WO2018120051A1 - Waste incineration fly ash stabilizing agent and preparation method therefor - Google Patents
Waste incineration fly ash stabilizing agent and preparation method therefor Download PDFInfo
- Publication number
- WO2018120051A1 WO2018120051A1 PCT/CN2016/113579 CN2016113579W WO2018120051A1 WO 2018120051 A1 WO2018120051 A1 WO 2018120051A1 CN 2016113579 W CN2016113579 W CN 2016113579W WO 2018120051 A1 WO2018120051 A1 WO 2018120051A1
- Authority
- WO
- WIPO (PCT)
- Prior art keywords
- fly ash
- polyferric
- waste incineration
- incineration fly
- dihydrogen phosphate
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Ceased
Links
Classifications
-
- A—HUMAN NECESSITIES
- A62—LIFE-SAVING; FIRE-FIGHTING
- A62D—CHEMICAL MEANS FOR EXTINGUISHING FIRES OR FOR COMBATING OR PROTECTING AGAINST HARMFUL CHEMICAL AGENTS; CHEMICAL MATERIALS FOR USE IN BREATHING APPARATUS
- A62D3/00—Processes for making harmful chemical substances harmless or less harmful, by effecting a chemical change in the substances
- A62D3/30—Processes for making harmful chemical substances harmless or less harmful, by effecting a chemical change in the substances by reacting with chemical agents
- A62D3/33—Processes for making harmful chemical substances harmless or less harmful, by effecting a chemical change in the substances by reacting with chemical agents by chemical fixing the harmful substance, e.g. by chelation or complexation
Definitions
- the invention relates to a waste incineration fly ash treatment medicament, in particular to a waste incineration fly ash stabilization medicament and a preparation method thereof.
- Waste incineration treatment technology has been widely used at home and abroad because of its advantages in resource reduction and reduction.
- Municipal solid waste incineration will produce incineration fly ash equivalent to 2% to 5% of the original waste quality.
- Fly ash contains water-soluble Cd, Pb, Zn, Cu, Cr and other harmful heavy metal substances.
- the list of hazardous wastes in China has clearly classified waste incineration fly ash as hazardous waste (No. HW18), which requires passivation and stabilization.
- Special treatments such as chemical treatment, in order to meet the requirements of the heavy metal leaching concentration value in the Domestic Waste Landfill Pollution Control Standard (GB16889-2008), can only enter the landfill for safe disposal.
- the treatment methods of waste incineration fly ash mainly include chemical stabilization method, melting/glass solidification, cement solidification, acid or other solvent elution method, and safe landfill.
- the chemical stabilization method mainly uses a chemical agent to chemically react with harmful substances in fly ash to convert it into a process of low solubility, low migration and low toxicity.
- the chemical stabilization method has become a commonly used treatment method at home and abroad because of its simple operation and quick effect. However, it also has problems such as high treatment cost and unstable treatment effect, and there is a risk of secondary pollution.
- the present invention provides a waste incineration fly ash stabilization agent, and a method for preparing the above-mentioned waste incineration fly ash stabilization agent, a waste incineration fly ash stabilization agent, which is composed of potassium dihydrogen phosphate and polysilicon
- the above preparation method of the waste incineration fly ash stabilization agent comprises the following steps:
- the particle size of the polymeric calcium silicate sulfate is not more than 0.2 mm;
- the particle size of the polyferric chloride is not more than 0.15 mm;
- the particle size of the sea foam is not more than 0.1 mm.
- the ground polysilicate ferric sulfate, polyferric chloride and sea foam are added to the potassium dihydrogen phosphate and stirred uniformly to form a waste incineration fly ash stabilization agent.
- the application of the above-mentioned waste incineration fly ash stabilization agent includes the following steps:
- stirred chelate (treated fly ash) is bagged and numbered, and after 24 hours of curing, it is sent to the landfill for landfill.
- a waste incineration fly ash stabilization agent consisting of potassium dihydrogen phosphate, polyferric sulfate, polyferric chloride, sea foam, and components by weight The contents are: potassium dihydrogen phosphate 40-50%, polymeric ferric sulfate 20-30%, polyferric chloride 20-30%, sea foam mud 5-10%; a waste incineration fly ash stabilization agent
- the preparation method comprises the following steps:
- potassium dihydrogen phosphate, polyferric sulfate ferric sulfate, polyferric chloride, and sea foam are weighed separately.
- the contents of each component by weight are: potassium dihydrogen phosphate 40-50%, polymeric silicic acid sulfuric acid 20-30% iron, 20-30% polyferric chloride, 5-10% sea foam mud;
- the polyferric silicate sulfate, the polyferric chloride, and the sea foam are uniformly ground;
- the particle size of the polymeric calcium silicate sulfate is not more than 0.2 mm;
- the particle size of the polyferric chloride is not more than 0.15 mm;
- the particle size of the sea foam is not more than 0.1 mm.
- the ground polysilicate ferric silicate, the polyferric chloride and the sea foam are added to the potassium dihydrogen phosphate and stirred uniformly to form a waste incineration fly ash stabilization agent.
- the invention has the beneficial effects that the composition of the waste incineration fly ash stabilizing agent of the invention is reasonable, and the components can cooperate synergistically, and the plurality of solidifications such as adsorption, complexation reaction and precipitation reaction of the mineral lattice are utilized.
- the mechanism can permanently and effectively stabilize the heavy metals in the fly ash.
- the treated fly ash can meet the entry requirements of the Domestic Waste Landfill Pollution Control Standard (GB16889-2008); in addition, the stabilized chemical is inexpensive.
- the preparation and application process are simple, the operability is strong, and it is suitable for wide-ranging application.
- a waste incineration fly ash stabilization agent the components and percentages thereof are as follows:
- the preparation method of the above-mentioned waste incineration fly ash stabilization agent is as follows:
- the polyferric sulfate ferric sulfate is ground, and after pulverization, a sieve of 0.2 mm is used, and used;
- the polyferric chloride is ground, crushed and passed through a 0.15 mm sieve, and used;
- the sea foam mud is ground, crushed and passed through a 0.1 mm sieve, and used;
- the raw material after the grinding in step 2 is added to potassium dihydrogen phosphate and then stirred uniformly to form a waste incineration fly ash stabilization agent.
- waste incineration fly ash stabilization agent Take 5kg of fly ash from a waste incineration power plant in Shenzhen, add 1kg of waste incineration fly ash stabilization agent of the invention, stir evenly, add 0.75kg of water and continue stirring for 120 seconds until uniform.
- the treated fly ash (chelate) is bagged and numbered.
- the numbering method is: year + month + day + production batch format, this time number is 2016-10-12-001. Samples were taken after 24 hours of curing.
- the unit is mg/L
- a waste incineration fly ash stabilization agent the components and percentages thereof are as follows:
- the above-mentioned waste incineration fly ash stabilizing agent is prepared in the same manner as in the first embodiment.
- waste incineration fly ash stabilization agent Take 10kg of fly ash from a waste incineration power plant in Wuhan, add 2.5kg of waste incineration fly ash stabilization agent of the invention, stir evenly, add 1.5kg of water and continue stirring for 120 seconds until uniform.
- the treated fly ash (chelate) is bagged and numbered.
- the numbering method is: year + month + day + production batch format, this time number is 2016-10-15-001. Samples were taken after 24 hours of curing.
- the detection items and methods are the same as in the first embodiment.
- the unit is mg/L
Landscapes
- Health & Medical Sciences (AREA)
- General Health & Medical Sciences (AREA)
- Toxicology (AREA)
- Chemical & Material Sciences (AREA)
- Chemical Kinetics & Catalysis (AREA)
- General Chemical & Material Sciences (AREA)
- Business, Economics & Management (AREA)
- Emergency Management (AREA)
- Processing Of Solid Wastes (AREA)
Abstract
Description
本发明涉及一种垃圾焚烧飞灰处理药剂,尤其是涉及一种垃圾焚烧飞灰稳定化药剂及其制备方法。The invention relates to a waste incineration fly ash treatment medicament, in particular to a waste incineration fly ash stabilization medicament and a preparation method thereof.
目前,随着城市化进程不断加快,城市生活垃圾量急剧增加,且增长势头不减,垃圾围城压力越来越大,所产生的环境与社会问题,已成为制约城市发展的瓶颈之一。垃圾焚烧处理技术由于其在资源化和减量化上的优势,在国内外得到了广泛的应用,但城市生活垃圾焚烧后会产生相当于原垃圾质量2%~5%的焚烧飞灰。飞灰中含有水溶性的Cd、Pb、Zn、Cu、Cr等多种有害重金属物质,我国危险废物名录已明确将垃圾焚烧飞灰列为危险废物(编号HW18),要求必须经过钝化、稳定化等特殊处理,满足《生活垃圾填埋场污染控制标准》(GB16889-2008)中对于重金属浸出浓度值的要求后,才能进入填埋场进行安全处置。At present, with the accelerating urbanization process, the amount of urban domestic waste has increased sharply, and the growth momentum has not decreased. The pressure on the garbage surrounding city has become larger and larger, and the environmental and social problems have become one of the bottlenecks restricting urban development. Waste incineration treatment technology has been widely used at home and abroad because of its advantages in resource reduction and reduction. However, municipal solid waste incineration will produce incineration fly ash equivalent to 2% to 5% of the original waste quality. Fly ash contains water-soluble Cd, Pb, Zn, Cu, Cr and other harmful heavy metal substances. The list of hazardous wastes in China has clearly classified waste incineration fly ash as hazardous waste (No. HW18), which requires passivation and stabilization. Special treatments such as chemical treatment, in order to meet the requirements of the heavy metal leaching concentration value in the Domestic Waste Landfill Pollution Control Standard (GB16889-2008), can only enter the landfill for safe disposal.
垃圾焚烧飞灰的处理方法主要有:化学稳定法、熔融/玻璃固化、水泥固化、酸或其它溶剂洗提法、安全填埋等。化学稳定法主要是利用化学药剂与飞灰中的有害物质发生化学反应,使其转化为低溶解性、低迁移性及低毒性物质的过程。化学稳定法因其具有操作简单、处理效果见效快等特点,已成为国内外较普遍采用的处理方法,但其也存在处理成本高、处理效果不稳定等问题,存在二次污染的风险。The treatment methods of waste incineration fly ash mainly include chemical stabilization method, melting/glass solidification, cement solidification, acid or other solvent elution method, and safe landfill. The chemical stabilization method mainly uses a chemical agent to chemically react with harmful substances in fly ash to convert it into a process of low solubility, low migration and low toxicity. The chemical stabilization method has become a commonly used treatment method at home and abroad because of its simple operation and quick effect. However, it also has problems such as high treatment cost and unstable treatment effect, and there is a risk of secondary pollution.
发明内容Summary of the invention
为了解决上述问题,本发明提供一种垃圾焚烧飞灰稳定化药剂,同时提供上述垃圾焚烧飞灰稳定化药剂的制备方法,一种垃圾焚烧飞灰稳定化药剂,由磷酸二氢钾、聚合硅酸硫酸铁、聚合氯化铁、海泡泥组成,以重量计各成分的含量分别为:磷酸二氢钾40-50%、聚合硅酸硫酸铁20-30%、聚合氯化铁20-30%、海泡泥5-10%;上述的垃圾焚烧飞灰稳定化药剂的制备方法,包括如下步骤:In order to solve the above problems, the present invention provides a waste incineration fly ash stabilization agent, and a method for preparing the above-mentioned waste incineration fly ash stabilization agent, a waste incineration fly ash stabilization agent, which is composed of potassium dihydrogen phosphate and polysilicon The composition of acid ferric sulfate, polyferric chloride and sea foam mud, the content of each component by weight: potassium dihydrogen phosphate 40-50%, polymeric ferric sulfate 20-30%, polyferric chloride 20-30 %, sea foam mud 5-10%; the above preparation method of the waste incineration fly ash stabilization agent comprises the following steps:
1、按上述重量百分比分别称取各原料;1. Weigh each raw material according to the above weight percentage;
2、将聚合硅酸硫酸铁、聚合氯化铁、海泡泥研磨均匀;2. Grinding polyaluminum silicate sulfate, polyferric chloride and sea foam mud evenly;
进一步地,聚合硅酸硫酸铁粒径不大于0.2mm;Further, the particle size of the polymeric calcium silicate sulfate is not more than 0.2 mm;
进一步地,聚合氯化铁粒径不大于0.15mm;Further, the particle size of the polyferric chloride is not more than 0.15 mm;
进一步地,海泡泥粒径不大于0.1mm。Further, the particle size of the sea foam is not more than 0.1 mm.
3、将研磨后的聚合硅酸硫酸铁、聚合氯化铁、海泡泥加入到磷酸二氢钾中搅拌均匀,即制成垃圾焚烧飞灰稳定化药剂。3. The ground polysilicate ferric sulfate, polyferric chloride and sea foam are added to the potassium dihydrogen phosphate and stirred uniformly to form a waste incineration fly ash stabilization agent.
上述垃圾焚烧飞灰稳定化药剂的应用,包括如下步骤:The application of the above-mentioned waste incineration fly ash stabilization agent includes the following steps:
(1)将飞灰输送至搅拌机; (1) conveying the fly ash to the mixer;
(2)在飞灰输送完后,将药剂输送至搅拌机,干搅拌至均匀;(2) After the fly ash is delivered, the agent is delivered to the mixer and dryly stirred until uniform;
(3)加水继续搅拌至均匀;(3) adding water and stirring until uniform;
(4)搅拌后的螯合物(处理后的飞灰)装袋并编号,养护24h之后送填埋场填埋。(4) The stirred chelate (treated fly ash) is bagged and numbered, and after 24 hours of curing, it is sent to the landfill for landfill.
本发明解决其技术问题所采用的技术方案是:一种垃圾焚烧飞灰稳定化药剂,由磷酸二氢钾、聚合硅酸硫酸铁、聚合氯化铁、海泡泥组成,以重量计各成分的含量分别为:磷酸二氢钾40-50%、聚合硅酸硫酸铁20-30%、聚合氯化铁20-30%、海泡泥5-10%;一种垃圾焚烧飞灰稳定化药剂的制备方法,包括如下步骤:The technical solution adopted by the invention to solve the technical problem is: a waste incineration fly ash stabilization agent, consisting of potassium dihydrogen phosphate, polyferric sulfate, polyferric chloride, sea foam, and components by weight The contents are: potassium dihydrogen phosphate 40-50%, polymeric ferric sulfate 20-30%, polyferric chloride 20-30%, sea foam mud 5-10%; a waste incineration fly ash stabilization agent The preparation method comprises the following steps:
第一步、分别称取磷酸二氢钾、聚合硅酸硫酸铁、聚合氯化铁、海泡泥,以重量计各成分的含量分别为:磷酸二氢钾40-50%、聚合硅酸硫酸铁20-30%、聚合氯化铁20-30%、海泡泥5-10%;In the first step, potassium dihydrogen phosphate, polyferric sulfate ferric sulfate, polyferric chloride, and sea foam are weighed separately. The contents of each component by weight are: potassium dihydrogen phosphate 40-50%, polymeric silicic acid sulfuric acid 20-30% iron, 20-30% polyferric chloride, 5-10% sea foam mud;
第二步、将聚合硅酸硫酸铁、聚合氯化铁、海泡泥研磨均匀;In the second step, the polyferric silicate sulfate, the polyferric chloride, and the sea foam are uniformly ground;
进一步地,聚合硅酸硫酸铁粒径不大于0.2mm;Further, the particle size of the polymeric calcium silicate sulfate is not more than 0.2 mm;
进一步地,聚合氯化铁粒径不大于0.15mm;Further, the particle size of the polyferric chloride is not more than 0.15 mm;
进一步地,海泡泥粒径不大于0.1mm。Further, the particle size of the sea foam is not more than 0.1 mm.
第三步、将研磨后的聚合硅酸硫酸铁、聚合氯化铁、海泡泥加入到磷酸二氢钾中搅拌均匀,即制成垃圾焚烧飞灰稳定化药剂。In the third step, the ground polysilicate ferric silicate, the polyferric chloride and the sea foam are added to the potassium dihydrogen phosphate and stirred uniformly to form a waste incineration fly ash stabilization agent.
本发明的有益效果:本发明所述垃圾焚烧飞灰稳定化药剂的成分搭配合理,各组分能够协同发挥作用,利用矿物质晶格层间吸附、络合反应、沉淀反应等多种固化稳定机理,能够长久、有效的稳定化飞灰中的重金属,经处理后的飞灰能够满足《生活垃圾填埋场污染控制标准》(GB16889-2008)的入场要求;此外该稳定化药剂价格低廉,制备和应用工艺简单,可操作性强,适于大范围推广应用。The invention has the beneficial effects that the composition of the waste incineration fly ash stabilizing agent of the invention is reasonable, and the components can cooperate synergistically, and the plurality of solidifications such as adsorption, complexation reaction and precipitation reaction of the mineral lattice are utilized. The mechanism can permanently and effectively stabilize the heavy metals in the fly ash. The treated fly ash can meet the entry requirements of the Domestic Waste Landfill Pollution Control Standard (GB16889-2008); in addition, the stabilized chemical is inexpensive. The preparation and application process are simple, the operability is strong, and it is suitable for wide-ranging application.
实施例一Embodiment 1
一种垃圾焚烧飞灰稳定化药剂,各成分及其含量百分比如下:A waste incineration fly ash stabilization agent, the components and percentages thereof are as follows:
上述垃圾焚烧飞灰稳定化药剂的制备方法如下:The preparation method of the above-mentioned waste incineration fly ash stabilization agent is as follows:
第一步、按上表中的重量百分比分别称取各原料; In the first step, weigh each raw material according to the weight percentage in the above table;
第二步、对聚合硅酸硫酸铁进行研磨,粉碎后过0.2mm的筛子,备用;In the second step, the polyferric sulfate ferric sulfate is ground, and after pulverization, a sieve of 0.2 mm is used, and used;
对聚合氯化铁进行研磨,粉碎后过0.15mm的筛子,备用;The polyferric chloride is ground, crushed and passed through a 0.15 mm sieve, and used;
对海泡泥进行研磨,粉碎后过0.1mm的筛子,备用;The sea foam mud is ground, crushed and passed through a 0.1 mm sieve, and used;
第三步、将步骤2中研磨后的原料加入到磷酸二氢钾然后搅拌均匀,即制成垃圾焚烧飞灰稳定化药剂。In the third step, the raw material after the grinding in step 2 is added to potassium dihydrogen phosphate and then stirred uniformly to form a waste incineration fly ash stabilization agent.
垃圾焚烧飞灰稳定化药剂应用实例:取深圳市某垃圾焚烧发电厂飞灰5kg,加入本发明垃圾焚烧飞灰稳定化药剂1kg,搅拌均匀,加入水0.75kg继续搅拌120秒至均匀。处理后的飞灰(螯合物)装袋并编号,编号方法采用:年+月+日+生产批次的格式,此次编号为2016-10-12-001。养护24小时后取样检测。Application example of waste incineration fly ash stabilization agent: Take 5kg of fly ash from a waste incineration power plant in Shenzhen, add 1kg of waste incineration fly ash stabilization agent of the invention, stir evenly, add 0.75kg of water and continue stirring for 120 seconds until uniform. The treated fly ash (chelate) is bagged and numbered. The numbering method is: year + month + day + production batch format, this time number is 2016-10-12-001. Samples were taken after 24 hours of curing.
检测方法:依据《固体废物浸出毒性浸出方法醋酸缓冲溶液法》(HJ/T300-2007)进行浸出毒性实验,《危险废物鉴别标准浸出毒性鉴别》(GB5085.3-2007)测定浸出液的重金属浓度。Detection method: According to the "Solid Waste Leaching Toxicity Leaching Method Acetate Buffer Solution Method" (HJ/T300-2007) for the leaching toxicity test, "Dangerous Waste Identification Standard Leaching Toxicity Identification" (GB5085.3-2007) to determine the heavy metal concentration of the leachate.
试验结果表明,使用本发明垃圾焚烧飞灰稳定化药剂处理后的飞灰能够满足《生活垃圾填埋污染控制标准》(GB16889-2008)的入场要求。The test results show that the fly ash treated by the waste incineration fly ash stabilization agent of the invention can meet the admission requirements of the Domestic Waste Landfill Pollution Control Standard (GB16889-2008).
备注:单位为mg/LRemarks: The unit is mg/L
实施例二Embodiment 2
一种垃圾焚烧飞灰稳定化药剂,各成分及其含量百分比如下:A waste incineration fly ash stabilization agent, the components and percentages thereof are as follows:
上述垃圾焚烧飞灰稳定化药剂,其制备方法与实施例一相同。The above-mentioned waste incineration fly ash stabilizing agent is prepared in the same manner as in the first embodiment.
垃圾焚烧飞灰稳定化药剂应用实例:取武汉市某垃圾焚烧发电厂飞灰10kg,加入本发明垃圾焚烧飞灰稳定化药剂2.5kg,搅拌均匀,加入水1.5kg继续搅拌120秒至均匀。处理后的飞灰(螯合物)装袋并编号,编号方法采用:年+月+日+生产批次的格式,此次编号为2016-10-15-001。养护24小时后取样检测。Application example of waste incineration fly ash stabilization agent: Take 10kg of fly ash from a waste incineration power plant in Wuhan, add 2.5kg of waste incineration fly ash stabilization agent of the invention, stir evenly, add 1.5kg of water and continue stirring for 120 seconds until uniform. The treated fly ash (chelate) is bagged and numbered. The numbering method is: year + month + day + production batch format, this time number is 2016-10-15-001. Samples were taken after 24 hours of curing.
检测项目和方法与实施例一相同。 The detection items and methods are the same as in the first embodiment.
试验结果表明,使用本发明垃圾焚烧飞灰稳定化药剂处理后的飞灰能够满足《生活垃圾填埋污染控制标准》(GB16889-2008)的入场要求。The test results show that the fly ash treated by the waste incineration fly ash stabilization agent of the invention can meet the admission requirements of the Domestic Waste Landfill Pollution Control Standard (GB16889-2008).
备注:单位为mg/L Remarks: The unit is mg/L
Claims (2)
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| PCT/CN2016/113579 WO2018120051A1 (en) | 2016-12-30 | 2016-12-30 | Waste incineration fly ash stabilizing agent and preparation method therefor |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| PCT/CN2016/113579 WO2018120051A1 (en) | 2016-12-30 | 2016-12-30 | Waste incineration fly ash stabilizing agent and preparation method therefor |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| WO2018120051A1 true WO2018120051A1 (en) | 2018-07-05 |
Family
ID=62706700
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| PCT/CN2016/113579 Ceased WO2018120051A1 (en) | 2016-12-30 | 2016-12-30 | Waste incineration fly ash stabilizing agent and preparation method therefor |
Country Status (1)
| Country | Link |
|---|---|
| WO (1) | WO2018120051A1 (en) |
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN113145606A (en) * | 2021-02-25 | 2021-07-23 | 北京旷世达资源环境工程发展中心 | Method for preparing paste slurry for resource utilization of household garbage incineration fly ash |
| CN116409973A (en) * | 2023-04-13 | 2023-07-11 | 常熟理工学院 | A method for harmless disposal of waste incineration fly ash based on nano-modified magnesium silicate cement |
| CN117224888A (en) * | 2023-09-14 | 2023-12-15 | 深圳市泰美瑞环保科技有限公司 | Stabilization treatment process for municipal solid waste incineration fly ash heavy metal |
Citations (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH10118612A (en) * | 1996-10-17 | 1998-05-12 | Nippon Soda Co Ltd | Method for disposing hazardous heavy metal-containing flyash |
| JP2007209829A (en) * | 2005-10-04 | 2007-08-23 | Miyoshi Oil & Fat Co Ltd | Solid waste disposal method |
| WO2009116184A1 (en) * | 2008-03-19 | 2009-09-24 | 株式会社 環境開発 | Method of reclaiming incinerated ash from solidified fuel from refuse, woody biomass fuel, solidified fuel from sludge, etc. as well as other waste and contaminated soil incinerated ash |
| CN102657926A (en) * | 2012-04-13 | 2012-09-12 | 武汉理工大学 | Heavy metal normal temperature curing agent and method for curing heavy metal in heavy metal pollutants by use of heavy metal normal temperature curing agent |
| CN102921142A (en) * | 2012-11-06 | 2013-02-13 | 莱沃睿智绿色科技(北京)有限公司 | Heavy metal pollutant immobilized reagent composition and immobilization treatment method |
| CN102974068A (en) * | 2012-11-22 | 2013-03-20 | 深圳市能源环保有限公司 | Waste incineration fly ash treatment agent |
| CN105110506A (en) * | 2015-08-28 | 2015-12-02 | 浙江省环境保护科学设计研究院 | Acid mine drainage/refuse incineration fly ash coupled stabilization treatment method |
-
2016
- 2016-12-30 WO PCT/CN2016/113579 patent/WO2018120051A1/en not_active Ceased
Patent Citations (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH10118612A (en) * | 1996-10-17 | 1998-05-12 | Nippon Soda Co Ltd | Method for disposing hazardous heavy metal-containing flyash |
| JP2007209829A (en) * | 2005-10-04 | 2007-08-23 | Miyoshi Oil & Fat Co Ltd | Solid waste disposal method |
| WO2009116184A1 (en) * | 2008-03-19 | 2009-09-24 | 株式会社 環境開発 | Method of reclaiming incinerated ash from solidified fuel from refuse, woody biomass fuel, solidified fuel from sludge, etc. as well as other waste and contaminated soil incinerated ash |
| CN102657926A (en) * | 2012-04-13 | 2012-09-12 | 武汉理工大学 | Heavy metal normal temperature curing agent and method for curing heavy metal in heavy metal pollutants by use of heavy metal normal temperature curing agent |
| CN102921142A (en) * | 2012-11-06 | 2013-02-13 | 莱沃睿智绿色科技(北京)有限公司 | Heavy metal pollutant immobilized reagent composition and immobilization treatment method |
| CN102974068A (en) * | 2012-11-22 | 2013-03-20 | 深圳市能源环保有限公司 | Waste incineration fly ash treatment agent |
| CN105110506A (en) * | 2015-08-28 | 2015-12-02 | 浙江省环境保护科学设计研究院 | Acid mine drainage/refuse incineration fly ash coupled stabilization treatment method |
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN113145606A (en) * | 2021-02-25 | 2021-07-23 | 北京旷世达资源环境工程发展中心 | Method for preparing paste slurry for resource utilization of household garbage incineration fly ash |
| CN116409973A (en) * | 2023-04-13 | 2023-07-11 | 常熟理工学院 | A method for harmless disposal of waste incineration fly ash based on nano-modified magnesium silicate cement |
| CN117224888A (en) * | 2023-09-14 | 2023-12-15 | 深圳市泰美瑞环保科技有限公司 | Stabilization treatment process for municipal solid waste incineration fly ash heavy metal |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN104174634B (en) | Stable solidification method of strong-acid arsenic sulfide waste residue | |
| CN108059958B (en) | Antimony-polluted site soil stabilization restoration agent and preparation method thereof | |
| CN105948589B (en) | A kind of method of electroplating sludge harmless treatment | |
| CN105294023A (en) | Method for repairing heavy metal-polluted soil by using red mud granular material | |
| CN104607434B (en) | One way of life incineration of refuse flyash curing | |
| CN105254166B (en) | A kind of dewatered sludge curing agent, preparation method and application method | |
| CN104492024A (en) | Fly ash treatment method for waste incineration | |
| CN107814544A (en) | A kind of curing agent and methods for making and using same for Compound Heavy Metals soil | |
| CN107418582A (en) | A kind of heavy metals immobilization stabilization agent and application method | |
| CN106467745A (en) | It is suitable for the steel slag and desulfurized gypsum base soil-solidified-agent of As polluted soil | |
| CN105880277A (en) | Chromium-contaminated soil remediation method | |
| CN106866066B (en) | Baking-free brick manufactured by treating municipal sludge through special soil stabilizer resource | |
| CN114985413B (en) | Improvement method for realizing harmless treatment of waste incineration fly ash based on magnesium phosphate cement | |
| CN108203271A (en) | Baking-free and steaming-free brick prepared by treating sludge with lead-zinc smelting wastewater and preparation method thereof | |
| CN102718378B (en) | A method for co-processing cement kiln after urban sludge is calcium-increased and passivated | |
| WO2018120051A1 (en) | Waste incineration fly ash stabilizing agent and preparation method therefor | |
| CN108085006A (en) | It is a kind of to be used to repair curing agent of As polluted soil and its preparation method and application | |
| CN104003637A (en) | Method of preparing building material products by carbonating municipal waste incineration ash | |
| CN109453493A (en) | Stabilization agent and its preparation method and application for handling the waste residue containing beryllium | |
| CN102657926A (en) | Heavy metal normal temperature curing agent and method for curing heavy metal in heavy metal pollutants by use of heavy metal normal temperature curing agent | |
| CN109111927B (en) | A kind of heavy metal pollution sand soil curing agent and application method thereof | |
| CN113800941B (en) | A method for preparing ceramsite from chromium-contaminated soil and ceramsite | |
| CN113233824A (en) | Preparation method of tin tailing based low-permeability heavy metal solidified body for underground filling | |
| CN112608044A (en) | Cement kiln co-processing contaminated soil mixed material and preparation method and application thereof | |
| CN107721106A (en) | Utilize the method for acid-soluble oil body refuse processing heavy metal sewage sludge |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| 121 | Ep: the epo has been informed by wipo that ep was designated in this application |
Ref document number: 16925380 Country of ref document: EP Kind code of ref document: A1 |
|
| NENP | Non-entry into the national phase |
Ref country code: DE |
|
| 32PN | Ep: public notification in the ep bulletin as address of the adressee cannot be established |
Free format text: NOTING OF LOSS OF RIGHTS PURSUANT TO RULE 112(1) EPC, (EPO FORM 1205 DATED 25.10.19) |
|
| 122 | Ep: pct application non-entry in european phase |
Ref document number: 16925380 Country of ref document: EP Kind code of ref document: A1 |