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Aim:- To perform analysis on cyclone separator and calculate the separation efficiency and pressure drop. Objective: To study different empirical models used to calculate the cyclone separator efficiency. To perform an analysis on the cyclone separator model and understanding its working. To understand…
Vishavjeet Singh Yadav
updated on 10 Sep 2020
Aim:- To perform analysis on cyclone separator and calculate the separation efficiency and pressure drop.
Objective:
Introduction
Cyclone separators are separation devices (dry scrubbers) that remove particulate matter from flue gases by using the principle of inertia. Cyclone separators are one of many air pollution control devices known as pre-cleaners since they generally remove larger pieces of particulate matter. This prevents finer filtration methods from having to deal with large, more abrasive particles later on. In addition, several cyclone separators can operate in parallel, and this system is known as a multi-cyclone.
Working
Cyclone separators work much like a centrifuge, but with a continuous feed of dirty air. In a cyclone separator, dirty flue gas is fed into a chamber. The inside of the chamber creates a spiral vortex, similar to a tornado. This spiral formation and the separation are shown in the Figure shown below. The lighter components of this gas have less inertia, so it is easier for them to be influenced by the vortex and travel up it. Contrarily, larger components of particulate matter have more inertia and are not as easily influenced by the vortex.
Since these larger particles have difficulty following the high-speed spiral motion of the gas and the vortex, the particles hit the inside walls of the container and drop down into a collection hopper. These chambers are shaped like an upside-down cone to promote the collection of these particles at the bottom of the container. The cleaned flue gas escapes out the top of the chamber.
Most cyclones are built to control and remove particulate matter that is larger than 10 micrometers in diameter. However, there do exist high-efficiency cyclones that are designed to be effective on particles as small as 2.5 micrometers. As well, these separators are not effective on extremely large particulate matter. For particulates around 200 micrometers in size, gravity settling chambers or momentum separators are a better option.
Out of all of the particulate-control devices, cyclone separators are among the least expensive. They are often used as a pre-treatment before the flue gas enters more effective pollution control devices. Therefore, cyclone separators can be seen as "rough separators" before the flue gas reaches the fine filtration stages.
Cyclone separators are generally able to remove somewhere between 50-99% of all particulate matter in the flue gas. How well the cyclone separators are actually able to remove this matter depends largely on particle size. If there is a large amount of lighter particulate matter, less of these par0ticles are able to be separated out. Because of this, cyclone separators work best on flue gases that contain large amounts of big particulate matter.
There are several advantages and disadvantages of using cyclone separators. First, cyclone separators are beneficial because they are not expensive to install or maintain, and they have no moving parts. This keeps maintenance and operating costs low. Second, the removed particulate matter is collected when dry, which makes it easier to dispose of. Finally, these units take up very little space. Although effective, there are also disadvantages in using cyclone separators. Mainly because the standard models are not able to collect particulate matter that is smaller than 10 micrometers effectively and the machines are unable to handle sticky or tacky materials well.
Different Empirical models used for cyclone separator efficiency:
4.1. Iozia and Leith Model
Particle Size | 1μm | 2 μm | 3 μm | 4 μm | 5 μm |
Particle Time | ![]() |
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Particle Size | Tracked | Escaped | Trapped | Incomplete | Efficiency |
1 μm | 576 | 266 | 301 | 9 | 0.522 |
2 μm | 576 | 245 | 329 | 2 | 0.571 |
3 μm | 576 | 202 | 374 | - | 0.649 |
4 μm | 576 | 189 | 387 | - | 0.671 |
5 μm | 576 | 166 | 410 | - | 0.712 |
Particle Velocity | 1 m/s | 2 m/s | 3 m/s | 4 m/s | 5 m/s |
Particle Time | ![]() |
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Pressure | ![]() |
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Velocity | ![]() |
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Vortex | ![]() |
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Particle Velocity | Tracked | Escaped | Trapped | Incomplete | Pressure at Inlet [Pa] | Pressure at Outlet-1 | Pressure at Outlet-2 | Total Pressure Drop | Efficiency |
1 m/s | 576 | 220 | 240 | 116 |
2.36565 |
0.1901 | 0.3571 | 1.87855 | 0.416667 |
2 m/s | 576 | 183 | 385 | 8 |
9.89978 |
0.7815 | 1.2726 | 8.62716 | 0.6684 |
3 m/s | 576 | 137 | 439 | - |
11.9642 |
1.6573 | 2.3941 | 9.5701 | 0.76215 |
4 m/s | 576 | 95 | 481 | - | 18.6148 | 3.0441 | 4.1623 | 14.4525 | 0.8351 |
5 m/s | 576 | 58 | 518 | - |
34.0316 |
4.3134 | 5.8386 | 28.193 | 0.8993 |
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