CN110102165B - Method for preparing deodorant from landfill leachate concentrated solution - Google Patents
Method for preparing deodorant from landfill leachate concentrated solution Download PDFInfo
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- CN110102165B CN110102165B CN201910356463.4A CN201910356463A CN110102165B CN 110102165 B CN110102165 B CN 110102165B CN 201910356463 A CN201910356463 A CN 201910356463A CN 110102165 B CN110102165 B CN 110102165B
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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
- B01D53/52—Hydrogen sulfide
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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
- B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
- B01D53/77—Liquid phase processes
- B01D53/78—Liquid phase processes with gas-liquid contact
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F9/00—Multistage treatment of water, waste water or sewage
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
- C02F1/5236—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/66—Treatment of water, waste water, or sewage by neutralisation; pH adjustment
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/72—Treatment of water, waste water, or sewage by oxidation
- C02F1/722—Oxidation by peroxides
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/72—Treatment of water, waste water, or sewage by oxidation
- C02F1/76—Treatment of water, waste water, or sewage by oxidation with halogens or compounds of halogens
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/06—Contaminated groundwater or leachate
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2303/00—Specific treatment goals
- C02F2303/02—Odour removal or prevention of malodour
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- Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- Environmental & Geological Engineering (AREA)
- Analytical Chemistry (AREA)
- Health & Medical Sciences (AREA)
- Biomedical Technology (AREA)
- General Chemical & Material Sciences (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Water Supply & Treatment (AREA)
- Hydrology & Water Resources (AREA)
- Organic Chemistry (AREA)
- Life Sciences & Earth Sciences (AREA)
- Disinfection, Sterilisation Or Deodorisation Of Air (AREA)
- Treating Waste Gases (AREA)
Abstract
The invention relates to a method for preparing deodorant from landfill leachate concentrated solution, which comprises the steps of firstly adding coagulant into the landfill leachate concentrated solution to remove macromolecular organic matters, then adding oxidant into the obtained solution to carry out advanced oxidation to remove micromolecular organic matters and odor, then adding acid to react to prepare the oxidant, and preparing the deodorant containing Cl2And ClO2A composite air deodorant of solution. Compared with the prior art, the invention not only can effectively treat the concentrated solution, but also can convert the concentrated solution into the oxidation deodorant which is effective to the odor.
Description
Technical Field
The invention belongs to the technical field of environmental protection and energy conservation, and relates to a method for preparing a deodorant from a landfill leachate concentrated solution.
Background
The concentration treatment of the landfill leachate mainly adopts a method combining a membrane technology and biochemical treatment, 15-30% of concentrated solution is generated by the liquid membrane treatment of the landfill leachate, and the concentrated solution contains about 5% of sodium chloride, macromolecular humic acid and strong odor. The high concentration of contaminants and the low biodegradability of the concentrate make it a potential source of pollution with a strong destructive power to the environment. The treatment mode of the garbage percolate concentrated solution mainly comprises three methods of recharging, burning or evaporating treatment. Recharge will probably cause groundwater pollution and will result in effluent COD, conductivity and NH4+、Cl-Etc. The evaporation or incineration method has the problems of high requirement on energy sources (biogas or steam sources), high equipment investment and high maintenance cost, and high concentration humic acid and high hardness in the concentrated solution can cause evaporation coking and scaling.
Disclosure of Invention
The invention aims to provide a method for preparing a deodorant from a landfill leachate concentrated solution, aiming at solving the problem that the method for preparing the deodorant from the landfill concentrated solution is difficult.
The purpose of the invention can be realized by the following technical scheme:
a process for preparing deodoriser from the concentrated garbage percolate includes adding coagulant to the concentrated garbage percolate to remove the macromolecular organic substances (humic acid, etc), adding oxidant to the solution for high-grade oxidization to remove the micromolecular organic substances and odour, adding acid and reacting to obtain oxidant2And ClO2A composite air deodorant of solution.
Preferably, the coagulant is an iron salt coagulant comprising FeSO4Or FeCl3。
Preferably, the dry weight of the coagulant added in each 1L of the landfill leachate concentrated solution is 5-60 g, and solid-liquid separation is carried out after precipitation for 30-60 min after coagulation.
Preferably, the coagulant can be prepared into a 10-30 wt% solution and added in the form of a solution.
Preferably, the oxidant is H2O2Or Na2S2O8。
Preferably, 10-50g of oxidizing agent (active ingredient) is added per 1L of solution.
Preferably, the acid is sulfuric acid or hydrochloric acid,
preferably, the pH is adjusted to 1-2 by adding acid.
Preferably, the reaction to produce an oxidizing agent comprises H2O2、NaClO2、NaClO3Or NaClO4。
Preferably, 60-160 g of the reaction preparation oxidant is added into each 1L of the solution.
Compared with the prior art, the invention adopts the combined process of coagulation, advanced oxidation and preparation, firstly removes macromolecular organic matters such as humic acid and the like by adopting a coagulation method, removes micromolecular organic matters and odor by adopting an advanced oxidation technology, and then adds acid and an oxidizing agent to prepare the Cl-containing material2And ClO2A compound air deodorant of a solution; the method not only can effectively treat the concentrated solution, but also can convert the concentrated solution into an oxidation deodorant which is effective on odor.
Detailed Description
The present invention will be described in detail with reference to specific examples.
Example 1
Firstly, 5g FeCl is added into 1L of concentrated solution3Removing macromolecular organic matters such as humic acid and the like (by dry weight), adding a coagulant in the form of 10 wt% solution, and precipitating for 30min after coagulation for solid-liquid separation; adding 50gH into each 1L of the solution2O2(181g content: 27.5%) is subjected to advanced oxidation to remove small molecular organic substances and odor, hydrochloric acid is added to pH 1, and 27.5g H is added to 1L solution2O2(100g content 27.5%) and 132.5g NaClO3(133.2g content 99.5%) reaction to prepare an oxidizing agent to prepare a solution containing 9-12% Cl2And ClO2A composite air deodorant of solution. Can be diluted by 10 times and sprayed at 60m3The room atomizing sprays 100mL of diluent, and after 5min, the concentration of the indoor hydrogen sulfide can be from 80mg/m3Reduced to 10mg/m3The following.
Example 2
Firstly, 60g of FeSO is added into every 1L of concentrated solution4Removing macromolecular organic matters such as humic acid and the like (by dry weight), adding a coagulant in the form of a 30 wt% solution, and precipitating for 60min after coagulation for solid-liquid separation; 50g of Na is added into each 1L of the solution2S2O8(51g content 98.5%) to remove small molecular organic matter and odor, adding sulfuric acid to pH 2, and adding 60g NaClO to 1L solution3(60g content: 99.5%) to prepare a solution containing 5% Cl2And ClO2A composite air deodorant of solution. Can be diluted by 5 times and sprayed at 60m3The room is atomized and sprayed with 120mL of diluent, and after 5min, the concentration of the indoor hydrogen sulfide can be 40mg/m3Reduced to 10mg/m3The following.
Example 3
Firstly, 60g of FeSO is added into every 1L of concentrated solution4Removing macromolecular organic matters such as humic acid and the like (by dry weight), adding a coagulant in the form of a 30 wt% solution, and precipitating for 60min after coagulation for solid-liquid separation; 10g H was added to each 1L of the solution2O2(36.4g content: 27.5%) was subjected to advanced oxidation to remove small molecular organic substances and odors, sulfuric acid was added to pH 1, and 60g of NaClO was added to 1L of the solution2(75g content: 80%) to give a solution containing 4-5% Cl2And ClO2A composite air deodorant of solution. Can be diluted by 5 times and sprayed at 60m3The room atomizing sprays 200mL of diluent, and after 5min, the concentration of the indoor hydrogen sulfide can be from 30mg/m3Reduced to 10mg/m3The following.
Examples 1 to 3 were carried out by the following series of reactions,
NaClO3+NaCl+H2SO4=ClO2+1/2C12+Na2SO4+H2O;
sodium chlorate is added to react with salt in water to generate Cl2And ClO2(example 2);
under the condition of acidity, the water-soluble organic acid,
5NaClO2+4HCl=4ClO2+5NaCl+2H2O;
adding sodium chlorite to react with chlorine ion in water to produce ClO2(example 3);
2HClO3+H2O2=2ClO2+O2+2H2O;
sodium chlorate is added to be converted into chloric acid under the acidic condition, and the chloric acid is further reacted with hydrogen peroxide to generate ClO2(example 1).
In which Cl is formed2And ClO2Has remarkable functions of deodorization and air purification.
Example 4
This example is essentially the same as example 1, except that in this example 40g of FeSO per 1L of concentrate was added4(on a dry weight basis).
Example 5
This example is substantially the same as example 1, except that in this example, solid-liquid separation was carried out by precipitation for 45min after coagulation.
Example 6
This example is substantially the same as example 1, except that in this example, 30gH was added to 1L of the solution2O2(109g content: 27.5%) was subjected to advanced oxidation to remove small molecular organic substances and odors.
Example 6
This example is essentially the same as example 1 except that in this example, 100g of NaClO was added as the reaction-producing oxidizing agent4(active ingredient).
The embodiments described above are intended to facilitate the understanding and use of the invention by those skilled in the art. It will be readily apparent to those skilled in the art that various modifications to these embodiments may be made, and the generic principles described herein may be applied to other embodiments without the use of the inventive faculty. Therefore, the present invention is not limited to the above embodiments, and those skilled in the art should make improvements and modifications within the scope of the present invention based on the disclosure of the present invention.
Claims (5)
1. A process for preparing deodoriser from the concentrated garbage percolate includes such steps as adding coagulant to said concentrated garbage percolate to remove macromolecular organic substance, adding oxidant to the solution, high-grade oxidizing to remove micromolecular organic substance and odour, adding acid, and reacting to obtain the deodoriser2And ClO2A composite air deodorant of solution; the reaction for preparing the oxidant comprises H2O2、NaClO2、NaClO3Or NaClO4;
Adding 10-50g of oxidant into every 1L of solution;
the oxidant is H2O2Or Na2S2O8;
Adding acid to adjust the pH value to 1-2.
2. The method for preparing deodorant according to claim 1, wherein the coagulant is iron salt coagulant including FeSO coagulant4Or FeCl3。
3. The method for preparing a deodorant according to claim 1 or 2, wherein the dry weight of coagulant added per 1L of landfill leachate concentrate is 5-60 g, and solid-liquid separation is performed after 30-60 min of precipitation after coagulation.
4. The method of claim 1, wherein the acid is sulfuric acid or hydrochloric acid.
5. The method for preparing a deodorant according to claim 1, wherein 60-160 g of the reaction preparation oxidant is added to 1L of the solution.
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CN111718040A (en) * | 2020-06-09 | 2020-09-29 | 上海老港废弃物处置有限公司 | Method for preparing deodorant by electrolyzing concentrated solution of nanofiltration percolate of garbage |
EP4271659A1 (en) * | 2020-12-29 | 2023-11-08 | Ecolab Usa Inc. | Method for controlling odor and taste producing metabolites in water systems through use of primary and secondary oxidation processes |
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CN103402621A (en) * | 2010-12-23 | 2013-11-20 | A.P.F.液化系统股份公司 | Method for producing an aqueous stable chlorine dioxide solution |
CN105692986A (en) * | 2014-11-24 | 2016-06-22 | 中国石油化工股份有限公司 | Waste salt comprehensive utilization processing method |
CN108439342A (en) * | 2018-06-14 | 2018-08-24 | 四川蒙顶山化工有限公司 | A method of preparing disinfection agent of chlorine dioxide |
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CN108975552A (en) * | 2018-08-01 | 2018-12-11 | 西南交通大学 | A kind of processing method of landfill leachate |
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US6755973B2 (en) * | 2002-04-04 | 2004-06-29 | Water Solutions Inc. | Waste water treatment process for animal processing contaminant removal |
KR20160098989A (en) * | 2016-03-07 | 2016-08-19 | (주)삼원이앤이 | Treatment System of Food Waste Leachate Capable of Deodoring and Highly Concentration with High Solubility |
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Patent Citations (5)
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CN103402621A (en) * | 2010-12-23 | 2013-11-20 | A.P.F.液化系统股份公司 | Method for producing an aqueous stable chlorine dioxide solution |
CN105692986A (en) * | 2014-11-24 | 2016-06-22 | 中国石油化工股份有限公司 | Waste salt comprehensive utilization processing method |
CN108793588A (en) * | 2018-05-25 | 2018-11-13 | 中节能工程技术研究院有限公司 | A kind of percolate treatment processing method based on advanced oxidation group technology |
CN108439342A (en) * | 2018-06-14 | 2018-08-24 | 四川蒙顶山化工有限公司 | A method of preparing disinfection agent of chlorine dioxide |
CN108975552A (en) * | 2018-08-01 | 2018-12-11 | 西南交通大学 | A kind of processing method of landfill leachate |
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