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versão impressa ISSN 1678-5878
J. Braz. Soc. Mech. Sci. & Eng. vol.32 no.4 Rio de Janeiro out./dez. 2010
CFD analysis of the pulverized coal combustion processes in a 160 MWe tangentially-fired-boiler of a thermal power plant
Cristiano V. da SilvaI; Maria Luiza S. IndrusiakII; Arthur B. BeskowIII
IUniversidade Regional Integrada do Alto Uruguai e das Missões - URI Campus de Erechim, Department of Eng. and Computational Science, GEAPI - Group of Applied Engineering to Industrial Processes, LABSIM - Numerical Simulation Laboratory, 99700-000 Erechim, RS, Brazil. email@example.com
IIUNISINOS - Universidade do Vale do Rio dos Sinos, Graduate Program in Mechanical Engineering, 93022-000 São Leopoldo, RS, Brazil. firstname.lastname@example.org
IIIUniversidade Regional Integrada do Alto Uruguai e das Missões - URI Campus de Erechim, Department of Eng. and Computational Science, GEAPI - Group of Applied Engineering to Industrial Processes, LABSIM - Numerical Simulation Laboratory 99700-000 Erechim, RS, Brazil. Arthur@uricer.edu.br
The strategic role of energy and the current concern with greenhouse effects, energetic and exergetic efficiency of fossil fuel combustion greatly enhance the importance of the studies of complex physical and chemical processes occurring inside boilers of thermalpower plants. The state of the art in computational fluid dynamics and the availability of commercial codes encourage numeric studies of the combustion processes. In the presentwork the commercial software CFX © Ansys Europe Ltd. was used to study the combustionof coal in a 160 MWe commercial thermal power plant with the objective of simulating the operational conditions and identifying factors of inefficiency. The behavior of the flow of air and pulverized coal through the burners was analyzed, and the three-dimensional fluegas flow through the combustion chamber and heat exchangers was reproduced in the numeric simulation.
Keywords: coal combustion, computational fluid dynamics, thermal power plant
In many parts of the world, coal is an important energy resource to meet the future demand for electricity, as coal reserves are much greater than for other fossil fuels. However, the efficient and clean utilization of this fuel is a major problem in combustion processes. In recent years, the interest on performance optimization of large utility boilers has become very relevant, aiming at extending their lifetime, increasing the thermal efficiency and reducing the pollutant emissions, particularly the NOx emissions.
Coal reserves in Brazil, which are used mainly for electricity production in large utility boilers, are enough to meet the next 1,109 years demand, considering the consumption levels of 2006 (EIA/U.S. Department of Energy, 2009). Nonetheless, in order to face the competition from renewable, natural gas and nuclear energy sources, some main problems must be solved, as to reduce CO2 emissions through increasing efficiency (Williams et al., 2000). Also NOx and SOx emissions should be reduced to environmentally acceptable levels. An efficient operation of combustion chambers of these boilers depends on the proper knowledge of the oxidation reactions and heat transfer between the combustion products and the chamber walls and heat exchangers, which requires a detailed analysis of the governing mechanisms. Many combustion modeling methodologies are now available, but only a few are able to deal with the process in its entirety. Eaton et al. (1999) present a revision of combustion models. The models are generally based on the fundamental conservation equations of mass, energy, chemical species and momentum, while the closure problem is solved by turbulence models such as the k - ε (Launder and Sharma, 1974), combustion models like Arrhenius (Kuo, 1996; Turns, 2000), Magnussen - EBU - "Eddy Breakup" (Magnussen and Hjertager, 1976); radiative transfer models based on the Radiative Transfer Equation - RTE (Carvalho et al., 1991) and models to devolatilization and combustion of solid and liquid fuels.
Abbas et al. (1993) describe an experimental and predicted assessment of the influence of coal particle size on the formation of NOx of a swirl-stabilized burner in a large-scale laboratory furnace. Three particle size distributions, 25, 46, and 121 µm average size, of high volatile coal were fired under similar operation conditions. The data presented combine detailed in-flame measurements of gas temperature, gas species concentrations of CO, CH4, O2, NOx, HCL, NH3, particle burnout, and "on-line" N2O, with the complementary predicted studies. The predicted results are in good agreement with experimental data. Although the NOx emission trends with particle size are similar, predicted values for each fraction are higher, suggesting a limitation in the NOx reducing mechanisms used in the model. Three mechanisms - thermal, fuel and prompt - were used to calculate the NOx formation.
Xu et al. (2000) employed the CFD code to analyze a coal combustion process in a front wall pulverized coal fired utility boiler of 350 MW with 24 swirl burners installed at the furnace front wall. Five different cases with 100, 95, 85, 70 and 50% boiler full load were simulated. Comparisons were addressed, with good agreement between predicted and measured results in the boiler for all but one case thus validating the models and the algorithm employed in the computation.
Li et al. (2003) numerically investigated the combustion process using only a two-fluid model (instead of the Eulerian gas - Lagrangian particle models) for simulating tree-dimensional turbulent reactive flows and coal combustion. To improve the simulation of the flow field and NOx formation, a modified k - ε - kp two-phase turbulence model and a second-order-moment (SOM) reactive rate model were proposed. The proposed models were used to simulate NOx formation of methane-air combustion, and the prediction results were compared with those using only the presumed-PDF (Probability Density Function)-finite-reaction-rate model and experimental data. The proposed models were also used to predict the coal combustion and NOx formation at the exit of a double air register swirl pulverized-coal burner. The results indicate that a pulverized coal concentrator installed in the primary air tube of the burner has a strong effect on the coal combustion and NOx formation.
In a numerical investigation, Kurose et al. (2004) employed a tree-dimensional simulation to the pulverized coal combustion field in a furnace equipped with a low-NOx burner, called CI-α, to investigate in details the combustion processes. The validities of available NOx formation and reduction models were investigated too. The results show that a recirculation flow is formed in high-gastemperature region near the CI-α burner outlet, and this lengthens the residence time of coal particles in this high-gas-temperature region, promotes the evolution of volatile matter and the process of char reaction, and produces an extremely low-O2 region for effective NO reduction.
Zhang et al. (2005) presented a numerical investigation on the coal combustion process using an algebraic unified second-order moment (AUSM) turbulence-chemistry model to calculate the effect of particle temperature fluctuation on char combustion. The AUSM model was used to simulate gas-particles flows in coal combustion including sub-models as the k - ε - kp two-phase turbulence model, the EBU-Arrhenius volatile and CO combustion model, and the six-flux radiation model. The simulation results indicate that the AUSM char combustion model presented good result, since the latter totally eliminates the influence of particle temperature fluctuation on char combustion rate.
Bosoaga et al. (2006) presented a study developing a CFD model for the combustion of low-grade lignite and to characterize the combustion process in the test furnace, including the influence of the geometry of burner and furnace. A number of computations were made in order to predict the effect of coal particle size, the moisture content of lignite, and the influence of combustion temperature and operation of the support methane flame on the furnace performance and emissions. The influence of lignite predrying was also modeled to investigate the effects of reduced fuel consumption and CO2 emissions. It was found that the increase of moisture tends to reduce NOx, and the methane support flame greatly increases NOx.
In another work, Backreedy et al. (2006) presented a numerical and experimental investigation of the coal combustion process to predict the combustion process of pulverized coal in a 1 MW test furnace. The furnace contains a triple-staged low-NOx swirl burner. A number of simulations were made using several coal types in order to calculate NOx and the unburned carbon-in-ash, the latter being a sensitive test for the accuracy of the char combustion model. The NOx modeling incorporates fuel-NO, thermal, and prompt mechanisms to predict the NO formation on the combustion processes.
Kumar and Sahur (2007) studied the effect of the tilt angle of the burners in a tangentially fired 210 MWe boiler, using commercial code FLUENT. They showed the influence of the tilt angle in the residence time of the coal particles and consequently in the temperature profiles along the boiler.
Asotani et al. (2008), also using the code FLUENT, studied the ignition behavior of pulverized coal clouds in a 40 MW commercial tangentially fired boiler. The results for unburned carbon in ash and for outlet temperature were validated respectively by the operating data and by the design parameter. A qualitative comparison between the results for temperature and ignition behavior in the vicinity of the burners was made, using the images of a high temperature resistant video camera system. At the same line Choi and Kim (2009), also using the code FLUENT, investigated numerically the characteristics of flow, combustion and NOx emissions in a 500 MWe tangentially fired pulverized-coal boiler. They showed that the relation among temperature, O2 mass fraction and CO2 mass fraction has been clearly demonstrated based on the calculated distributions, and the predicted results have shown that the NOx formation in the boiler highly depend on the combustion process as well as the temperature and species concentration.
The strategic role of energy and the current concern with greenhouse effects enhance the importance of the studies of complex physical and chemical processes occurring inside boilers of thermal power plants. Combustion comprises phenomena such as turbulence, radiative and convective heat transfer, particle transport and chemical reactions. The study of these coupled phenomena is a challenging issue. The state of the art in computational fluid dynamics and the availability of commercial codes encourage numeric studies of the combustion processes. In the present work, a commercial CFD code, CFX © Ansys Europe Ltd., was used to study the pulverized-coal combustion process in a 160 MWe thermal power plant erected in the core of the Brazilian coal reserves region, with the objective of simulating the operation conditions and identifying inefficiency factors.
|NOx||=||Oxides of nitrogen|
|k||=||Constant of chemical reaction rate; or turbulent kinetic energy, m2/s2|
|x||=||Spatial coordinate, m|
|r||=||Vector position, m|
|s||=||Vector direction, m|
|S"||=||Radiation source term, W/m|
|Kα||=||Absorption coefficient, m-1|
|=||Average velocity, m/s|
|Cµ||=||Empirical turbulence model constant|
|Co||=||Mass fraction of raw coal, kg/kg|
|Cch||=||Mass fraction of char, kg/kg|
|p*||=||Modified pressure, Pa|
|pA||=||Atmospheric pressure, Pa|
|=||Average pressure, Pa|
|D||=||Dynamic mass diffusivity, m2/s|
|=||Average mass fraction kg/kg|
|I||=||Total radiation intensity, W/m2|
|=||Chemical reaction rate, kg/(s.m3) or rate of formation/destruction of chemical species, W/m3.kg|
|=||Universal ideal gas constant 8314.5 kJ/(kmol K)|
|E||=||Activation energy, J/kmol|
|A||=||Empirical coefficient, (m3/s)/kmol|
|=||Average molar concentration, kmol/m3|
|=||Molecular mass, kg /kmol|
|=||Average enthalpy of mixture, kJ/kg|
|=||Enthalpy of formation, kJ/kg|
|cp||=||Specific heat, kJ/(kg.K)|
|S||=||Path length, m; or source term, W/m3|
|τw||=||Shear stress in the wall, Pa|
|µ||=||Dynamic viscosity, (N.s)/m2|
|ε||=||Dissipation of turbulent kinetic energy, m2/s3|
|β||=||Temperature exponent or empirical constant|
|α||=||Empirical constant or α-th chemical species|
|η||=||Stoichiometric coefficient, kmol|
|κ||=||Thermal conductivity, W/(m.K)|
|σ||=||Stefan-Boltzmann constant, 5.678x10-8 W/(m2.K4)|
|δ||=||Krönecker delta function|
|i||Index or Chemical species|
|k||Chemical reaction or index|
|p||Products or particles|
|*||Represents the α -reacting component that leads to the smallest value for|
|p||Represents the combustion gas products|
A steady-state combustion of raw coal in air for a boiler combustion chamber is considered in order to determine the temperature, chemical species concentrations and the velocity fields for multi-component-flow (gas mixture and raw coal particles), as well as to study the influence of the operational parameters, such as heterogeneous condition for fuel and air flow in the chamber, on the combustion process and NOx formation.
The complete chemical reaction of the raw coal used at this work, including two devolatilization processes, is modeled according to the basic scheme showed in Fig. 1.
As basic assumptions, it is considered that the mass fractions of volatiles are 0.3636 of methane and 0.6364 of carbon monoxide, and that the combustion processes of these volatiles occur at finite rates. The methane oxidation is modeled by two global steps, given by:
Equation 2 also models the combustion of carbon monoxide resulting from the devolatilisation processes. The formation of NOx is modeled using two different paths, the thermal-NO (Zeldovich mechanism) and the prompt-NO (Fennimore mechanism), where the first, predominant at temperatures above 1800 K, is given by treestep chemical reaction mechanisms (CFX Inc., 2004):
In sub or near stoichiometric conditions, a third reaction is also used:
where the chemical reaction rates are predicted by Arrhenius equation.
For the prompt-NO, formed at temperatures lower than 1800 K, radicals can react with molecular nitrogen to form HCN, which may be oxidized to NO under flame conditions. The complete mechanism is not straightforward. However, De Soete proposed a single reaction rate to describe the NO source by Fennimore mechanism, which is used at this work. Arrhenius equations are used for predicting this chemical reaction rate (CFX Inc., 2004).
For multi-component-fluid, scalar transport equations are solved for velocity, pressure, temperature and chemical species. Additional equations are solved to determine how the components of the fluid are transported within the fluid. The bulk motion of the fluid is modeled using single velocity, pressure, temperature, chemical species and turbulence intensity fields.
Mass and Species Conservation
Each component has its own Reynolds-Averaged equation for mass conservation which, considering incompressible and stationary flow can be written in tensor notation as:
where and are the mass-average density of fluid component i in the mixture and average density, respectively, x is the spatial coordinate, is the vector of velocity and ij is the mass-averaged velocity of fluid component i . The term represents the relative mass flow, and Si is the source term for component i which includes the effects of chemical reactions. Note that if all the equations represented by Eq. (6) are added over all components, and the source term is set to zero, the result is the standard continuity equation.
The relative mass flow term accounts for differential motion of the individual components. At this work, this term is modeled for the relative motion of the mixture components and the primary effect is that of concentration gradient. Therefore,
where Di is the kinetic diffusivity. The mass fraction of component i is defined as . Substituting this expression into Eq. (7) and modeling the turbulent scalar flows using the eddy dissipation assumption, it follows that
where µt is the turbulent viscosity and Sct is the turbulent Schmidt number. Note that the sum of component mass fractions over all components is equal to one.
For the fluid flow the momentum conservation equations are given by:
where µeff =µ+µt and µ is the mixture dynamic viscosity and µt is the turbulent viscosity, defined as µt = Cµρ k2 / ε. The term p* = - ( 2 / 3)k is the modified pressure, Cµ is an empirical constant of the turbulence model and equal to 0.09, is the time-averaged pressure of the gaseous mixture, and δ is the Krönecker delta function. is the source term, introduced to model the buoyancy and drag force due to the transportation particles, and other mathematical terms due to turbulence models. The Boussinesq model is used to represent the buoyancy force due to density variations.
The k - Turbulence Model
The equations for turbulent kinetic energy, k, and its turbulent frequency, , are (Menter, 1994):
where β' , β and α are empirical constants of the turbulence model, σk and are the Prandtl numbers of the kinetic energy and frequency, respectively, and Pk is the term which accounts for the production or destruction of the turbulent kinetic energy.
Considering the transport of energy due to the diffusion of each chemical species, the energy equation can be written as
where and cp are the average enthalpy and specific heat of the mixture. The latter is given by
where c p,α and are the specific heat and the average mass fraction of the α -th chemical species, κ is the thermal conductivity of the mixture, Prt is the turbulent Prandtl number, and and represent the sources of thermal energy due to the radiative transfer and to the chemical reactions. The term can be written as:
where is the average temperature of the mixture, and ref ,α are the formation enthalpy and the reference temperature of the α -th chemical species. To complete the model, the density of mixture can be obtained from the ideal gas state equation (Kuo, 1996; Spalding, 1979; Turns, 2000), , where p is the combustion chamber operational pressure, which is here set equal to 1 atm (Spalding, 1979), and is the mixture molecular mass. The aforementioned equations are valid only in the turbulent core, where µt >> µ. Close to the wall, the logarithmic law of the wall is used.
To consider thermal radiation exchanges inside the combustion chamber, the Discrete Transfer Radiation Model - DTRM is employed (Carvalho et al., 1991), considering that the scattering is isotropic. The effect of the wavelength dependence is not considered, and the gas absorption coefficient is considered uniform inside the combustion chamber and its value is 0.5 m-1. Then, the Radiative Transfer Equation - RTE is integrated within its spectral band and a modified RTE can be written as
At the equation above, σ is the Stefan-Boltzmann constant (5.672 x 10-8 W/m2K4), r is the vector position, s is the vector direction, S is the path length, Ka is the absorption coefficient, I is the total radiation intensity which depends on position and direction, and S" is the radiation source term, where the radiative emission of the solid particles can be computed. The radiative properties required for an entrained particle phase are the absorption coefficients and scattering phase function, which depend on the particle concentration, size distribution, and effective complex refractive indices. However, optical properties of coal are not well characterized (Eaton et al., 1999). Generally, as a starting point to arrive at a tractable method for calculating radiative properties, the particles are assumed to be spherical and homogeneous. At this work, the heat transfer from gas mixture to particle considers that the particles are opaque bodies with emissivity equal to one, and the Hanz-Marshall correlation is used to model the heat transfer coupling between the gas mixture flow and the particles (CFX Inc., 2004).
The E-A (Eddy Breakup - Arrhenius) Chemical Reactions Model
The reduced chemical reactions model employed in this work assumes finite rate reactions and a steady state turbulent process to volatiles combustion. In addition, it is considered that the combined pre-mixed and non-premixed oxidation occurs in two global chemical reaction steps, and involving only six species: oxygen, methane, nitrogen, water vapor, carbon dioxide and carbon monoxide. A conservation equation is required for each species but nitrogen. Thus, one has the conservation equation for the α -th chemical species, given by Eq. (8), where the source term, Si , considers the average volumetric rate of formation or destruction of the α -th chemical species at all chemical reactions. This term is computed from the summation of the volumetric rates of formation or destruction in all the k -th equations where the α -th species are present, . Thus, .
The rate of formation or destruction, , can be obtained from an Arrhenius kinetic rate relation, which takes into account the turbulence effect, such as Magnussen equations (Eddy Breakup) (Magnussen and Hjertager, 1976), or a combination of the two formulations, the so called Arrhenius-Magnussen model (Eaton et al., 1999; CFX Inc., 2004). Such relations are appropriate for a wide range of applications, for instance, laminar or turbulent chemical reactions with or without pre-mixing. The Arrhenius equation can be written as follows:
where βk is the temperature exponent in each chemical reaction k , which is obtained empirically together with the energy activation Ek and the coefficient Ak. Πα is the product symbol, α is the molar concentration of the α -th chemical species, γα,k is the concentration exponent in each reaction k , is the gas constant, α and ηα ,k are the molecular mass and the stoichiometric coefficient of α in the k -th chemical reaction.
In the Eddy-Breakup or Magnussen model, the chemical reaction rates are based on the theories of vortex dissipation in the presence of turbulence. Thus, for diffusive flames:
where the index α* represents the reactant α that has the least value of .
In the presence of premixing, a third relation for the Eddy Breakup model is necessary, so that
where the index p represents the gaseous products of the combustion. A and B are empirical constants that are set as 4 and 0.5 (Magnussen and Hjertager, 1976). Magnussen model, Eqs. (18) and (19), can be applied to both diffusive and pre-mixed flames, or for the situation where both flames coexist, taking the smallest rate of chemical reaction.
Finally, for the Arrhenius-Magnussen model, given by Eqs. (17), (18) and (19), the rate of formation or destruction of the chemical species is taken as the lowest one between the values obtained from each model. It follows that Silva et al. (2007) used this formulation in this work to simulate the combustion process of methane and air in a cylindrical chamber obtaining good results. At this way:
The Coal Decomposition
Pulverized coal particles are treated at this work as noninteracting spheres with internal reactions and heat transfer and full coupling of mass, momentum and energy with the gaseous phase. The combustion of coal particles is a two-stage process: the devolatilization of raw coal particle followed by oxidation of residual char to leave incombustible ash. The devolatilization was modeled with two competing reactions (see Fig. 1) in order to deal with the strong dependence on temperature and heating rate of the bituminous coal. The two equations have different rate parameters and volatile yields. The yield fractions for the lower temperature equation were obtained from proximate analysis, and to the ones for the higher temperature equation it was given the values suggested by Li et al. (2003). The model adopted for the char burn out computes the rate of the reaction taking into account the rate of diffusion of oxygen within the pores of the char particle and its partial pressure at the particle surface (Kanury, 1975). Particle size plays an important role in the char combustion process and is usually modeled by a statistical distribution like the one developed by Rosin-Rammler (Brown, 1995), with the parameters adjusted from pulverized coal analysis.
The Coal Devolatilization Model
The devolatilization of the coal is modeled using the generic Arrhenius reactions capability in two steps (Ubhayakar et al., 1976) in which two reactions with different rate parameters and volatiles yields compete to pyrolyse the raw coal. The first reaction dominates at lower particle temperatures and has a yield Y1 lower than the yield Y2 of the second reaction which dominates at higher temperatures. As a result, the final yields of volatiles will depend on the temperature history of the particle, and will increase with temperature, lying somewhere between Y1 and Y2 . In this model, the mass fraction of the raw coal is specified as the mass fraction of volatiles (here methane and carbon monoxide, see Fig. 1) since all this material could be converted to volatiles.
At time t, it is assumed that a coal particle consists of mass of raw coal ( CO ), mass of residual char ( Cch ) after devolatilization has occurred, and mass of ash ( A ). The rate constants k1 and k2 of two reactions determine the rate of conversion of the raw coal:
the rate of volatiles production is given by
and so the rate of char formation is
The Field Char Oxidation Model
The oxygen diffusion rate is given by kd (pg - ps) , where pg is the partial pressure of oxygen in the furnace gases far from particle boundary layer and pS is the oxygen pressure at the particle surface. The value of kd is given by
where Rp is the particle radius, Tp is the particle temperature, g is the far-field gas temperature, PA is atmospheric pressure, Dref is the dynamic diffusivity, and α is the exponent with value 0.75. The char oxidation rate per unit area of particle surface is given by kc ps. The chemical rate coefficient is given by,
where the parameters Ac and Tc depend on the type of coal. The overall char reaction rate of a particle is given by
and is controlled by the smallest of the two rates, kd and kc.
The boiler under consideration is part of a pulverized coal (PC) power plant operating in a subcritical steam cycle. The tangential firing combustion chamber is rectangular in shape with four burners firing from each corner, thus creating a large vortex in the center of the chamber. The evaporation process occurs mainly in the steel tubes covering the boiler walls. In the upper middle of the boiler there are the reheater (LTR, HTR), super-heater (LTS, HTS) and economizer (ECO2) tube banks. The second stage of the boiler comprises a large rectangular curved duct, the first economizer (ECO1) tube bank and the regenerative air heater (Ljungström). From there the flue gases are directed through the electrostatic precipitator to the chimney. Figure 2(a) shows the general disposition of the boiler heat exchangers and burners.
Mesh Settings and Convergence Criteria
The domain under consideration comprises the first stage of the boiler: the combustion chamber with the burners at the corners and the heat exchangers until the top. The entrance to the second stage was considered the outlet of the domain. The discretization was done using tetrahedral volumes, and the grid details are depicted in Fig. 3. Other type of mesh volumes were not used due to software license limitations. As the boiler height corresponds to only six equivalent diameters of the boiler, the boundary layer is not developed at the whole domain. Nevertheless, prismatic volumes were used at the walls in order to capture the boundary layer behavior. Due to computational limitations, the mesh size used has approximately 1.5 × 106 elements, using mesh refinements in the combustion reactions zone. The convergence criterion adopted was the RMS - root mean square of the residual values, and the value adopted was 1 × 10-6 for all equations.
The boundary conditions were obtained from the design data set and also from the daily operation data sheets. The operating conditions considered were the rated ones, for 160 MW. The following parameters were considered:
Inlet: The inlet conditions are those for air and coal flows entering the domain from the burner nozzles. Total primary and secondary combustion air and pulverized coal mass flow rates were set as 79.5 kg/s, 100 kg/s and 50 kg/s respectively. Temperatures of primary air and coal, and secondary combustion air were set as 542 K and 600 K respectively. Pulverized coal size was modeled by a probabilistic distribution and limited between 50 µm and 200 µm.
Outlet: The outlet boundary is the flue gas passage at lateral wall near the top of the boiler, just above the ECO 2 heat exchanger, where the mean static pressure was. The outlet region was considered as black body to thermal radiation.
Boiler walls: The boiler walls are covered with slanting tubes from the bottom until the beginning of the heat exchangers region. From there to the top the tubes are vertically positioned. Wall roughness to steel was used, and the temperature was set as 673 K, the water saturation temperature at the working pressure of the boiler. The thermal radiation coefficient set for that two wall regions was 0.6.
The temperature field is shown at Fig. 4(b) for a vertical plane diagonally positioned. The large amount of heat released by the devolatilization and oxidation of the volatiles is pointed up by the near black regions at the edge of the flames originated at each burner. Devolatilization is the first reaction of the combustion process and takes place where the air and coal mixture injected by the burners achieve the adequate temperature. The central vortex created by the tangential layout of the burners is visible at the center of the combustion chamber.
As the flow moves to the outlet heat is exchanged with the walls and tube banks, creating the temperature gradient shown in the figure. The temperature and velocity fields are presented in a superimposed way at Figs. 4(h) to 4(l) for horizontal planes corresponding to the four burner levels and a level just upstream the burner region. The temperature color scale is the same for all the figures. At the lower burner levels the general temperature distribution shows lower values than at the higher levels. At Fig. 4(h) the temperature presents a trend to equalization, due to both the absence of new inflows and the strong turbulence and vorticity of the flow. The velocity fields, Figs. 4(m) to 4(q), represented by means of vectors, show that at the lower burner level the vortex region is narrow and increases in the upstream direction, due to the vorticity moment imparted by the burners jets at each level. Figure 4(m) shows the final aspect of the vortex which dominates the section, with a characteristic dimension of the same magnitude of the boiler wall horizontal length.
There is an intense formation of volatiles very near to the burner nozzles, denoting the action of the first reaction which is activated at relatively low temperatures. The oxidation of the resulting volatile yields is almost immediate, according to the set of equations which models the combustion process.
Figures 4(c) to 4(g) show the distribution of NOx mass concentration along the boiler. The NOx formation takes place mainly after the coal devolatilization and volatile oxidation, at the top edges of the air-fuel jets from each burner, where the higher temperatures were achieved. The major role of high temperature along with high oxygen concentration levels in NOx formation is also emphasized by the impressive enlargement of NOx production at the higher burner levels. An enhancement of the oxygen concentration is expected at these levels, where the inlet air jets are reinforced by the residual oxygen of the lower levels.
The results obtained were analyzed and compared with known data of the boiler operation. The main control parameters used to validate the results, shown at Table 1, were the heat transfer rate at the walls, outlet temperature and mass fractions of gases at the boiler outlet where there are regular measurements. The simulation results for heat rate, outlet temperature and %O2 match quite well with experimental data. The additional amount of %O2 and CO (ppm) in experimental results point out that the actual combustion process is less efficient than at the simulation, with more CO and O2 and less CO2 as products. Several simulations were done with more and less fuel and air and the results indicate that the model response is adequate to those variations. However, more experimental information is necessary in order to improve the agreement between actual data and simulation results. Indeed, there are strong uncertainties in the experimental data on account of the old and not properly calibrated field instruments used by the power plant staff for the measurements. The continuity of the research would provide adequate instruments in order to get better confidence in the analyses of the results.
Experimental and simulation results for NOx do not match at all. In the present work only prompt and thermal NO were simulated. The fuel NO, which accounts for 75-95% of the total NO in coal combustors (Kurose et al., 2004), was not simulated, being the next goal of the research.
The general description of the numeric model of a thermal power plant boiler using a commercial CFD code was presented in this article. The aim of the work is using of the results to better understand the complex processes occurring within the boiler. Some results were presented and discussed. The temperature and velocity fields are in agreement with the expected behavior of a tangentially fired coal combustion chamber.
The simulation of NOx production by means of only two mechanisms points up the role of high temperature and oxygen concentration on the process. Nevertheless, the total production of NOx must be analyzed, considering also the amount of N2 within the fuel.
The code shows good sensibility to variations in the inlet and boundary conditions and this was explored in order to study the performance of the boiler at out of design and part-load operation conditions and also to other conditions at the burners, like the vertical tilt.
Authors gratefully acknowledge the support by CNPq - Brazilian Scientific and Technological Council.
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Paper accepted February, 2010.
Technical Editor: Demétrio Bastos Neto.