Rectification-heat exchange coupled type tray and wet flue gas desulfurization tower

A technology of wet flue gas desulfurization and thermal coupling, which is applied in the direction of separation methods, gas treatment, chemical instruments and methods, etc., can solve the problems of complex process flow, large consumption of chemical reagents, high cost, etc., and achieve enhanced removal efficiency, The effect of no risk of clogging and simple structure

Pending Publication Date: 2020-12-25
HUAZHONG UNIV OF SCI & TECH
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

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Problems solved by technology

Based on these two characteristics, the wet flue gas desulfurization tower in the existing conventional flue gas purification equipment is considered to be the most effective in removing heavy metals and SO 3 potential, however, the current wet FGD for heavy metals and SO 3 The removal effect is not good, and it fluctuates greatly with the combustion conditions and unit configuration. Therefore, the strengthening of wet flue gas desulfurization towers for heavy metals and SO 3 The control effect needs to be solved urgently
[0004] Among the existing technologies on the emission control of heavy metal pollutants in coal-fired flue gas, mainly include: (1) Patent CN108939875A discloses a device for collaborative removal of heavy metals in coal-fired power plants, including heavy metal removal devices arranged in sequence along the flue gas flow direction device, denitrification reactor, phase change agglomeration device, dust removal device, and desulfurization absorption tower, the heavy metal removal device is composed of lead removal device, primary oxidation conversion device, secondary oxidation conversion conversion device, absorption device, Composed of a mercury removal device, after two-stage oxidation and a coordinated absorption device, the arsenic and selenium in the flue gas are removed in a high-valence state by oxidation. This method can achieve a removal effect of 80%-99.5% for heavy metals, realizing Heavy metal synergistic removal of coal-fired flue gas, but the process is complicated, the transformation cost is high, and it is not suitable for large-scale application; (2) Patent CN109045963A discloses an oxidation-absorption removal of gaseous selenium dioxide in coal-fired flue gas In the method, the prepared oxidant and absorbent are sprayed from the upper part of the spray tower at the

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  • Rectification-heat exchange coupled type tray and wet flue gas desulfurization tower
  • Rectification-heat exchange coupled type tray and wet flue gas desulfurization tower
  • Rectification-heat exchange coupled type tray and wet flue gas desulfurization tower

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Embodiment 1

[0049] Application object: a wet flue gas desulfurization device in a power plant, the inlet flue gas volume is 1580000m 3 / h (standard state, wet basis), the selenium concentration in the inlet flue gas is 118μg / m 3 , the arsenic concentration is 39μg / m 3 , the lead concentration is 27μg / m 3 , SO 3 The concentration is 8mg / m 3 , the flue gas temperature at the entrance is 102°C, the slurry temperature inside the desulfurization tower is 53°C, and the operating liquid-gas ratio of the desulfurization tower is 12.

[0050] Retrofit plan: Add a rectification-heat exchange coupling tray in the desulfurization tower and install it 3m above the flue gas inlet. The ratio of the tube spacing to the tube diameter of the heat pipe bundle is 2, the ratio of the tube spacing to the tube diameter of the lower heat exchange tube bundle is 3, the diameter of the air flow channel hole is 50 mm, the minimum distance between the air flow channel hole and the edge of the gas distribution pl...

Embodiment 2

[0053] Application object: a wet flue gas desulfurization device in a power plant, the inlet flue gas volume is 3490000m3 3 / h (standard state, wet basis), the selenium concentration in the inlet flue gas is 67μg / m 3 , the arsenic concentration is 27μg / m 3 , the lead concentration is 15μg / m 3 , SO 3 The concentration is 15mg / m 3 , the flue gas temperature at the entrance is 121°C, the slurry temperature inside the desulfurization tower is 55°C, and the operating liquid-gas ratio of the desulfurization tower is 15.

[0054]Retrofit plan: Add a rectification-heat exchange coupling tray in the desulfurization tower and install it 6m above the flue gas inlet. The ratio of the tube spacing to the tube diameter of the heat pipe bundle is 5, the ratio of the tube spacing to the tube diameter of the lower heat exchange tube bundle is 6, the diameter of the airflow channel hole is 60mm, and the minimum distance between the airflow channel hole and the edge of the gas distribution p...

Embodiment 3

[0057] Application object: a wet flue gas desulfurization device in a power plant, the inlet flue gas volume is 620000m 3 / h (standard state, wet basis), the selenium concentration in the inlet flue gas is 58μg / m 3 , the arsenic concentration is 78μg / m 3 , the lead concentration is 21μg / m 3 , SO 3 The concentration is 11mg / m 3 , the flue gas temperature at the entrance is 97°C, the slurry temperature inside the desulfurization tower is 55°C, and the operating liquid-gas ratio of the desulfurization tower is 12.5.

[0058] Retrofit plan: Add a rectification-heat exchange coupling tray in the desulfurization tower and install it 1m above the flue gas inlet. The ratio of the tube spacing to the tube diameter of the heat pipe bundle is 10, the ratio of the tube spacing to the tube diameter of the lower heat exchange tube bundle is 12, the hole diameter of the air flow channel is 15 mm, the minimum distance between the air flow channel hole and the edge of the gas distribution ...

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Abstract

The invention belongs to the field of coal-fired flue gas treatment, and discloses a rectification-heat exchange coupled type tray and a wet flue gas desulfurization tower. The tray comprise an upper-layer heat exchange tube bundle, a spray liquid isolation plate, a gas distribution plate and a lower-layer heat exchange tube bundle which are fixedly connected in sequence from top to bottom; the upper-layer heat exchange tube bundle and the lower-layer heat exchange tube bundle are arranged in a cross shape; the spraying liquid isolation plate is located on the gas distribution plate; the spraying liquid isolation plate and the upper-layer heat exchange tube bundle are arranged in a cross shape; the spraying liquid isolation plate and the upper-layer heat exchange tube bundle divide the gasdistribution plate into a plurality of bubbling areas; a plurality of gas flow channel holes are formed in the bubbling areas. With the rectification-heat exchange coupled type tray and the wet fluegas desulfurization tower of the invention adopted, the problem that heavy metal pollutants and SO3 in coal-fired flue gas cannot be efficiently removed in a conventional wet flue gas desulfurizationtower at present can be solved. The tray and tower have the advantages of being remarkable in strengthening effect, simple in structure, low in cost, safe, reliable, free of other negative effects andthe like.

Description

technical field [0001] The invention belongs to the field of coal-fired flue gas treatment, and more specifically relates to a rectification-heat exchange coupled tray and a wet flue gas desulfurization tower. Background technique [0002] With the sharp increase in energy demand and consumption, coal power generation plays an important role. However, coal-fired power generation also brings a series of ecological and environmental problems, which must be properly resolved. Currently, conventional pollutants such as SO 2 , NO x The treatment of some trace unconventional pollutants (such as heavy metals, SO 3 ) has attracted increasing attention from all walks of life. Although heavy metals (arsenic, selenium, lead, etc.), SO 3 The absolute content of pollutants is low, but they are easy to accumulate in organisms, which will cause irreversible damage to the nervous system and reproductive system, and will also cause damage to the ecological environment of water bodies. SO...

Claims

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Application Information

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IPC IPC(8): B01D53/00B01D53/50B01D53/64B01D53/80B01D49/00
CPCB01D49/00B01D53/002B01D53/504B01D53/64B01D53/80B01D2258/0283
Inventor 罗光前邹仁杰方灿王莉吕敏胡红云李显姚洪
Owner HUAZHONG UNIV OF SCI & TECH
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