CN101045599A - Method for treating sludge heavy metal - Google Patents
Method for treating sludge heavy metal Download PDFInfo
- Publication number
- CN101045599A CN101045599A CN 200710078443 CN200710078443A CN101045599A CN 101045599 A CN101045599 A CN 101045599A CN 200710078443 CN200710078443 CN 200710078443 CN 200710078443 A CN200710078443 A CN 200710078443A CN 101045599 A CN101045599 A CN 101045599A
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- lime
- fly ash
- sludge
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- flyash
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Abstract
A process for treating the heavy metals in sludge, especially the Zn and Cu in city sludge features that the lime modified powdered coal ash is used to passivate the Zn and Cu in the dewatered city sludge. Its passivated rate is more than 85% for Cu and more than 70% for Zn.
Description
One, technical field
The invention belongs to the technical field of handling sludge heavy-metal, particularly handle contain in the municipal sludge zinc and copper amount high method.
Two, background technology
The disposal of mud and utilization more and more cause people's attention, owing to contain abundant nitrogen, phosphorus, potassium and organic matter in the mud, be good plant nutrient raw material and soil physical property modifying agent, as agricultural and afforestation utilization is a kind of economically feasible the most and the most promising method of disposal, paid attention to by countries in the world.But the utilization ratio of countries in the world mud is not high at present, only is 40%～50% as Britain, Switzerland, Holland etc. yet.Its important reasons is that the heavy metal content in the mud exceeds standard.And heavy metal content is higher in the mud that wastewater treatment in China factory produces, and particularly plumbous (Pb), zinc (Zn), copper (Cu), manganese heavy metal elements such as (Mn) usually exceed standard in the mud.Statistics shows: China's municipal sludge heavy metal contamination is mainly based on Zn and Cu, and other heavy metal content is lower.China city is a large amount of, and to use zinc-plated pipeline be one of higher reason of Zn content in the domestic sludge.This has not only influenced the mud utilization, and also the leaching owing to sludge heavy-metal causes secondary pollution.Therefore, solve the heavy metal in the mud, make that heavy metal content in the mud does not exceed standard, innoxious and resource utilization, become one of problem of China and even whole world environment circle extensive concern.
Along with going deep into of Research of Environmental Sciences, people recognize gradually sludge heavy-metal to the harm of environment except outside the Pass having with its total amount, depend on the distribution of its form to a greater extent, so the research that the heavy metal form distributes in the mud has important directive significance to the development and use of mud.The biological effectiveness of heavy metal and the form of heavy metal have substantial connection.In general, the form that exists of heavy metal can be divided in the mud: 1. exchangeable species; 2. carbonate combined; 3. iron and manganese oxides combined; 4. sulfide and organically combine attitude; 5. residual form etc.Exchangeable species belongs to effectively and easily and is absorbed by crop, is called and can utilizes attitude; The carbonate combined is meant and carbonate bonded heavy metal; The ferrimanganic combined is meant and ferrimanganic bonded heavy metal ion that very strong binding ability is arranged between them; Sulfide and organically combine attitude and be meant with sulphur bonded heavy metal with organism and form the heavy metal ion of complex compound; Residual form is meant and extracts the heavy metal ion that exists with the layered silicate form after above-mentioned four components, exchangeable species and to organically combine the biological effectiveness of attitude heavy metal higher wherein, and other biological effectiveness is low.Therefore the biological effectiveness that how to reduce exchangeable species and combination attitude heavy metal is to handle the key point of the heavy metal in the mud.
The existing method of handling heavy metal in the mud mainly contains: methods such as curing/stabilizing, chemical reagent extraction, microorganism leaching, burning, phytoremediation.The shortcoming of chemical method, biological process, phytoremediation method and burning method is: removing heavy metal from mud not only needs a large amount of financial resources, material resources, and to take this method in the face of annual up to a hundred tons mud obviously be unpractiaca, and those absorbing enriched the plant of heavy metal, also exist and be difficult to further processing, and may cause the secondary pollution problem; Heavy metal in the direct passivation mud of research and utilization flyash is arranged, although test-results shows that adding 10%～20% flyash can make the attitude the utilized content of zinc (Zn) in the mud, copper (Cu), manganese (Mn), plumbous (Pb) obviously descend, its form is converted into steady state by labile state, but processing mud and soil just can not exert an influence to the biological effect and the environmental effect of mud when volume ratio was used with 1: 5.And this method is to utilize the strong basicity of flyash to make the heavy metal in the mud generate BS, and throw out is met acid and can be dissolved again, and then loses and solidify stabilization and cause secondary pollution, and special obviously is infeasible for the more serious Chongqing of acid rain.
Three, summary of the invention
The objective of the invention is: at the existing weak point of handling the sludge heavy-metal method, a kind of method of handling sludge heavy-metal is provided, floor space matrix that this method has passivation sludge heavy-metal non-reversibility, the mud after handling can be directly used in roof greenings such as Linear Stonecrop Herb and other agricultural and afforestation, simple to operate, and can make full use of flyash mud waste resource, characteristics such as with low cost.
Mechanism of the present invention: flyash is the combustion waste of China's quantity discharged maximum, but flyash has certain active porous spherical fine particle, and stronger adsorptive power is arranged.Particularly lime modified fly ash absorbent has very big specific surface area, increases 2.5 times than original state flyash, so it has very strong physical adsorption ability, also makes its chemical adsorptivity be enhanced simultaneously.In addition, the aluminosilicate of flyash modified generation and silicates have very strong ion-exchange performance, can adsorb with the heavy metal generation ion-exchange in the mud, and generally all be irreversible.Simultaneously modified coal ash also has strong basicity, can eliminate and kill the pathogenic agent in the mud under the modified coal ash effect of high pH value, thereby the toxicity of pollutent is reduced or eliminates.
The technical scheme that realizes the object of the invention is: a kind of method of handling sludge heavy-metal.Utilize lime modified fly ash absorbent to have very big specific surface area and very strong physical adsorption performance and very strong cation exchange property, with high zinc (Zn) and the copper (Cu) of content in its Passivation Treatment dehydration municipal sludge, concrete method steps is as follows:
(1) prepares lime modified fly ash absorbent
According to lime: the weight ratio of flyash is 1: 5.7～19 ratio, lime and flyash are mixed, then mixture is carried out roasting, maturing temperature is 950～1050 ℃, behind the roast 2.5～3.5 hours, material is taken out and cooling, levigate at last, just preparing specific surface area is 850～1050m again
2The modified fly ash absorbent of/kg.
(2) handle mud
After step (1) is finished, in the dehydration municipal sludge of crossing 10 mesh sieves, add the lime modified fly ash absorbent that step (1) is prepared, mix, under 30～58 ℃ of temperature, be divided under 35～45% the condition passivation 10～15 days with constant weight Faville water holding.Sorbent material wherein: the weight percent of dewatered sludge is 1: 4～9.
After the present invention adopts technique scheme, mainly contain following characteristics:
1 lime modified fly ash absorbent can be adjusted to the pH value of mud the scope that makes heavy metal ion have minimal solubility, can control the oxidation/reduction potential of heavy metal in the mud, generates the metallic compound that can not leach under the stable common environment.Therefore, to the good passivation effect of mud, particularly to the deactivation rate of heavy metal copper in the mud up to more than 85%, the deactivation rate Da Gaoda of zinc is more than 70%.
The exchange state of Zn, Cu, three kinds of elements of Mn, the content of combination attitude are obvious downtrending in the 2 processing back mud, and the content of Fe-Mn oxide and residual form is increase trend.Thereby reduced the biological effectiveness of sludge heavy-metal.
Mud after 3 these processing can be directly used in matrix and the agricultural and the afforestation of roofing lawn floor space, and can environment not polluted, and helps environmental protection.
4 the inventive method are simple to operate, make full use of the flyash waste resource, and are with low cost, easy to utilize.
The present invention can be widely used in handling the heavy metal in the mud, is specially adapted to handle high zinc and the copper of content in the municipal sludge.Adopting the mud after the present invention handles is good plant nutrient raw material and the agent of soil physics Improvement in Shape, can be widely used in agricultural and greenery patches, gardens and roof greening, helps making full use of sludge resource, helps environmental protection.
Four, embodiment
Below in conjunction with embodiment, further specify the present invention.
Embodiment 1
A kind of concrete steps of handling the sludge heavy-metal method are as follows:
(1) prepares lime modified fly ash absorbent
According to lime: the weight ratio of flyash is 1: 5.7 a ratio, to mix in lime and the flyash adding high-speed mixer, then mixture is dropped into the roasting kiln roasting, maturing temperature is 950 ℃, behind the roast 2.5 hours, material is taken out and cooling, levigate at last, just preparing specific surface area is 850m again
2The modified fly ash absorbent of/kg.
(2) handle mud
After step (1) is finished, in crossing the dehydration municipal sludge of 10 mesh sieves, add the lime modified fly ash absorbent that step (1) is prepared, mix, under 30 ℃ of temperature, be divided under 35% the condition passivation 10 days with constant weight Faville water holding.Sorbent material wherein: the weight percent of dewatered sludge is 1: 4.
Embodiment 2
A kind of concrete steps of handling the sludge heavy-metal method are as follows:
(1) prepares lime modified fly ash absorbent
According to lime: the weight ratio of flyash is 1: 14 a ratio, to mix in lime and the flyash adding high-speed mixer, then mixture is dropped into the roasting kiln roasting, maturing temperature is 1000 ℃, behind the roast 3 hours, material is taken out and cooling, levigate at last, that just prepare specific surface area is 1000m again
2/ kg modified fly ash absorbent.
(2) handle mud
After step (1) is finished, in crossing the dehydration municipal sludge of 10 mesh sieves, add the lime modified fly ash absorbent that step (1) is prepared, mix, under 42 ℃ of temperature, be divided under 40% the condition passivation 14 days with constant weight Faville water holding.Sorbent material wherein: the weight percent of dewatered sludge is 1: 6.
Embodiment 3
A kind of concrete steps of handling the sludge heavy-metal method are as follows:
(1) prepares lime modified fly ash absorbent
According to lime: the weight ratio of flyash is 1: 19 a ratio, to mix in lime and the flyash adding high-speed mixer, then mixture is dropped into the roasting kiln roasting, maturing temperature is 1050 ℃, behind the roast 3.5 hours, material is taken out and cooling, levigate at last, just preparing specific surface area is 1050m again
2The modified fly ash absorbent of/kg.
(2) handle mud
After step (1) is finished, in crossing the dehydration municipal sludge of 10 mesh sieves, add the lime modified fly ash absorbent that step (1) is prepared, mix, under 58 ℃ of temperature, be divided under 45% the condition passivation 15 days with constant weight Faville water holding.Sorbent material wherein: the weight percent of dewatered sludge is 1: 9.
Test-results:
With the mud after embodiment 1～3 processing, plant the Linear Stonecrop Herb experiment on the roof.Desiring the thick slag of the planted roof about 0.1cm of upper berth skim, spread layer of non-woven fabric above the slag, be divided into the sub-district of 0.5m * 0.5m with fragment of brick, in seven sub-districts, fill out the thick laterite of about 2cm, mud after then embodiment 1～3 being handled is inserted (each embodiment accounts for two sub-districts) in six experimental plots respectively, remains a sub-district and inserts untreated mud do contrast experiment.Seven sub-districts are paved, and thickness is 4～6cm, and management work such as the seeding row spacing by 2 * 2cm inserts Linear Stonecrop Herb in seven sub-districts, waters according to a conventional method, the prevention and control of plant diseases, pest control.
Behind two months Cheng Ping of Linear Stonecrop Herb, carry out following two groups of experiments respectively;
1, with sub-district and the contrast experiment district of embodiment 1～3, get plantation matrix respectively, 18 mesh sieves are crossed in air-dry back, extract through the water vibration, measure the content of Zn in the extracting solution, Cu respectively and calculate deactivation rate.
2, with another sub-district of embodiment 1～3, carry out rainfall or simulated rainfall, collect the water from diffusion of each sub-district respectively, analyze water from diffusion water quality.
Its result such as following table:
| Embodiment | Water from diffusion water quality (mg/l) | Curing degree (%) | |||
| Zn | Cu | COD | Zn | Cu | |
| Embodiment 1 | 1.21 | 0.98 | 65 | 83.8 | 90.0 |
| Embodiment 2 | 0.79 | 0.75 | 53 | 86.0 | 92.3 |
| Embodiment 3 | 0.64 | 0.30 | 38 | 90.2 | 94.0 |
As seen from the above table: after adopting modified coal ash to handle the sludge seeding Linear Stonecrop Herb, Zn, Cu curing degree reach 80% respectively, more than 90%, the deactivation rate of not planting Linear Stonecrop Herb than modified coal ash processing mud exceeds respectively more than 10,5 percentage points, and Zn, Cu are starkly lower than the municipal sewage system water quality standard in its water from diffusion.
Claims (4)
1, a kind of method of handling sludge heavy-metal is characterized in that concrete method steps is as follows:
(1) prepares lime modified fly ash absorbent
According to lime: the weight ratio of flyash is 1: 5.7～19 ratio, lime and flyash are mixed, then mixture is carried out roasting, maturing temperature is 950～1050 ℃, behind the roast 2.5～3.5 hours, material is taken out and cooling, levigate at last, just preparing specific surface area is 850～1050m again
2The modified fly ash absorbent of/kg;
(2) handle mud
After step (1) is finished, in the dehydration municipal sludge of crossing 10 mesh sieves, add the lime modified fly ash absorbent that step (1) is prepared, mix, under 30～58 ℃ of temperature, be divided into constant weight Faville water holding under 35～45% the condition, passivation 10～15 days, wherein sorbent material: the weight percent of dewatered sludge is 1: 4～9.
2,, it is characterized in that a kind of concrete steps of the method for handling sludge heavy-metal are as follows according to right 1 described a kind of method of handling sludge heavy-metal:
(1) prepares lime modified fly ash absorbent
According to lime: the weight ratio of flyash is 1: 5.7 a ratio, to mix in lime and the flyash adding high-speed mixer, then mixture is dropped into the roasting kiln roasting, maturing temperature is 950 ℃, behind the roast 2.5 hours, material is taken out and cooling, levigate at last, just preparing specific surface area is 850m again
2The modified fly ash absorbent of/kg;
(2) handle mud
After step (1) is finished, in the dehydration municipal sludge of crossing 10 mesh sieves, add the lime modified fly ash absorbent that step (1) is prepared, mix, under 30 ℃ of temperature, be divided into constant weight Faville water holding under 35% the condition, passivation 10 days, wherein sorbent material: the weight percent of dewatered sludge is 1: 4.
3,, it is characterized in that a kind of concrete steps of the method for handling sludge heavy-metal are as follows according to right 2 described a kind of methods of handling sludge heavy-metal:
(1) prepares lime modified fly ash absorbent
According to lime: the weight ratio of flyash is 1: 14 a ratio, to mix in lime and the flyash adding high-speed mixer, then mixture is dropped into the roasting kiln roasting, maturing temperature is 1000 ℃, behind the roast 3 hours, material is taken out and cooling, levigate at last, just preparing specific surface area is 1000m again
2The modified fly ash absorbent of/kg;
(2) handle mud
After step (1) is finished, in the dehydration municipal sludge of crossing 10 mesh sieves, add the lime modified fly ash absorbent that step (1) is prepared, mix, under 42 ℃ of temperature, be divided into constant weight Faville water holding under 40% the condition, passivation 14 days, wherein sorbent material: the weight percent of dewatered sludge is 1: 6.
4,, it is characterized in that a kind of concrete steps of the method for handling sludge heavy-metal are as follows according to right 3 described a kind of methods of handling sludge heavy-metal:
(1) prepares lime modified fly ash absorbent
According to lime: the weight ratio of flyash is 1: 19 a ratio, to mix in lime and the flyash adding high-speed mixer, then mixture is dropped into the roasting kiln roasting, maturing temperature is 1050 ℃, behind the roast 3.5 hours, material is taken out and cooling, levigate at last, just preparing specific surface area is 1050m again
2The modified fly ash absorbent of/kg;
(2) handle mud
After step (1) is finished, in the dehydration municipal sludge of crossing 10 mesh sieves, add the lime modified fly ash absorbent that step (1) is prepared, mix, under 58 ℃ of temperature, be divided into constant weight Faville water holding under 45% the condition, passivation 15 days, wherein sorbent material: the weight percent of dewatered sludge is 1: 9.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CNB2007100784432A CN100515966C (en) | 2007-04-30 | 2007-04-30 | Method for treating sludge heavy metal |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CNB2007100784432A CN100515966C (en) | 2007-04-30 | 2007-04-30 | Method for treating sludge heavy metal |
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| Publication Number | Publication Date |
|---|---|
| CN101045599A true CN101045599A (en) | 2007-10-03 |
| CN100515966C CN100515966C (en) | 2009-07-22 |
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| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CNB2007100784432A Expired - Fee Related CN100515966C (en) | 2007-04-30 | 2007-04-30 | Method for treating sludge heavy metal |
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Cited By (23)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101695649B (en) * | 2009-11-09 | 2011-08-31 | 湖南大学 | Application of modified flyash in urban sludge conditioning |
| CN102179233A (en) * | 2011-03-31 | 2011-09-14 | 中国矿业大学 | Method for preparing heavy metal ion absorbent |
| CN102603139A (en) * | 2012-04-05 | 2012-07-25 | 上海市园林科学研究所 | Method for eliminating copper and zinc pollution in municipal sludge utilizing barnyard grass |
| CN102746850A (en) * | 2012-07-02 | 2012-10-24 | 浩蓝环保股份有限公司 | Preparation method of fly ash stabilizing agent for managing heavy metal pollution |
| CN102814489A (en) * | 2012-07-31 | 2012-12-12 | 马鞍山科润冶金材料有限公司 | Method for preparing casting powder for steelmaking die-casting by using bentonite |
| CN102814490A (en) * | 2012-07-31 | 2012-12-12 | 马鞍山科润冶金材料有限公司 | Method for preparing casting powder for steelmaking die-casting by using calcareous shale |
| CN102814473A (en) * | 2012-07-31 | 2012-12-12 | 马鞍山科润冶金材料有限公司 | Preparation method of low-viscosity casting powder for preparing steelmaking cast ingots |
| CN102825218A (en) * | 2012-07-31 | 2012-12-19 | 马鞍山科润冶金材料有限公司 | Composite exothermic agent for high-manganese wear resistant steel |
| CN102825224A (en) * | 2012-07-31 | 2012-12-19 | 马鞍山科润冶金材料有限公司 | Composite heat generating agent for weathering steel |
| CN102825246A (en) * | 2012-07-31 | 2012-12-19 | 马鞍山科润冶金材料有限公司 | Covering slag for steelmaking die casting by using fly ash |
| CN102825223A (en) * | 2012-07-31 | 2012-12-19 | 马鞍山科润冶金材料有限公司 | Steel-making die-cast protecting slag produced by utilizing attapulgite |
| CN102825217A (en) * | 2012-07-31 | 2012-12-19 | 马鞍山科润冶金材料有限公司 | Composite heat generating agent for die steel |
| CN104003593A (en) * | 2014-06-14 | 2014-08-27 | 济南米铎碳新能源科技有限公司 | Sludge harmless treatment method |
| CN104140185A (en) * | 2014-08-06 | 2014-11-12 | 江西省广德环保科技有限公司 | Harmless recycling method for high-iron-chromium sludge |
| CN104402179A (en) * | 2014-11-28 | 2015-03-11 | 北京交通大学 | Method for passivating heavy metal in municipal sludge by adopting urea as passivator |
| CN106622111A (en) * | 2017-01-12 | 2017-05-10 | 哈尔滨工业大学 | Fly ash modifying method based on passivation of heavy metals in stored sludge |
| CN107503383A (en) * | 2017-10-17 | 2017-12-22 | 中国科学院武汉岩土力学研究所 | A kind of Multi-layered composite gasket system antifouling for refuse landfill base impervious |
| CN108236933A (en) * | 2016-12-27 | 2018-07-03 | 北京林业大学 | It is a kind of to remove sorbing material of organically combine state heavy metal ion and preparation method thereof in water removal |
| CN108892343A (en) * | 2018-07-23 | 2018-11-27 | 上海理工大学 | A method of passing through the fixed heavy metals in city sewage sludge of addition flying dust |
| CN109179928A (en) * | 2018-09-28 | 2019-01-11 | 沈阳航空航天大学 | The method of content of beary metal in the protein supernatant extracted in a kind of reduction sludge |
| CN109534629A (en) * | 2018-12-18 | 2019-03-29 | 毅康科技有限公司 | A method of administering river sludge heavy metal |
| CN110372075A (en) * | 2019-05-14 | 2019-10-25 | 山东环瑞生态科技有限公司 | A kind of new and effective fluorine removal medicament and its application |
| CN113042018A (en) * | 2021-03-12 | 2021-06-29 | 重庆大学 | Preparation method and application of calcium-rich biochar |
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2007
- 2007-04-30 CN CNB2007100784432A patent/CN100515966C/en not_active Expired - Fee Related
Cited By (27)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101695649B (en) * | 2009-11-09 | 2011-08-31 | 湖南大学 | Application of modified flyash in urban sludge conditioning |
| CN102179233A (en) * | 2011-03-31 | 2011-09-14 | 中国矿业大学 | Method for preparing heavy metal ion absorbent |
| CN102179233B (en) * | 2011-03-31 | 2012-10-24 | 中国矿业大学 | Method for preparing heavy metal ion absorbent |
| CN102603139A (en) * | 2012-04-05 | 2012-07-25 | 上海市园林科学研究所 | Method for eliminating copper and zinc pollution in municipal sludge utilizing barnyard grass |
| CN102746850A (en) * | 2012-07-02 | 2012-10-24 | 浩蓝环保股份有限公司 | Preparation method of fly ash stabilizing agent for managing heavy metal pollution |
| CN102746850B (en) * | 2012-07-02 | 2014-05-21 | 浩蓝环保股份有限公司 | Preparation method of fly ash stabilizing agent for managing heavy metal pollution |
| CN102825217A (en) * | 2012-07-31 | 2012-12-19 | 马鞍山科润冶金材料有限公司 | Composite heat generating agent for die steel |
| CN102825223B (en) * | 2012-07-31 | 2016-08-03 | 马鞍山科润冶金材料有限公司 | A kind of covering slag utilizing the steel-making molding of attapulgite system |
| CN102825218A (en) * | 2012-07-31 | 2012-12-19 | 马鞍山科润冶金材料有限公司 | Composite exothermic agent for high-manganese wear resistant steel |
| CN102825224A (en) * | 2012-07-31 | 2012-12-19 | 马鞍山科润冶金材料有限公司 | Composite heat generating agent for weathering steel |
| CN102825246A (en) * | 2012-07-31 | 2012-12-19 | 马鞍山科润冶金材料有限公司 | Covering slag for steelmaking die casting by using fly ash |
| CN102825223A (en) * | 2012-07-31 | 2012-12-19 | 马鞍山科润冶金材料有限公司 | Steel-making die-cast protecting slag produced by utilizing attapulgite |
| CN102814490A (en) * | 2012-07-31 | 2012-12-12 | 马鞍山科润冶金材料有限公司 | Method for preparing casting powder for steelmaking die-casting by using calcareous shale |
| CN102814489A (en) * | 2012-07-31 | 2012-12-12 | 马鞍山科润冶金材料有限公司 | Method for preparing casting powder for steelmaking die-casting by using bentonite |
| CN102814473A (en) * | 2012-07-31 | 2012-12-12 | 马鞍山科润冶金材料有限公司 | Preparation method of low-viscosity casting powder for preparing steelmaking cast ingots |
| CN104003593A (en) * | 2014-06-14 | 2014-08-27 | 济南米铎碳新能源科技有限公司 | Sludge harmless treatment method |
| CN104140185A (en) * | 2014-08-06 | 2014-11-12 | 江西省广德环保科技有限公司 | Harmless recycling method for high-iron-chromium sludge |
| CN104402179A (en) * | 2014-11-28 | 2015-03-11 | 北京交通大学 | Method for passivating heavy metal in municipal sludge by adopting urea as passivator |
| CN108236933A (en) * | 2016-12-27 | 2018-07-03 | 北京林业大学 | It is a kind of to remove sorbing material of organically combine state heavy metal ion and preparation method thereof in water removal |
| CN106622111A (en) * | 2017-01-12 | 2017-05-10 | 哈尔滨工业大学 | Fly ash modifying method based on passivation of heavy metals in stored sludge |
| CN107503383A (en) * | 2017-10-17 | 2017-12-22 | 中国科学院武汉岩土力学研究所 | A kind of Multi-layered composite gasket system antifouling for refuse landfill base impervious |
| CN108892343A (en) * | 2018-07-23 | 2018-11-27 | 上海理工大学 | A method of passing through the fixed heavy metals in city sewage sludge of addition flying dust |
| CN109179928A (en) * | 2018-09-28 | 2019-01-11 | 沈阳航空航天大学 | The method of content of beary metal in the protein supernatant extracted in a kind of reduction sludge |
| CN109534629A (en) * | 2018-12-18 | 2019-03-29 | 毅康科技有限公司 | A method of administering river sludge heavy metal |
| CN110372075A (en) * | 2019-05-14 | 2019-10-25 | 山东环瑞生态科技有限公司 | A kind of new and effective fluorine removal medicament and its application |
| CN110372075B (en) * | 2019-05-14 | 2022-03-25 | 山东环瑞生态科技有限公司 | Efficient defluorination medicament and application thereof |
| CN113042018A (en) * | 2021-03-12 | 2021-06-29 | 重庆大学 | Preparation method and application of calcium-rich biochar |
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