In a preferred embodiment, this invention involves the use of turbulent eddies to manipulate the relative trajectories of very small pollutant particles and larger collector particles carried by a flowing fluid, which is typically an exhaust gas stream from an industrial process, to increase the probability of the particles colliding or interacting to agglomerate, or otherwise react with each other, to form more easily removable particles. A formation is designed to provide turbulence of the required size and scale to cause the different species of particles to have substantially differential slip velocities.
The turbulence should be such that the Stokes Number (St) of the small pollutant particles is much less than 1 (St<<1), while the Stokes Number (St) of the larger collector particles is much greater than 1 (St>>1).
The Stokes number (St) is a theoretical measure of the ability of a particle to follow a turbulence streamline. The Stokes number is defined as the ratio of the particle response time to a fluid flow time and is characterised by:
St=τ
p/τfρp U dp2/18 μL, (1)
where; τp is the particle response time, τf is the characteristic flow time, ρp is the particle density, U is the fluid velocity, dp is the particle diameter, μ is the fluid viscosity and L is the eddy dimension. Typically, for St<<1 a particle is able to respond fully to a turbulent eddy of scale L, and follows it closely. At the other extreme, where St>>1, a particle does not respond to turbulent motions of that scale at all and its trajectory is largely unaffected. In the intermediate range, for St≈1, particles respond partially to the fluid motions, but there is still a significant departure of the particle trajectory from the fluid motions.
When a Stokes analysis is performed for the common pollution species in the flue of, for example, an industrial coal fired boiler, it is found that for turbulence eddies at the scale of a typical duct (say 4 m2) and velocity of the gas (8-16 m/sec), all particles of all commonly found sizes will respond fully to the turbulence eddies, i.e. St<<1 for all particles. Even for turbulence of a scale corresponding to the dimensions of duct height/width mixers, turning vanes, stiffeners etc (say 400 mm), the majority of particles below 100 μm will respond fully to the turbulence eddies. It is not until the turbulence scales are reduced significantly below this size that the particles exhibit a range of responses from St<<1 to St>>1 for sizes ranging from 0.1 μm up to 100 μm. Under such conditions, the trajectories of the large and small particles diverge from those of the flow to different extents, causing increased probability of collisions.
From the foregoing, it is evident that, if turbulent eddies are sized correctly, it is possible to increase the number of collisions between different sized constituents within the same fluid flow on the basis of their differing interaction with, and hence path through, a turbulent eddy of fixed size. Further, it is possible to tailor the dominant size of a turbulent eddy to maximise the interaction between specific constituents on the basis of their relative inertia and hence responses to the turbulent eddy. A suitable formation can then be designed to provide the desired combination of eddy sizes.
Vortex generators can be used to create the eddies. Vortex generators are generally known in the art, and need not be described in detail in this application. A common vortex generator is a vane. A formation comprising a plurality of vanes can be used to generate a multitude of eddies in the fluid stream.
In one embodiment, illustrated in
The vanes 10 are arranged in an array comprising a plurality of parallel rows each extending in the direction of flow, each row containing a plurality of spaced vanes, orientated transversely to the fluid flow, as shown in the section view of
Turbulent eddies are formed in the wake of the folds and protrusions 12 of the vanes 10. The dominant sizes of eddies created by this design approximate the significant dimensions of the generator, and include the width of the vane Vw, the length of the vane Vl, the tooth depth Td and the tooth pitch Tp. The separation distance between successive vanes Vs is selected so that the eddies may form fully in the inter vane region.
The combination of dimensions determines the combination of eddy sizes that are formed. The optimal range of eddy sizes is selected, and the vane design is optimized to achieve this within other constraints, such as pressure drop.
Although teeth are used on the illustrated vane 10 and the vanes are angled to the direction of fluid flow, other variations are possible because eddies will form in the wake of any planar cylindrical or other shaped body placed in the path of the fluid flow and the eddies formed will be approximately the same size as the obstructing vane.
For example, as shown in
The multiple small scale vortices or eddies generated by the array of vanes extend across the entire duct as it is preferable for the turbulence field to encompass the entire flow path. However, although the vanes may be mounted in a duct in which the subject air stream flows, it is to be noted that the invention does not require that vanes to be mounted in a duct or other conduit.
Thus, in one embodiment, a formation for causing turbulent flow of the desired size and scale in a fluid flow can be designed and constructed as follows:
Namely, using the eddy size (L) as determined in step 3 (above), check St for the desired “collected particle” size (for low slip particles, St<<1). Using eddy size (L) as determined in step 3 (above) and St=1, check the intermediate particle response. Iterate these steps, adjusting the eddy size (L) to obtain the desired particle response.
There may be a range of sizes for each of the critical vane dimensions as dictated by the physical properties of the system, the dimensional requirements of manufacturing, and the engineering constraints of the apparatus. However, in general, the variables Vw, Vl, Vs, Tp and Td will determine the size, shape, intensity and frequency of the turbulence created, which in turn will control the degree to which individual particles will slip and collide in the turbulence behind the vanes. The important design criteria are the size and spacing of the vanes.
In addition, the objective is to cause the collision of suspended particles for a useful purpose e.g. agglomeration, sorption, catalisation, condensation etc. Hence, sufficient particle interactions should occur that substantially all particles experience at least one (and preferably multiple) collision event/s while traversing the device. In a practical sense, this requires a multiplicity of vanes in the direction of flow as well as across the flow. A multiplicity of vanes across the flow ensures that there is no flow path through the device that is free of appropriately sized eddies, while a multiplicity of vanes in the direction of flow ensures the flow remains in the device for a sufficient time for a useful number of particle collisions to occur.
In a preferred embodiment, the device is long enough in the direction of flow that the flowing fluid is treated by it for at least 0.1 second. For a typical industrial flow of (say) 10 m/sec, this would require a device at least 1 m deep in the direction of flow.
Separation between subsequent vanes in the direction of flow should be such that the eddies created by a vane are reinforced by the eddy creating action of the vane immediately downstream, as illustrated in
Alignment of the vanes is not critical and may be horizontal, vertical or at some angle between these two directions.
The present invention has the advantage that mixing devices can be designed to suit particular applications. More specifically, turbulence of a desired scale can be achieved, so that small pollutant particles are entrained into the turbulent eddies and vortices, whereas larger collector particles are entrained to a smaller or negligible degree). The resultant differential slip velocities and trajectories of the small pollutant particles and the larger removal particles result in more collisions between the two types of particles. Consequently, there is greater interaction between the particles (e.g impact adhesion, absorption, adsorption or chemical reaction), improving the efficiency of pollutant removal.
Conceptually, the invention involves generating turbulence of such a scale that the two species of interest are entrained to significantly differing extents, and is not limited to any particular apparatus and process. Optimum collision rates will occur for a system which maintains St<<1 for one species and St≧1 for the other species. The turbulence itself may be generated in any suitable manner, and is not limited to known vortex generators.
Although the invention has been described with particular reference to its application in pollution control, it can be used to design high efficiency mixers for other applications.
Further, although the invention has been described with particular reference to the mixing of particles in a gas stream, it also has application to mixing in other fluid flows, e.g. liquids.
The vanes need not be mounted in a rectilinear array. As shown in
In a further embodiment of the invention, two or more turbulence generators are spaced successively along the flow path, generating progressively larger turbulence eddies to promote the impact of progressively larger particles. Such an arrangement accommodates agglomerates which are progressively increased in size along the flow path. This embodiment has potential application in mist eliminators and fine particle agglomerators, as well as in chemical interaction or catalisation processes in which successively larger constituents are targeted to enhance the process efficiency.
Number | Date | Country | Kind |
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2004900593 | Feb 2004 | AU | national |
Filing Document | Filing Date | Country | Kind | 371c Date |
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PCT/AU05/00160 | 2/9/2005 | WO | 00 | 8/7/2006 |