely used because the obtained results have high accuracy. The DO model considers the integration of the radiative transfer equation calculated as 80, 90:
urn:x-wiley:09307516:media:ceat202200551-math-0019(6)

where the variables are: urn:x-wiley:09307516:media:ceat202200551-math-0020 the radiation intensity, urn:x-wiley:09307516:media:ceat202200551-math-0021 the position vector, urn:x-wiley:09307516:media:ceat202200551-math-0022 the direction vector, urn:x-wiley:09307516:media:ceat202200551-math-0023 the scattering direction vector, α the absorption coefficient of the medium, σs the scattering coefficient, n the refractive index of the medium, σ the Stefan-Boltzmann constant (5.67 × 10−8 W m−2K−4), T the local temperature, ϕ the phase function, and urn:x-wiley:09307516:media:ceat202200551-math-0024 the solid angle.

As for the P-1 model, the non-gray radiation can be performed using the DO model, with a gray-band model, which divides the radiation spectrum into N wavelength bands.

In the DO model, the RTE is integrated over the control volume (existing mesh) using a finite volume method 80, 84. For the case of anisotropic scattering at complex surfaces, the DO model does not conserve radiant energy. Some CFD codes implemented a conservative variant of the DO to tackle this issue 91.

Through the years, the DOM was used in the simulation of several types of photochemical or photocatalytic (immobilized or slurry) reactors due to its accuracy. Romero et al. proposed the DOM to solve the RTE in a heterogeneous reaction medium in a photocatalytic system with an annular geometry 92. Subsequently, many researchers studied the radiation field using the DOM in annular photoreactors 11, 78, 90, 93. The radiation field in a flat-plate reactor using DOM was investigated by Brandi et al. 94.

Sgalari et al. computed the radiative transfer with DOM within an annular photoreactor for typical situations of photocatalytic processes, investigating the effects of the parameters on the local rate of radiant energy absorption and the angular distribution of the radiation intensity 93. The radiation transport equation was solved using a finite-volume-based DO method for an annular bubble-column photocatalytic reactor with a three-phase flow for photodegradation of Bayer liquor 11. Pareek et al. applied the MC approach to estimate light intensity distribution (LVREA) in an annular photocatalytic reactor and the DO model to assess the effect of wall reflectivity, catalyst loading, and phase function parameter on the light intensity distribution 78.

Bagheri and Mohseni developed a CFD model for simulating annular VUV/UV photoreactors considering reflection, absorption, and refraction of photons by the wall and slurry media in radiation modeling using the DO method 90. Li et al. used the DOM to study the wall reflection on an annular single-lamp UV reactor, which directly affects the radiation distribution 95. Asadollahfardi et al. presented a comparison of the reliability of the DOM with MC predictions for solving RTE 76. The DOM is widely applied to model steady-state radiative transfer in media 96.

2.1.3 Monte Carlo Model

The Monte Carlo (MC) radiation model generates photons randomly in a stochastic method and will, therefore, produce speckled results if the target number of histories is relatively small. Increasing the target number of histories produces a smoother and more accurate solution, but at the expense of higher computation effort 79. The MC model considers that the intensity is proportional to the differential angular flux of the photons. Then, the mean radiation intensity is obtained by computing the distance travelled for a typical selection of photons, in each volume cell 80.

An MC approach is used to solve the radiant energy balance equation and determine scattering phenomena in photosensitized reactions for continuous processes by Spadoni et al. 97. The radiation field inside an annular photocatalytic reactor was performed using an MC model in a specific case of radiative transfer in absorbing-scattering media 98. Imoberdorf et al. presented the MC approach to simulate the radiation field in single and multi-lamp homogeneous photoreactors with an annular geometry, showing the importance of the reflection, refraction, and absorption of photons by the lamp and the wall 99. The MC model was employed to model and optimize the radiation field in a multiplate photocatalytic reactor (MPPR – parallel photocatalytic plates irradiated by cylindrical UV lamps orthogonal to the plates) for air or water purification 100.

3 Case Study

The models for simulation of radiation in CFD are assessed using a case study with a tutorial approach to the models' implementation. In this tutorial, the UV-intensity fields were simulated. In the base case, a 3D annular photoreactor and a 2D rectangular enclosure with axisymmetry (axial cut the 3D annular geometry) with black walls were considered as showcases.

3.1 Geometry Model and Computational Grid

The case study reactor has an annular geometry with 645 mm of length, 15 mm of external radius, and 2.25 mm of internal radius. In this configuration of the photoreactor, a UV lamp was placed in the middle of the cylindrical vessel. In the laboratory case, the lamp is enclosed in a quartz sleeve to isolate it from the reacting medium, but in the simulated system the quartz medium was not considered. This reactor has been used in several experimental and numerical works 77, 85, 87. The photoreactor shown in Fig. 4a was simulated in 2D and 3D. The inlet and outlet correspond to the circular crowns at the ends of the cylindrical reactor. The geometry model was generated using ANSYS DesignModeler®.

Details are in the caption following the image
(a) Single-lamp axial annular geometry of the photoreactor, (b) computational grid of mesh 8 of the 3D model (isometric view and front view), (c) computational grid of mesh 5 of the 2D model.

After the generation of the geometry, the computational grid was generated using ANSYS Meshing®. The geometric model was discretized, subdividing it into small finite volumes that define the computational grid and where the equations are solved. The generation of the grid is one of the most critical steps of the CFD analysis because the size of the elements influences the accuracy of the results due to numerical approximations. The mesh structure is quite relevant for the simulation of radiation. Thus, there is a compromise between the accuracy of the results and the computational effort required.

Figs. 4b and 4c represent the computational grid of the 3D model and 2D model, respectively. The 2D meshes are made of regular quadrilateral elements. Refinement in this mesh consists of the division of the quadrilaterals. The 3D mesh is made mainly of hexahedral elements, which start as quadrilaterals in the top face and are repeated in layers along the heigh. This repetition creates a regular mesh.

Tab. 3 summarizes the properties of the studied meshes. The 2D meshes were generated using several element sizes (meshes 1, 2, and 3). The lamp wall was identified as the most critical region of the mesh. Thus, meshes 4 and 5 were generated to refine the region near the lamp wall by adding several layers. The 2D domain was generated using an axisymmetric model due to the symmetric condition of the photoreactor. The 3D mesh 7 was refined in Ansys Fluent using different levels of refinement near the lamp wall.

Table 3. Data of the 2D and 3D meshes for the CFD simulations.

Mesh

Dimension

Element size [mm]

Layers refinement on lamp wall

Number of elements

1

2D

3.0

9.7 × 103

2

2D

1.0

9.0 × 104

3

2D

0.1

9.0 × 106

4

2D

3.0

20

1.4 × 104

5

2D

3.0

67

2.5 × 104

6

3D

3.0

9.7 × 105

7

3D Fluent Level 4

3.0

4

1.3 × 106

8

3D Meshing inflation

10.0

40

3.8 × 105

3.2 Selection of Radiation Model

The DO model using the finite volume method (FVM) of ANSYS Fluent R2020® was chosen to simulate the RTE. This is a promising method for modeling radiative transfer due to its extensive applicability and high accuracy.

The P-1 model was not employed because the chosen case had low optical thicknesses. The medium which defines the optical thickness is air and the maximum length in the geometry of the problem is approximately 0.15 m. The MC model was excluded due to its ergodic treatment of the problem. To obtain good approximations of the physical quantities, a high number of histories of the photons was necessary, which results in a high computational cost.

3.3 Lamp Characteristics

The presence of radiation is the distinguishing factor of the photoreactors, so it is necessary to consider the characteristics of the radiation source (lamp). The reactor simulated has a single lamp concentric to the body reactor.

Considering the real characteristics of a UV lamp, the rays pass through the lamp body and lamp sleeve until they reach a point in the medium. This is a complex phenomenon because of absorbance, reflection, and refraction of radiation from/through the lamp's sleeve and body 101. The presented model assumes that there is no sleeve, the UV source behaves as a diffuse radiant emitter, and refraction and reflection through and from the surface of UV lamp are neglected. The sufurce emission model was used to determine the boundary condition for the tubular lamps 102 and the average value of irradiance computed from Eq. 7 was 127.3 W m−2 considering a power output of the lamp Plamp = 6.58 W 85.
urn:x-wiley:09307516:media:ceat202200551-math-0025(7)

Where dlamp (m) is the lamp diameter and L (m) is the lamp length.

3.4 Boundary Conditions

In the CFD analysis, air was considered as the fluid in the annular space, and its properties were set using the standard models available in Fluent. For the external reactor wall and the wall of the lamp, the properties of fused quartz were considered. The properties of the materials are provided as Supporting Information.

The simulation of the radiation distribution implies the calculation of irradiation, which corresponds to the radiation emitted by the lamp to set as boundary condition, considering the lamp a semi-transparent wall. Then, the simulations were carried out simulating an infinite cylinder, defining as radiation boundary condition the intensity of the radiation emitted by the lamp.

For both 2D and 3D cases, the flow was set as stagnant. For 2D cases, air inlet and outlet were considered as interface boundaries linked by a periodic condition. Because the pressure gradient between the boundaries was set to ΔP/x = 0 Pa m−1, there is no flow field in this case. In 3D cases, air inlet and outlet were considered as walls, with the three velocity components set to zero. The boundary conditions used in the 2D and 3D models are summarized in Tabs. 4 and 5, respectively.

Table 4. Boundary conditions of the 2D Model.

Boundary

Boundary conditions

Name: Air inlet

Periodic BC – linked to outlet ΔP/x = 0

Type: Interface boundary

Name: Air outlet

Periodic BC – linked to inlet ΔP/x = 0

Type: Interface boundary

Name: Lamp wall

Hflux = 0 W m−2

Type: Wall

Ilamp = 127.3 W m−2

Semi-transparent wall, direct irradiation, ε = 1

Velocity non-slip condition

Name: Reactor wall

Hflux = 0 W m−2

Type: Wall

Ilamp = 0 W m−2

Semi-transparent wall, direct irradiation, ε = 1

Velocity non-slip condition

Table 5. Boundary conditions of the 3D model.

Boundary

Boundary conditions

Name: Air inlet

Velocity components set to 0

Type: Wall

Opaque wall, ε = 1

Name: Air outlet

Velocity components set to 0

Type: Wall

Opaque wall, ε = 1

Name: Lamp wall

Hflux = 0 W m−2

Type: Wall

Ilamp = 127.3 W m−2

Semi-transparent wall, direct irradiation, ε = 1

Velocity non-slip condition

Name: Reactor wall

Hflux = 0 W m−2

Type: Wall

Ilamp = 0 W m−2

Semi-transparent wall, direct irradiation, ε = 1

Velocity non-slip condition

To obtain the radiation field from the RTE without the effect of thermal radiation, the temperature of the domain was set to1 K (minimal temperature supported in ANSYS Fluent R2020®). The flow was stagnant, so although all sets of equations were defined, as well as the boundary conditions (BCs), the actual flow equations were not solved, and so the flow variables were all set to zero. This enables to focus solely on the issues pertaining to the simulation of radiation in CFD, particularly with ANSYS/Fluent.

3.5 Numerical Solution and Convergence Criteria

In the chosen case the flow is stagnant and the boundary conditions for the radiation and the energy are constant. So, the solvers were set to steady state and only the sets of equations for radiation and energy are solved. The discretization scheme is second-order upwind for the energy and second-order upwind for discrete ordinates. The convergence criterion for the numerical solution was residuals should be less than 10−20. The numerical mesh validity is checked in Sect. 4.1, for the several meshes described in Sect. 3.1.

4 Validation and Evaluation of Radiation Models

First, the mesh quality was evaluated to ensure the lowest numerical diffusion and the most reliable results for the 2D axisymmetric and 3D configurations. Then, angular discretization and absorption coefficient were investigated to determine their influence in the radiation field. Finally, a comparison between simulation results and previous works is made to assess the validity of the results obtained with 2D axisymmetric and 3D models.

4.1 Study of the Computational Grid

Assuming a case with a medium that does not absorb light, the mesh element size and the number of layers in the lamp wall were assessed. The 2D meshes were refined using ANSYS Meshing®, one of the 3D meshes was refined in Ansys Fluent using the refinement tool and another in ANSYS Meshing®. In 3D cases, the simulations were carried out using 20 × 20 directions and 10 × 10 pixilation of angular discretization Figs. 5 and 6 present the light distribution along the radius at a line in the mid-axial position, for 2D and 3D models, respectively.

Details are in the caption following the image
Influence of the element size in the grid of the 2D axisymmetric model.
Details are in the caption following the image
Influence of the element size in the grid of the 3D model.

It is observed that the refinement of the grid in the lamp wall influences the result of the radiation distribution. Only the more refined meshes around the lamp sleeve can describe accurately the radiation intensity. Away from the lamp, the local values in the neighbouring of the sleeve do not influence the overall radiation profile. For the simulation of radiative transfer, it is used a mesh able to accurately describe the full radiation profile. The selected mesh has elements with a size of 3.0 mm where refinement of the 67-layers in the lamp wall was considered for the 2D axisymmetric model. In the 3D model, a grid with an element size of 10 mm and refinement of the 40-layers shows the best results.

These findings indicate that the 2D model describes the same radiation profile behavior as the 3D model. This accordance between geometric models was expected because the 3D case is axisymmetric, with complete homogeneity through the angular direction.

4.2 Study of the Angular Discretization

Angular discretization and pixelation play a major role to obtain a reliable solution for RTE. At any spatial location, each octant of the angular space 4π is divided into solid angles (Nθ × Nϕ), in which θ and ϕ represent polar and azimuthal angles. In 2D calculations, there are only 4Nθ × Nϕ directions since only four octants are solved due to symmetry. In 3D cases, 8Nθ × Nϕ directions are solved. For Cartesian meshes, it is possible to align the global angular discretization with the control volume face. However, when generalized unstructured meshes are used, control volume faces do not align with the angular discretization, leading to control angle overhang. Control angle overhang can be corrected using pixelation. The overhanging control angle is discretized into Nθp × Nϕp 80.

The RTE is simulated for two angular discretizations: (i) 5 × 5 directions (solid angles) and pixilation of 3 × 3 and (ii) 20 × 20 directions and pixilation of 10 × 10 were performed considering the non-absorption case (α = 0 m−1) for 2D and 3D models. Figs. 7 and 8 represent the radiation profile and radiation intensity results for each case of angular discretization for 2D and 3D models, respectively.

Details are in the caption following the image
(a) Radiation intensity results and (b) radiation profiles of the non-absorption case for different angular discretization for the 2D axisymmetric model of mesh 5 at x/L = 0.5.
Details are in the caption following the image
(a) Radiation intensity results and (b) radiation profiles of the non-absorption case for different angular discretization for the 3D model of mesh 6 at x/L = 0.5.

The results of angular discretization indicate that for the 2D case the angular discretization does not have a role in the distribution of radiation results, because radial homogeneity is already implicit when simulating only a slice of the reactor. For the 3D case, an increase in angular discretization enables more uniform distribution of light, namely in the lamp wall.

Fig. 8 displays the radiation intensity map for two angular discretization values. The visual effect of the discretization is striking even at the lamp surface with the occurrence of stripes of larger intensity. This heterogeneity is propagated into the medium, as seen in the axial cut of the reactor. The effect of angular discretization is quantified in Fig. 8, where the angular distribution of the radiation intensity is shown at five radial locations. For the less dense angular discretization, the radiation has a wavy pattern originating at the source boundary. Thus, the simulations for 3D cases were performed using an angular discretization of 20 × 20 directions and 10 × 10 pixilation.

4.3 Effect of Absorption Coefficients in Radiation Profiles

For the study of absorption coefficients, only 2D simulation was performed, since for the non-absorption case the 2D and 3D results were very similar. The RTE was solved by discretizing each control volume into 5 × 5 directions (solid angles) and pixelation of 3 × 3 for the 2D model. After the numerical validation of the simulation conditions, the models were used for absorption coefficients in the range of α = 0 to 357.6 m−1. The 2D light distribution profiles for the several absorption coefficients are depicted in Fig. 9.

Details are in the caption following the image
(a) Radiation distribution and (b) radiation profiles for the 2D axisymmetric model (mesh 5).

The incident radiation map inside the annular reactor shows the overall profile from the lamp towards the outer wall. The distribution presented in Fig. 9 can be expected for the annular configuration of the photoreactor due to the radial increase of the section for radiation associated with the medium absorption. The radiation profile is flat throughout the reactor length due to the periodic BCs, so a representative profile can be obtained along any axial position. The dimensionless light distribution profiles along the radius are depicted in Fig. 9, which conveys a more detailed picture of the effect of the absorption coefficient.

The profiles presented in Fig. 9 show that the light intensity decreases rather sharply with the increase in the absorption coefficient. For the case with zero absorption coefficient, the decrease of incident radiation is due to the increment of the photonic flow area. When the absorption coefficient is equal to 357.6 m−1, 90 % of the incident light is absorbed in the initial ≈ 1.5 mm away from the lamp. This indicates that the exposure of the catalyst to radiation, when there are heterogeneities of absorption in the medium, will depend on the flow patterns and degree of mixing within the reactor in the photocatalytic systems. If the flow is very segregated promoting large gradients in the light absorption throughout the reactor, the illumination of the catalyst in the outer wall will be very heterogeneous.

4.4 Comparison with Reported Data

The presented models are compared with experimental data of Quan et al. (2004) 85 and simulation data from Yu et al. 87 and Huang et al. (2011) 77 whose works used the same reactor presented in this work. Quan et al. (2004) 85 made experiments in a light-attenuating medium (ozone+air) using potassium ferrioxalate actinometry to observe the absorption effect on the light intensity profile. Simulation data from Yu et al. (2008) 87 using the P-1 model to assess the effect of absorption coefficient, scattering coefficient, wall reflectivity, and phase function parameter in an annular photoreactor and data from Huang et al. 77 using the FVM to perform the radiative transfer in absorption and scattering media for a wide range of optical thickness were considered in this work. Also, the results were compared with the profile obtained from the Lambert-Beer equation for annular geometries 103,
urn:x-wiley:09307516:media:ceat202200551-math-0026(8)

where I is the radiation intensity (W m−2), which depends on initial radiation intensity (W m−2), I0, the reactor radius (m), r0, the local radius (m), r, and absorption coefficient (m−1), α. The results are shown in Fig. 10.

Details are in the caption following the image
Comparison of models of the relative incident radiation for several absorption coefficients.

From Fig. 10 it was concluded that the models to simulate radiation distribution inside an annular reactor described the same behavior as reported in the literature. Also, the proposed method to solve the RTE by the Lambert-Beer law proposed by Abu-Ghararah 103 displays the same curve shape for all absorption coefficients. Thus, this review presents a reliable CFD method to simulate the radiation distribution inside an annular reactor.

5 Conclusions

A review of radiation models is presented. The discrete ordinate model was the most reliable model to predict the radiation distribution inside a reactor. Using this model, a base case analysis was carried out and sequential steps of simulation radiation inside an annular reactor were described. Several critical parameters to obtain reliable results were investigated such as mesh refinement and angular discretization.

The model results were compared with the ones reported in the literature and with the Lambert-Beer law. The radiation distribution of 2D and 3D models proposed describe the same behavior of radiation distribution as in the literature, namely, Quan et al. (2004) 85, Yu et al. 87, and Huang et al. 77. Therefore, this review represents a tutorial for radiation simulation inside an annular reactor.

Supporting Information

Supporting Information for this article can be found under DOI: https://doi.org/10.1002/ceat.202200551.

Acknowledgements

This work was financially supported by LA/P/0045/2020 (ALiCE), UIDB/50020/2020, and UIDP/50020/2020 (LSRE-LCM), and by the project SuN2Fuel (2022.04682.PTDC), funded by national funds through FCT/MCTES (PIDDAC). I. S. O. Barbosa acknowledges her FCT grant UI/BD/151092/2021.

The authors have declared no conflict of interest.

    Symbols used

  1. a [m2s−1]
  2. thermal diffusivity

  3. C [–]
  4. linear-anisotropic phase function

  5. CP [J kg−1K−1]
  6. heat capacity

  7. dlamp [m]
  8. lamp diameter

  9. G [W m−2]
  10. incident radiation

  11. Hflux [W m−2]
  12. heat flux

  13. I [W m−2sr−1]
  14. radiation intensity

  15. Ilamp [W m−2]
  16. lamp irradiance

  17. I0 [W m−2]
  18. initial radiation intensity

  19. k [W m−1K−1]
  20. thermal conductivity

  21. n [–]
  22. refractive index

  23. N [–]
  24. number

  25. Plamp [W]
  26. power output of the lamp

  27. qr [W m−2]
  28. radiation flux

  29. r [m]
  30. local radius

  31. r0 [m]
  32. reactor radius

  33. urn:x-wiley:09307516:media:ceat202200551-math-0027 [–]
  34. unit position vector

  35. s [m]
  36. path length

  37. urn:x-wiley:09307516:media:ceat202200551-math-0028 [–]
  38. unit direction vector

  39. urn:x-wiley:09307516:media:ceat202200551-math-0029 [–]
  40. unit scattering direction vector

  41. SG [W m−3]
  42. user-defined radiation source

  43. T [K]
  44. local temperature

  45. Greek letters

  46. α [m−1]
  47. absorption coefficient

  48. Γ [m]
  49. diffusivity of the incident radiation

  50. ε [–]
  51. emissivity

  52. θ [sr]
  53. polar angle

  54. μ [Pa s]
  55. viscosity of the fluid

  56. ρ [kg m−3]
  57. density of the fluid

  58. σ [W m−2K−4]
  59. Stefan-Boltzmann constant

  60. σs [m−1]
  61. scattering coefficient

  62. φ [–]
  63. phase function

  64. ϕ [sr]
  65. azimuthal angle

  66. urn:x-wiley:09307516:media:ceat202200551-math-0030 [sr]
  67. solid angle

  68. Sub- and superscripts

  69. Lamp
  70. Lamp

  71. 0
  72. Initial

  73. Flux
  74. Flux

  75. Abbreviations

  76. 2D
  77. two-dimensional

  78. 3D
  79. three-dimensional

  80. AKN
  81. Abe-Nagano-Kondoh

  82. CFD
  83. computational fluid dynamics

  84. CPC
  85. compound parabolic collectors

  86. CPC-PR
  87. compound parabolic collectors photocatalytic reactor

  88. DO
  89. discrete ordinates

  90. DOM
  91. discrete ordinates model

  92. DT
  93. discrete transfer

  94. ESDE
  95. extensive source superficial diffusive emission

  96. ESVE
  97. extensive source volumetric emission

  98. ESVEA
  99. modified ESVE with photon absorption

  100. ESVERA
  101. modified ESVEA with reflection, refraction, and absorption

  102. FVM
  103. finite volume method

  104. LED
  105. light-emitting diode

  106. LSDE
  107. line source diffuse emission

  108. LSSE
  109. line source spherical emission

  110. LVREA
  111. local volumetric rate energy absorption

  112. MC
  113. Monte Carlo

  114. MO
  115. methyl orange

  116. MPPR
  117. multiplate photocatalytic reactor

  118. PCO
  119. photocatalytic oxidation

  120. R
  121. realizable

  122. RNG
  123. renormalization group

  124. RSM
  125. Reynolds stress model

  126. RTE
  127. radiation transfer equation

  128. S
  129. standard

  130. SA
  131. salicylic acid

  132. SST
  133. shear stress transport

  134. TCE
  135. trichloroethylene

  136. UV
  137. ultraviolet

  138. UV-A
  139. ultraviolet A

  140. UV-Vis
  141. ultraviolet visible

  142. VC
  143. vinyl chloride

  144. VOC
  145. volatile organic compound

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