A treatment method and device for flue gas and flue gas desulfurization wastewater

A technology for desulfurization wastewater and treatment methods, which is applied in gas treatment, separation methods, combined devices, etc., can solve the problems of unreduced flue gas temperature, high power consumption of electric mist eliminators, and high power consumption, so as to prevent deposition and accumulation. The effect of increasing the water vapor content and increasing the heat exchange rate

Active Publication Date: 2020-09-11
CHINA PETROLEUM & CHEM CORP +1
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  • Abstract
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AI Technical Summary

Problems solved by technology

Literature "SO in coal-fired flue gas 3 Causes, Impacts and Emission Reduction Countermeasures” mentions the use of wet electrostatic precipitators to remove SO 3 , the removal rate can reach 95%, but the construction and operation costs are relatively high
[0006] CN102335553A passes the sodium-based flue gas desulfurization wastewater into the bipolar membrane electrodialysis device, relies on the selective permeation of the membrane and the electrolysis device, regenerates the desulfurization absorbent, and produces sulfuric acid by-product, realizing "zero discharge" of desulfurization wastewater, but The technology consumes more power
CN103936220A first separates the desulfurization wastewater from solid and liquid, and then uses steam mechanical recompression technology (MVR) to recover sodium sulfite or ammonium salt. This technology better solves the problem of zero discharge of desulfurization wastewater, but the flue gas temperature has not been reduced, and the water consumption is still Larger and not involved in "white smoke" issues
CN104801162A uses ammonia water as reducing agent and absorbent to carry out denitrification and desulfurization treatment on flue gas respectively, purifies flue gas and removes mist droplets with wet electric demister, can eliminate "smoke plume" and "blue smoke" phenomenon, but due to the purification of flue gas Before the gas is emptied, it is still a saturated gas, and the temperature is high, which still cannot effectively solve the "white smoke" problem, and the power consumption of the electric demister is very large
However, this technology requires major changes to the boiler economizer to arrange the desulfurization wastewater heating system, which requires a high investment; and the moisture evaporated by the high-temperature flue gas enters the desulfurization tower together with the flue gas for recycling, which increases the desulfurization. Waste liquid treatment scale

Method used

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  • A treatment method and device for flue gas and flue gas desulfurization wastewater
  • A treatment method and device for flue gas and flue gas desulfurization wastewater
  • A treatment method and device for flue gas and flue gas desulfurization wastewater

Examples

Experimental program
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Effect test

Embodiment 1

[0039] Table 1 shows the sulfur-containing flue gas composition of a certain boiler flue gas after denitrification treatment.

[0040] Table 1 Composition of sulfur-containing flue gas after denitrification of a certain boiler flue gas

[0041]

[0042] Calculate the dew point temperature of flue gas acid (sulfuric acid) before and after desulfurization treatment according to the following formula:

[0043]

[0044] in,[ H 2 O ]——the content of water vapor in the flue gas, vol%.

[0045] [ SO3 ] - sulfur trioxide content in flue gas, vol %.

[0046] Different water vapor content and different SO 3 The sulfuric acid dew point temperature under the concentration is shown in Table 2. Keep the temperature of the flue gas after heat exchange with the desulfurization wastewater in the casing heat exchanger at 120-130°C, and no acid dew point corrosion will occur in the flue gas pipeline.

[0047] Table 2 Different water vapor content and different SO 3 flue gas dew p...

Embodiment 2

[0052] SO in flue gas to be treated 2 Concentration 1500mg / Nm 3 , SO 3 Concentration 140mg / Nm 3 , smoke volume and other parameters are the same as in Example 1.

[0053] Adopt the present invention to attach figure 1 Said treatment device: the flow rate of desulfurization wastewater in the outer pipe is 3.0m / s, and the desulfurization reaction zone adopts the form of absorbent spraying. Specific operating conditions: (1) Control the temperature of the flue gas desulfurization wastewater before entering the flue gas / desulfurization wastewater heat exchanger at 80°C, combined with Table 2, the temperature of the flue gas after heat exchange between the casing heat exchanger and the desulfurization wastewater is 120°C , there will be no sulfuric acid dew point corrosion; (2) NaOH solution with a mass concentration of 1.6% is sprayed at the outlet of the casing heat exchanger, the water vapor content in the flue gas entering the bag filter is 15%, and the flue gas temperature...

Embodiment 3

[0056] The processing flow and operating conditions are the same as in Example 1. The difference is that the spindle-shaped structured packing described in CN104607009A is filled in the dust removal and desulfurization zone of the dust removal and desulfurization tower.

[0057] Effect: Purify SO in flue gas 3 Not detected, dust concentration 3mg / Nm 3 .

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Abstract

The invention relates to a treatment method for flue gas and flue gas desulfurization wastewater. In the flue gas / desulfurization wastewater heat exchanger, the flue gas is used to exchange heat for the desulfurization wastewater, and a nozzle is set at the outlet of the flue gas to spray NaOH solution to make the flue gas At this time, the flue gas enters the bag filter to remove dust and sulfate / sulfuric acid droplets, and then enters the desulfurization tower; desulfurization purification and heating are carried out in the desulfurization tower, and the waste water at the bottom of the tower is used as The absorption liquid is circulated, and the others enter the plate heat exchanger in the form of desulfurization wastewater; the plate heat exchanger uses the steam condensed water generated by the heating coil in the exhaust cylinder to preheat the desulfurization wastewater, and after preheating, the wastewater enters the flue gas / desulfurization wastewater exchange heater. On the basis of making full use of the waste heat of the flue gas, the present invention realizes the dual purpose of purifying the flue gas to meet the emission requirements and zero discharge of flue gas desulfurization waste liquid, and simultaneously eliminates "white smoke" and "blue smoke", and reduces the cost of flue gas desulfurization. and the comprehensive treatment cost of desulfurization waste liquid.

Description

technical field [0001] The invention belongs to the field of environmental protection waste water and waste gas treatment, and in particular relates to a sodium method flue gas desulfurization and a treatment method and device for the generated flue gas desulfurization waste water. Background technique [0002] Since 2003, my country's SO 2 The total emissions have remained high. In 2014, my country's SO 2 The total emissions were 19.744 million tons, which was below 20 million tons for the first time since 2003. Common flue gas desulfurization methods mainly include dry method and wet method. Compared with dry desulfurization, wet desulfurization equipment is small, easy to operate, and has high desulfurization efficiency. It is widely used, such as sodium method, magnesium method, ammonia method and calcium method, among which sodium method and calcium method are the most. Wet desulfurization can also be divided into discarding method and recycling method according to w...

Claims

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Application Information

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Patent Type & Authority Patents(China)
IPC IPC(8): B01D53/50B01D53/78B01D50/00
CPCB01D53/002B01D53/343B01D53/504B01D2251/304B01D2251/604B01D2259/124B01D2258/0283B01D50/60
Inventor 王明星阮宗林李欣姜阳
Owner CHINA PETROLEUM & CHEM CORP
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