CN1280032A - Special device for processing so2 containing fume - Google Patents
Special device for processing so2 containing fume Download PDFInfo
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- CN1280032A CN1280032A CN 00119478 CN00119478A CN1280032A CN 1280032 A CN1280032 A CN 1280032A CN 00119478 CN00119478 CN 00119478 CN 00119478 A CN00119478 A CN 00119478A CN 1280032 A CN1280032 A CN 1280032A
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Abstract
The present invention relates to an equipment of eliminating SO2 from waste gas ane aims at treating waste gas with waste material and reducing production cost. The special equipment has a pulp mixing tank, which has a cinder powder feeding port and a supernatant liquor feeding port and leads pulp to the absorbant inlet of an absorbing tower. The absorption tower has a fume inlet and a fume outlet, and from the bottom of the absorption tower, reaction product is led to a circulation tank. Partial product in overflowed from the circulation tank to tank of the next stage absorption tower, and the gas after passing through two serially connected showering absorption towers is exhausted. The other partial product is led to settling separation tank, from which supernatant liquor is returned to the pulp mixing tank and the sediment is separated. With low cost, the method of the present invention may be used for environment protection in enterprise.
Description
The present invention relates to sulfur dioxide removal special equipment technical field in the waste gas.
At the protection environment, effectively purify SO
2On the smoke problem, a lot of scientific and technical personnel have developed various processing methods, as the patent No. is that China's " a kind of flue gas is done dirt sulfur removal technology and dedusting pond thereof " of 93115510.X is that a class is with rapid ball formula milk of lime spray absorption cleaning sulfur in smoke, its technological process sprays the milk of lime for preparing the SO that absorbs in the flue gas as shown in Figure 1 in the absorption tower
2, chemical reaction takes place, produce sulfurous acid, again with the compressed-air actuated oxygen that the feeds generation sulfuric acid that reacts, again through sulfuric acid and calcium hydroxide reaction production gypsum.Be characterized in that the milk of lime uptake is big, absorptivity is up to more than 99%, and lime is cheap, adapts to bearing of entreprise cost, yet numerous weak points are still arranged: though 1. rapid ball has improved SO in milk of lime and the flue gas
2Contact rate, but will regularly replace, must close sintering system during replacing, influence ordinary production, reduce the device operating rate; 2.,, and increase production cost because of quick lime contains impurity sometimes or need increase lime consumption through the lime of weathering though the milk of lime uptake is big; 3. reacted gypsum is not fully utilized under the limited situation of China's consumption, and business efficiency is not remarkable; 4. the belt filter press power consumption is big in the device, and guipure often ruptures, and aqueous gypsum is wanted artificial treatment, and is time-consuming; 5. the PROCESS FOR TREATMENT link is more, influence each other, and labor productivity is not high, and preparation milk of lime container is thick and stupid.Also having a class is that the patent No. is 85104062 Chinese patent " smoke catalytic agent and preparation method thereof ", it is a primary raw material with industrial wastes such as iron ore slag and cigarette mud, be equipped with active carbon and grain flour, ammonia is pore creating material, so the component compatibility is comparatively complicated, and need more mechanical device and complicated technological process, more catalyst changeout trouble in industrial application.
The object of the present invention is to provide a kind of treatment of wastes with processes of wastes against one another, the raw materials for production cost is extremely low, method is simple, technological process reasonably contains sulfur dioxide flue gas and handles isolated plant.
Technical scheme of the present invention is achieved in that a kind of sulfur dioxide flue gas processing isolated plant that contains, and it is characterized in that (1) has a slip mixing channel, the slag powder is set mends inlet and precipitate and separate pond supernatant circulation inlet port; (2) the slip mixing channel is carried slip and is connected to circulating slot with pipeline, circulating slot is delivered to the absorptive tower absorbent import with slip with pipeline, the absorption tower also is respectively arranged with gas approach and outlet, the bottom, absorption tower causes circulating slot with pipeline with product, and circulating slot part product uses the pipeline overflow to the next stage circulating slot simultaneously; (3) gas feed of next stage absorption tower connects upper level absorption tower gas vent with pipeline, to should with pipeline product being caused the absorptive tower absorbent import by the level circulating slot, absorbent outlet in bottom, absorption tower causes should the level circulating slot with pipeline, this absorption tower gas vent carries out emptying or causes the gas feed of next stage absorption tower going simultaneously, and this grade circulating slot causes the partial reaction product in precipitate and separate pond or the next stage circulating slot with pipeline and goes.(4) the precipitate and separate pond causes slip mixing channel supernatant circulation inlet port with supernatant with pipeline, precipitates and isolates the reactant that reacts completely simultaneously.
Above-mentioned absorption tower is the two-stage tandem spray column.
Above-mentioned slip is that the slag powder and the water of 120-250 order sizes is made into, and water and slag weight ratio are 2-5: 1, and slag is the slag that non-ferrous metals smelting works, ferrous metal smelting factory, power plant or oil plant are abandoned.
Facts have proved that the treatment of wastes with processes of wastes against one another is effective aborning, at first SO
2Fume emission obtains stable effectively control; Secondly, remedy rapid ball formula milk of lime spray column and purified SO
2The flue gas technical deficiency; The 3rd improves utilization ratio of device and labor productivity, and small investment, cost are low, profitable, and it is as shown in the table in index of correlation contrast:
| Technical name | Treatment of wastes with processes of wastes against one another SO 2Gas cleaning | Rapids ball formula milk of lime spray column SO 2Gas cleaning | Remarks |
| Raw material consumption and cost | Shanghai slag: 3.01T self-sufficiency, cost free | Lime 1.33T CaO needs 253 yuan | Handle 1T SO 2Consumption |
| The utilization of reactant | Produce reactant 15T and make chemical fertilizer 15T | Produce gypsum 8.1t/h and sell all the other stackings on a small quantity | Per hour produce reactant quantity (dry measure) |
| The exhaust emissions degree | 0-20PPM improves 25% than former technology | 40—80PPM | |
| Absorptivity | ????99．73％ | ????98．91 | |
| Process unit | Sedimentation and filtration is easy | Dense press filtration complexity |
Above data shows that the treatment of wastes with processes of wastes against one another purifies SO
2The flue gas new technology is considerably beyond rapid ball formula milk of lime spray column SO
2Flue gases purification more adapts to modern management.According to this enterprise sintering machine per hour desulfurization emit SO
23.33/t a large amount of flue gases of concentration 7300PPM are if continue to adopt rapid ball formula milk of lime spray column to purify SO
2Flue gas is probably seldom to guarantee and to carry out ordinary production that can not lower cost, more uncontrollable exhaust emissions is reduced to bottom line.In addition, the treatment of wastes with processes of wastes against one another brings more economic benefits to enterprise.According to above index of correlation measuring and calculating, save 8,050,000 yuan of the used quick lime expenses of milk of lime, reactant can utilize 1,080,000 villages, with 1,080 ten thousand yuan of the values of per ton hundred yuan of surveys, add saving traffic expense and other expenses and amount to about 2,000 ten thousand yuan, reduce about the about 660 yuan/t of identical cost.Plant investment, new technology and old technology will reduce the construction fund of concentrator, belt filter press at least, if with can purify SO
2The inlet device of flue gas more than 99.73% compare to save 60 surplus times.
Description of drawings:
Fig. 1. the milk of lime spray absorbs the sulfur dioxide in flue gas process chart;
Fig. 2. apparatus of the present invention flow chart.
Below in conjunction with description of drawings embodiments of the invention are further described:
As shown in the figure, this contains sulfur dioxide flue gas processing isolated plant a slip mixing channel, the slag powder is set on the slip mixing channel mends inlet and precipitate and separate pond supernatant circulation inlet port, the slip mixing channel causes circulating slot with slip with pipeline, circulating slot is delivered to the absorptive tower absorbent import with slip with pipeline again, the absorption tower also is respectively arranged with gas approach and outlet, the absorbent outlet of bottom, absorption tower causes circulating slot with pipeline with product, circulating slot part product overflows to the next stage circulating slot with pipeline simultaneously, gas feed pipeline in next stage absorption tower connects upper level absorption tower gas vent, this grade circulating slot causes the import of this grade absorptive tower absorbent with pipeline with product, the absorbent outlet of bottom, absorption tower causes this grade circulating slot with pipeline, this grade absorption tower gas vent carries out emptying simultaneously, this grade circulating slot causes the precipitate and separate pond with the partial reaction product with pipeline, the precipitate and separate pond causes slip mixing channel supernatant circulation inlet port with supernatant with pipeline, precipitates and isolates the reactant that reacts completely simultaneously.
Two-stage tandem spray column mode is adopted on above-mentioned absorption tower, described slip is that the slag powder and the water of 120-250 order sizes is made into, water and slag weight ratio are 2-5: 1, and slag can be non-ferrous metals smelting works, the slag that ferrous metal smelting factory, power plant or oil plant are abandoned.
Claims (3)
1. contain sulfur dioxide flue gas and handle isolated plant, it is characterized in that:
(1) a slip mixing channel is arranged, the slag powder is set mends inlet and precipitate and separate pond supernatant circulation inlet port;
(2) the slip mixing channel is carried slip and is connected to circulating slot with pipeline, circulating slot is delivered to the absorptive tower absorbent import with slip with pipeline, the absorption tower also is respectively arranged with gas approach and outlet, the bottom, absorption tower causes circulating slot with pipeline with product, and circulating slot part product uses the pipeline overflow to the next stage circulating slot simultaneously;
(3) gas feed of next stage absorption tower connects upper level absorption tower gas vent with pipeline, to should with pipeline product being caused the absorptive tower absorbent import by the level circulating slot, absorbent outlet in bottom, absorption tower causes should the level circulating slot with pipeline, this absorption tower gas vent carries out emptying or causes the gas feed of next stage absorption tower going simultaneously, and this grade circulating slot causes the partial reaction product in precipitate and separate pond or the next stage circulating slot with pipeline and goes.
(4) the precipitate and separate pond causes slip mixing channel supernatant circulation inlet port with supernatant with pipeline, precipitates and isolates the reactant that reacts completely simultaneously.
2. the sulfur dioxide flue gas that contains as claimed in claim 1 is handled isolated plant, it is characterized in that described absorption tower employing two-stage tandem spray column.
3. the sulfur dioxide flue gas that contains as claimed in claim 2 is handled isolated plant, it is characterized in that described slip is that the slag powder and the water of 120-250 order sizes is made into, water and slag weight ratio are 2-5: 1, slag can be non-ferrous metals smelting works, the slag that ferrous metal smelting factory, power plant or oil plant are abandoned.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN00119478A CN1096285C (en) | 2000-07-17 | 2000-07-17 | Special device for processing so2 containing fume |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN00119478A CN1096285C (en) | 2000-07-17 | 2000-07-17 | Special device for processing so2 containing fume |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| CN1280032A true CN1280032A (en) | 2001-01-17 |
| CN1096285C CN1096285C (en) | 2002-12-18 |
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ID=4587722
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN00119478A Expired - Lifetime CN1096285C (en) | 2000-07-17 | 2000-07-17 | Special device for processing so2 containing fume |
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| Country | Link |
|---|---|
| CN (1) | CN1096285C (en) |
Cited By (9)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN107569998A (en) * | 2017-09-27 | 2018-01-12 | 湖南新龙矿业有限责任公司 | A kind of mine tailing smelts three wastes desulphurization system and method |
| US10207220B2 (en) | 2017-03-15 | 2019-02-19 | Jiangnan Environmental Protection Group Inc. | Method and apparatus for removing sulfur oxides from gas |
| US10213739B2 (en) | 2017-05-25 | 2019-02-26 | Jiangnan Environmental Protection Group Inc. | Dust removal and desulfurization of FCC exhaust gas |
| US10357741B2 (en) | 2017-09-07 | 2019-07-23 | Jiangnan Environmental Protection Group Inc. | Method for controlling aerosol production during absorption in ammonia desulfurization |
| US10399033B2 (en) | 2017-05-25 | 2019-09-03 | Jiangnan Environmental Protection Group Inc. | Ammonia-based desulfurization process and apparatus |
| US10583386B2 (en) | 2017-06-14 | 2020-03-10 | Jiangnan Environmental Protection Group Inc. | Ammonia-adding system for ammonia-based desulfurization device |
| US10953365B2 (en) | 2018-07-20 | 2021-03-23 | Jiangnan Environmental Protection Group Inc. | Acid gas treatment |
| US11027234B2 (en) | 2018-04-13 | 2021-06-08 | Jiangnan Environmental Protection Group Inc. | Oxidization of ammonia desulfurization solution |
| US11224838B2 (en) | 2019-12-26 | 2022-01-18 | Jiangnan Environmental Protection Group Inc. | Controlling aerosol production during absorption in ammonia-based desulfurization |
Family Cites Families (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN1061914A (en) * | 1990-11-29 | 1992-06-17 | 湖南大学 | A kind of dusting and desulfurizing technology for smoke of coal-fired boiler |
-
2000
- 2000-07-17 CN CN00119478A patent/CN1096285C/en not_active Expired - Lifetime
Cited By (21)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US10207220B2 (en) | 2017-03-15 | 2019-02-19 | Jiangnan Environmental Protection Group Inc. | Method and apparatus for removing sulfur oxides from gas |
| US10675584B2 (en) | 2017-03-15 | 2020-06-09 | Jiangnan Environmental Protection Group Inc. | Method and apparatus for removing sulfur oxides from gas |
| US10406477B2 (en) | 2017-03-15 | 2019-09-10 | Jiangnan Environmental Protection Group Inc. | Method and apparatus for removing sulfur oxides from gas |
| US10413864B2 (en) | 2017-03-15 | 2019-09-17 | Jiangnan Environmental Protection Group Inc. | Method and apparatus for removing sulfur oxides from gas |
| US10471383B2 (en) | 2017-05-25 | 2019-11-12 | Jiangnan Environmental Protection Group Inc. | Dust removal and desulfurization of FCC exhaust gas |
| US10213739B2 (en) | 2017-05-25 | 2019-02-26 | Jiangnan Environmental Protection Group Inc. | Dust removal and desulfurization of FCC exhaust gas |
| US10343110B2 (en) | 2017-05-25 | 2019-07-09 | Jiangnan Environmental Protection Group Inc. | Dust removal and desulfurization of FCC exhaust gas |
| US10561982B2 (en) | 2017-05-25 | 2020-02-18 | Jiangnan Environmental Protection Group Inc. | Ammonia-based desulfurization process and apparatus |
| US10399033B2 (en) | 2017-05-25 | 2019-09-03 | Jiangnan Environmental Protection Group Inc. | Ammonia-based desulfurization process and apparatus |
| US10406478B2 (en) | 2017-05-25 | 2019-09-10 | Jiangnan Environmental Protection Group Inc. | Ammonia-based desulfurization process and apparatus |
| US10413865B2 (en) | 2017-05-25 | 2019-09-17 | Jiangnan Enviromental Protection Group Inc. | Ammonia-based desulfurization process and apparatus |
| US10589212B2 (en) | 2017-06-14 | 2020-03-17 | Jiangnan Environmental Protection Group Inc. | Ammonia-adding system for ammonia-based desulfurization device |
| US10583386B2 (en) | 2017-06-14 | 2020-03-10 | Jiangnan Environmental Protection Group Inc. | Ammonia-adding system for ammonia-based desulfurization device |
| US10449488B2 (en) | 2017-09-07 | 2019-10-22 | Jiangnan Environmental Protection Group Inc. | Method for controlling aerosol production during absorption in ammonia desulfurization |
| US10369517B2 (en) | 2017-09-07 | 2019-08-06 | Jiangnan Environmental Protection Group Inc. | Method for controlling aerosol production during absorption in ammonia desulfurization |
| US10357741B2 (en) | 2017-09-07 | 2019-07-23 | Jiangnan Environmental Protection Group Inc. | Method for controlling aerosol production during absorption in ammonia desulfurization |
| CN107569998A (en) * | 2017-09-27 | 2018-01-12 | 湖南新龙矿业有限责任公司 | A kind of mine tailing smelts three wastes desulphurization system and method |
| US11027234B2 (en) | 2018-04-13 | 2021-06-08 | Jiangnan Environmental Protection Group Inc. | Oxidization of ammonia desulfurization solution |
| US10953365B2 (en) | 2018-07-20 | 2021-03-23 | Jiangnan Environmental Protection Group Inc. | Acid gas treatment |
| US11529584B2 (en) | 2018-07-20 | 2022-12-20 | Jiangnan Environmental Protection Group Inc. | Acid gas treatment |
| US11224838B2 (en) | 2019-12-26 | 2022-01-18 | Jiangnan Environmental Protection Group Inc. | Controlling aerosol production during absorption in ammonia-based desulfurization |
Also Published As
| Publication number | Publication date |
|---|---|
| CN1096285C (en) | 2002-12-18 |
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| C10 | Entry into substantive examination | ||
| SE01 | Entry into force of request for substantive examination | ||
| C06 | Publication | ||
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Granted publication date: 20021218 |