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Stabilization method for secondary release of mercury in seawater desulfurization of coal-fired power plant and application

A secondary release, coal-fired power plant technology, applied in separation methods, chemical instruments and methods, water pollutants, etc., can solve problems such as low mercury removal efficiency, large oxidant consumption, increased absorption liquid corrosion, etc., to achieve industrial application High value, reduced secondary release, and low environmental impact

Pending Publication Date: 2021-06-11
XIAMEN HUAXIA INT POWER DEV +2
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

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Problems solved by technology

However, due to the direct injection method, the absorbed mercury is still free in the absorption liquid, which cannot inhibit the reduction of mercury, and consumes a lot of oxidants.
[0007] The Chinese invention patent with the publication number CN1962034 discloses a method and device for simultaneous desulfurization, denitrification and mercury removal of boiler flue gas, but the addition of chloride ions will increase the corrosion of the device by the absorbing liquid. At the same time, although mercury is partially complexed in the absorbing liquid, its The reduction inhibition effect is not ideal, and the total mercury removal efficiency is not high

Method used

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  • Stabilization method for secondary release of mercury in seawater desulfurization of coal-fired power plant and application

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Experimental program
Comparison scheme
Effect test

Embodiment 1

[0054] The concentration of mercury in the analog flue gas is 40 μg / m 3 SO 2 The concentration of 1000 ppm, NOx concentration is 300 ppm, and the gas flow is 1 L / min. Add NaClo and Fenton reagents in seawater, Fe 3+ With h 2 O 2 The molar ratio is 0.6, the Fenton reagent is added to H 2 O 2 The amount was 0.1 mmol / L, NaClo added amount was 3 mmol / L, sea water pH of 7.2, and the temperature was 55 ° C. Absorbing the simulated flue gas by single-layer spraying method, SO 2 The removal rate is above 70%, and the NOx removal rate is over 35%, and the removal rate of mercury is 65%. Then, 500 ml of the reaction after the reaction was taken, 5 mmol / L sodium sulfate solution was added thereto, and sodium thiosulfate solution was added thereto. 2- S 2 O 3 2- The molar ratio is 1, and the solution is stirred. The mercury content of the solid phase was 11%, and the mercury content in the liquid phase was 54%, and the escape amount of mercury in the gas phase was 35%.

Embodiment 2

[0056] The concentration of mercury in the analog flue gas is 40 μg / m 3 SO 2 The concentration of 1000 ppm, NOx concentration is 300 ppm, and the gas flow is 1 L / min. NaClo, Fenton reagent, Fe 3+ With h 2 O 2 The molar ratio is 0.8, the Fenton reagent is added to H 2 O 2 The amount was 0.1 mmol / L, NaClo added is 3 mmol / L, and the sea water is 7.5, and the temperature is 55 ° C. Absorbing the simulated flue gas by single-layer spraying method, SO 2 The removal rate is more than 70%, and the NOx removal rate is over 35%, and the removal rate of mercury is 70%. Then, 500 ml of the reaction after the reaction was taken, 6 mmol / L sodium sulfate solution was added thereto, and sodium thiosulfate solution was added thereto. 2- S 2 O 3 2- The molar ratio is 1, and the solution is stirred. The mercury content of the solid phase was 21%, and the mercury content in the liquid phase was 53%, and the escape amount of mercury in the gas phase was 26%.

Embodiment 3

[0058] The concentration of mercury in the analog flue gas is 40 μg / m 3 SO 2 The concentration of 1000 ppm, NOx concentration is 300 ppm, and the gas flow is 1 L / min. NaClo, Fenton reagent, Fe 3+ With h 2 O 2 The molar ratio is 1, the Fenton reagent is added to H 2 O 2 The amount was 0.1 mmol / L, NaClo added amount was 2 mmol / L, sea water pH of 7.5, and the temperature was 60 ° C. Absorbing the simulated flue gas by single-layer spraying method, SO 2 The removal rate is more than 70%, and the NOx removal rate is over 35%, and the removal rate of mercury is 71%. Then, 500 ml of the reaction after the reaction was taken, 6 mmol / L sodium sulfate solution was added thereto, and sodium thiosulfate solution was added thereto. 2- S 2 O 3 2- The molar ratio is 1, and the solution is stirred. The mercury content of the solid phase was 15%, and the mercury content in the liquid phase was 47%, and the escape amount of mercury in the gas phase was 33%.

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Abstract

The invention relates to a stabilization method for secondary release of mercury in seawater desulfurization of a coal-fired power plant and application. The stabilization method comprises the following steps: a, uniformly mixing seawater and an oxidizing agent; b, spraying the seawater uniformly mixed in the step a into the desulfurization tower, and mixing the seawater with flue gas in the desulfurization tower to wash the flue gas; c, the seawater treated in the step b flows out of the desulfurization tower and then flows into an aeration tank, a stabilizer is sprayed into the aeration tank, divalent mercury in the seawater is fixed, and secondary release of zero-valent mercury regenerated in the aeration tank is reduced; and d, filtering the seawater in the step b and the step c to separate mercury in the seawater. According to the stabilization method for secondary release of mercury in seawater desulfurization of the coal-fired power plant and the application, zero-valent mercury in flue gas is oxidized into divalent mercury by adding the oxidizing agent into the desulfurization tower, and divalent mercury in seawater is fixed by adding the stabilizing agent into the aeration tank, so that secondary release of mercury in seawater desulfurization of the coal-fired power plant is reduced, the corrosion to equipment is relatively small, and the pollution to the environment is relatively small.

Description

Technical field [0001] The present invention belongs to the field of air pollution control, and in particular, the present invention relates to a stable method and application of mercury secondary release in seawater desulfurization in coal-fired power plants. Background technique [0002] Heavy metallic mercury (HG) Although the content is very small in coal, it is a trace element, but since it has a wide focus on its volatile, volatility and biological accumulation characteristics. At the same time, mercury is the only toxic weight metal pollutant with global hazards, which will cause cross-regional pollution, resulting in environmental damage, and mercury will accumulate in biology, leading to various diseases. At present, coal combustion is considered to be the most important source of human mercury emissions, and my country will not have significant changes in coal-based energy structure in the next 50 years, so how to solve mercury pollution has aroused extensive attention....

Claims

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Application Information

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Patent Type & Authority Applications(China)
IPC IPC(8): B01D53/78B01D53/50B01D53/56B01D53/64C02F9/04C02F103/18C02F101/20
CPCB01D53/78B01D53/507B01D53/56B01D53/64C02F9/00B01D2251/10B01D2251/108B01D2251/106B01D2258/0283B01D2257/602C02F1/72C02F1/62C02F1/001C02F2103/18C02F2101/20
Inventor 黄见勋王乐乐苏胜谢建南尹子俊向军许积庄洪清池孙赐文叶顺长何川马云龙孔凡海雷嗣远谢敏勤
Owner XIAMEN HUAXIA INT POWER DEV