CN105972629A - Hazardous waste and waste gas treatment equipment and technology - Google Patents
Hazardous waste and waste gas treatment equipment and technology Download PDFInfo
- Publication number
- CN105972629A CN105972629A CN201610434994.7A CN201610434994A CN105972629A CN 105972629 A CN105972629 A CN 105972629A CN 201610434994 A CN201610434994 A CN 201610434994A CN 105972629 A CN105972629 A CN 105972629A
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- Prior art keywords
- gas
- waste
- hazardous waste
- emulsator
- waste gas
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Classifications
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23K—FEEDING FUEL TO COMBUSTION APPARATUS
- F23K5/00—Feeding or distributing other fuel to combustion apparatus
- F23K5/02—Liquid fuel
- F23K5/08—Preparation of fuel
- F23K5/10—Mixing with other fluids
- F23K5/12—Preparing emulsions
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/46—Removing components of defined structure
- B01D53/48—Sulfur compounds
- B01D53/50—Sulfur oxides
- B01D53/501—Sulfur oxides by treating the gases with a solution or a suspension of an alkali or earth-alkali or ammonium compound
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/46—Removing components of defined structure
- B01D53/48—Sulfur compounds
- B01D53/50—Sulfur oxides
- B01D53/507—Sulfur oxides by treating the gases with other liquids
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2251/00—Reactants
- B01D2251/20—Reductants
- B01D2251/206—Ammonium compounds
- B01D2251/2067—Urea
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2251/00—Reactants
- B01D2251/30—Alkali metal compounds
- B01D2251/304—Alkali metal compounds of sodium
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2251/00—Reactants
- B01D2251/30—Alkali metal compounds
- B01D2251/306—Alkali metal compounds of potassium
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2251/00—Reactants
- B01D2251/60—Inorganic bases or salts
- B01D2251/604—Hydroxides
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- Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- General Chemical & Material Sciences (AREA)
- Health & Medical Sciences (AREA)
- Biomedical Technology (AREA)
- Environmental & Geological Engineering (AREA)
- Analytical Chemistry (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Mechanical Engineering (AREA)
- General Engineering & Computer Science (AREA)
- Combustion & Propulsion (AREA)
- Treating Waste Gases (AREA)
Abstract
The invention discloses a hazardous waste and waste gas treatment technology and equipment. The hazardous waste and waste gas treatment equipment comprises a material mixing pool arranged in a plant. A gas outlet of the material mixing pool is connected with a washing tower through a gas outlet pipeline. An induced draught fan is installed on the gas outlet pipeline. An emulsifier is arranged on one side of the bottom of the washing tower. An outlet pipeline of the emulsifier passes through a circulating pump and is connected to an inlet of a combustor and the upper portion of the washing tower. An outlet in the top of the washing tower leads to the interior a rotary kiln and the interior of the plant through communicating pipes correspondingly. By the adoption of the above equipment and method, the concentration of organic volatiles and gas or powder concentration in airtight space are reduced, the field environment is improved, meanwhile, safety risks are lowered, and an emulsion agent and alkali liquid are used for emulsifying diesel oil according to a certain proportion; and meanwhile, acid gas generated by a breaker and in the mixing process can be absorbed, corrosion to the equipment and the plant is prevented, the emulsified diesel oil is used for improving the combustion state, emission of sulfur dioxide is reduced, secondary pollutants cannot be generated, and the cost of treating tail gas is reduced.
Description
Technical field
The present invention relates to a kind of solid burning waste residue resource and utilize disposal technology, specifically a kind of hazardous waste waste gas disposing technique and equipment.
Background technology
Making solid waste reducing, innoxious administering method have: sanitary landfills, centralized burning, recycling resource etc., burning disposal is increasingly used by a lot of countries because of the advantage of himself uniqueness, the important means of Ye Shi China solidification disposal of waste.When using this processing mode, solid dangerous waste has quite a few solid waste, barreled liquid needs to be crushed by disintegrating machine, deliver to compound hole after Po Sui mix, and crush and mixed process can produce organic volatile and overflow, even more than explosion limit, careless slightly will result in is caught fire or detonation.
Major part producer uses and delivers to exhaust gas processing device by air-introduced machine or partly deliver to incinerator as combustion air at present, but, the organic volatile substrate concentration that broken and mixed process produces is high, high by exhaust gas processing device operating cost, the most also produce the secondary pollution such as waste water or waste active carbon;Being passed to incinerator, incinerator uses air quantity limited, it is impossible to meet demand of bleeding, additionally containing a large amount of volatile matters in air, in fact it could happen that reaching explosion limit, incinerator is open firing point, can cause detonation, has great potential safety hazard.
Summary of the invention
The technical problem to be solved in the present invention is to provide a kind of organic volatile substrate concentration that can reduce in confined space and abnormal smells from the patient, improves site environment, reduces vent gas treatment cost and does not produce hazardous waste waste gas disposal facility and the technique of secondary pollution.
In order to solve above-mentioned technical problem, the hazardous waste waste gas disposal facility of the present invention, including the batch mixing pond arranged in Factory Building, the gas outlet in batch mixing pond connects scrubbing tower by outlet pipe, air-introduced machine is installed on outlet pipe, the bottom side of scrubbing tower is provided with emulsator, and the export pipeline of emulsator is connected to the entrance of burner and the top of scrubbing tower after a circulating pump, and the top exit of scrubbing tower is by respectively leading in rotary kiln and Factory Building communicating pipe.
Described batch mixing pond be provided above disintegrating machine, be provided with feed well between the open top in described disintegrating machine and batch mixing pond, the top of described disintegrating machine is provided with feed hopper.
A kind of hazardous waste waste gas disposing technique using above-mentioned hazardous waste waste gas disposal facility, comprises the following steps:
A, fuel and alkali liquor are proportionally added in emulsator, through being sufficiently stirred for emulsifying, prepare oil-water emulsion;
B, joining in scrubbing tower by emulsion through the export pipeline of emulsator, ON cycle pump is circulated washing;
C, opening air-introduced machine, carry out blended absorbent with oil-water emulsion in the organic volatile that batch mixing pond produces being delivered to scrubbing tower by air-introduced machine, the gas after absorption cleaning is through delivering to rotary kiln communicating pipe or being discharged in Factory Building;
D, liquid after absorption cleaning deliver to the entrance of burner through circulating pump after returning to emulsator.
Described fuel is 1:9 ~ 9:1 with the ratio of alkali liquor.
Described fuel is natural gas, diesel oil, tire oil or heavy oil, and described alkali liquor is sodium hydroxide, potassium hydroxide or carbamide.
nullAfter using above-mentioned equipment and method,Due to the air-introduced machine arranged between batch mixing pond and washing pump,The circulating pump arranged between emulsator and emulsator and washing pump that the bottom side of scrubbing tower is arranged,Thus the Organic substance volatile matter or the powder body that produce in disintegrating machine and mixed process effectively can be absorbed,Reduce the organic volatile substrate concentration in confined space and abnormal smells from the patient or powder concentration,Improve site environment,Reduce security risk simultaneously,Use emulsifying agent and alkali liquor that diesel oil (heavy oil) is carried out emulsifying by a certain percentage,The acid gas produced in disintegrating machine and mixed process can be absorbed simultaneously,Prevent the corrosion of equipment and Factory Building,The material being dissolved in oil be dissolved in water can be absorbed by diesel oil (heavy oil) and water respectively,Acidic materials are neutralized by alkali,The diesel oil (heavy oil) after emulsifying is used to improve fired state,Decrease the discharge of sulfur dioxide,Secondary pollution will not be produced and decrease the expense of vent gas treatment.
Accompanying drawing explanation
Fig. 1 is the structural representation of hazardous waste waste gas disposal facility of the present invention.
Detailed description of the invention
Below in conjunction with the accompanying drawings and detailed description of the invention, the hazardous waste waste gas disposal facility of invention is described in further detail.
As shown in the figure, the hazardous waste waste gas disposal facility of the present invention, including the batch mixing pond 2 arranged in Factory Building 1, the gas outlet in batch mixing pond 2 connects scrubbing tower 4 by outlet pipe 3, air-introduced machine 5 is installed on outlet pipe 3, the bottom side of scrubbing tower 4 is provided with emulsator 6, and the export pipeline of emulsator 6 is connected to entrance and the top of scrubbing tower 4 of burner 8 after a circulating pump 7, and the top exit of scrubbing tower 4 is by respectively leading in rotary kiln 9 and Factory Building 1 communicating pipe.
Further, described batch mixing pond 2 be provided above disintegrating machine 10, being provided with feed well 11 between the open top in disintegrating machine 10 and batch mixing pond 2, the top of disintegrating machine 10 is provided with feed hopper 12, and the gas outlet in batch mixing pond 2 enters in outlet pipe 3 after disintegrating machine and feed well 11.
A kind of hazardous waste waste gas disposing technique using above-mentioned hazardous waste waste gas disposal facility, comprises the following steps:
A, fuel and alkali liquor are proportionally added in emulsator, according to a certain percentage through being sufficiently stirred for emulsifying, prepare oil-water emulsion;Described fuel is 1:9 ~ 9:1 with the ratio of alkali liquor;
B, joining in scrubbing tower by emulsion through the export pipeline of emulsator, ON cycle pump is circulated washing;
C, opening air-introduced machine, carry out blended absorbent with oil-water emulsion in the organic volatile that batch mixing pond produces being delivered to scrubbing tower by air-introduced machine, the gas after absorption cleaning is through delivering to rotary kiln communicating pipe or being discharged in Factory Building;
D, liquid after absorption cleaning deliver to the entrance of burner through circulating pump after returning to emulsator.
Wherein, described fuel is natural gas, diesel oil, tire oil or heavy oil, and described alkali liquor is sodium hydroxide, potassium hydroxide or carbamide.
Present invention preferably employs following technological parameter, first, during configuration emulsion, in emulsator, add 500Kg 200# heavy oil, in emulsator, secondly add 200KgNaOH(30%) solution, in emulsator, again add 300Kg water and 1Kg emulsifying agent, stirring and emulsifying 1h;
Through it was verified that open the normal broken material of disintegrating machine, normal batch mixing feeding in batch mixing pond, on-the-spot smelling the odour and measurement VOC concentration, on-the-spot tanginess, dust is obvious, VOC local concentration 400mg/m3.The emulsion that emulsifying is good is added in circulating absorption tower, ON cycle pump, control circulating load 15m3/h, ON cycle blower fan (design air flow 4000m3/h), on-the-spot abnormal smells from the patient is obviously improved, VOC local concentration 40mg/ m3Dust Capacity is decreased obviously;After running 48h, detect absorption tower aerofluxus VOC concentration, 15mg/m3.By absorption liquid pump to burner, flame is normal, and Control for Kiln Temperature is normal.
Claims (5)
1. a hazardous waste waste gas disposal facility, including the batch mixing pond (2) arranged in Factory Building (1), the gas outlet of described batch mixing pond (2) connects scrubbing tower (4) by outlet pipe (3), it is characterized in that: air-introduced machine (5) is installed on described outlet pipe (3), the bottom side of described scrubbing tower (4) is provided with emulsator (6), the export pipeline of described emulsator (6) is connected to entrance and the top of scrubbing tower (4) of burner (8) after a circulating pump (7), the top exit of described scrubbing tower (4) is by respectively leading in rotary kiln (9) and Factory Building (1) communicating pipe.
2. according to the hazardous waste waste gas disposing technique described in claim 1 and equipment, it is characterized in that: described batch mixing pond (2) be provided above disintegrating machine (10), being provided with feed well (11) between the open top of described disintegrating machine (10) and batch mixing pond (2), the top of described disintegrating machine (10) is provided with feed hopper (12).
3. the hazardous waste waste gas disposing technique using hazardous waste waste gas disposal facility described in claim 1, it is characterised in that: comprise the following steps:
A, fuel and alkali liquor are proportionally added in emulsator, through being sufficiently stirred for emulsifying, prepare oil-water emulsion;
B, joining in scrubbing tower by emulsion through the export pipeline of emulsator, ON cycle pump is circulated washing;
C, opening air-introduced machine, carry out blended absorbent with oil-water emulsion in the organic volatile that batch mixing pond produces being delivered to scrubbing tower by air-introduced machine, the gas after absorption cleaning is through delivering to rotary kiln communicating pipe or being discharged in Factory Building;
D, liquid after absorption cleaning deliver to the entrance of burner through circulating pump after returning to emulsator.
4. according to the hazardous waste waste gas disposing technique described in claim 1, it is characterised in that: described fuel is 1:9 ~ 9:1 with the ratio of alkali liquor.
5. according to the hazardous waste waste gas disposing technique described in claim 1, it is characterised in that: described fuel is natural gas, diesel oil, tire oil or heavy oil, and described alkali liquor is sodium hydroxide, potassium hydroxide or carbamide.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
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CN201610434994.7A CN105972629A (en) | 2016-06-17 | 2016-06-17 | Hazardous waste and waste gas treatment equipment and technology |
Applications Claiming Priority (1)
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CN201610434994.7A CN105972629A (en) | 2016-06-17 | 2016-06-17 | Hazardous waste and waste gas treatment equipment and technology |
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CN105972629A true CN105972629A (en) | 2016-09-28 |
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CN201610434994.7A Pending CN105972629A (en) | 2016-06-17 | 2016-06-17 | Hazardous waste and waste gas treatment equipment and technology |
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Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN110170498A (en) * | 2019-06-04 | 2019-08-27 | 仙居卡贝环保科技有限公司 | A kind of danger wastes security landfill device |
CN114832921A (en) * | 2022-05-30 | 2022-08-02 | 镇江新宇固体废物处置有限公司 | Hazardous waste pretreatment system based on nitrogen protection |
Citations (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN2553255Y (en) * | 2002-07-01 | 2003-05-28 | 曹炳银 | Production equipment for environmental protection clean fuel oil |
CN103170217A (en) * | 2013-04-03 | 2013-06-26 | 李竑 | Method for purifying benzene containing waste gas and recycling benzene and system thereof |
CN103537171A (en) * | 2013-10-30 | 2014-01-29 | 许征 | Emulsified liquid for processing organic waste gas, device for processing organic waste gas and method for processing organic waste gas |
CN104988537A (en) * | 2015-06-12 | 2015-10-21 | 江西金铂铼资源循环新技术有限公司 | Wet process dust collecting and leaching electrodeposition integrated technology for zinc-contained solid waste disposal |
CN105132116A (en) * | 2015-07-21 | 2015-12-09 | 朱明� | High thermal-energy fuel or diesel additive and preparation method thereof |
CN206018686U (en) * | 2016-06-17 | 2017-03-15 | 镇江新宇固体废物处置有限公司 | A kind of hazardous waste waste gas disposal facility |
-
2016
- 2016-06-17 CN CN201610434994.7A patent/CN105972629A/en active Pending
Patent Citations (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN2553255Y (en) * | 2002-07-01 | 2003-05-28 | 曹炳银 | Production equipment for environmental protection clean fuel oil |
CN103170217A (en) * | 2013-04-03 | 2013-06-26 | 李竑 | Method for purifying benzene containing waste gas and recycling benzene and system thereof |
CN103537171A (en) * | 2013-10-30 | 2014-01-29 | 许征 | Emulsified liquid for processing organic waste gas, device for processing organic waste gas and method for processing organic waste gas |
CN104988537A (en) * | 2015-06-12 | 2015-10-21 | 江西金铂铼资源循环新技术有限公司 | Wet process dust collecting and leaching electrodeposition integrated technology for zinc-contained solid waste disposal |
CN105132116A (en) * | 2015-07-21 | 2015-12-09 | 朱明� | High thermal-energy fuel or diesel additive and preparation method thereof |
CN206018686U (en) * | 2016-06-17 | 2017-03-15 | 镇江新宇固体废物处置有限公司 | A kind of hazardous waste waste gas disposal facility |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN110170498A (en) * | 2019-06-04 | 2019-08-27 | 仙居卡贝环保科技有限公司 | A kind of danger wastes security landfill device |
CN114832921A (en) * | 2022-05-30 | 2022-08-02 | 镇江新宇固体废物处置有限公司 | Hazardous waste pretreatment system based on nitrogen protection |
CN114832921B (en) * | 2022-05-30 | 2023-09-01 | 镇江新宇固体废物处置有限公司 | Dangerous waste pretreatment system based on nitrogen protection |
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Application publication date: 20160928 |
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