CN112939622A - Method for preparing ceramsite by using chromium-containing sludge - Google Patents

Method for preparing ceramsite by using chromium-containing sludge Download PDF

Info

Publication number
CN112939622A
CN112939622A CN202110109509.XA CN202110109509A CN112939622A CN 112939622 A CN112939622 A CN 112939622A CN 202110109509 A CN202110109509 A CN 202110109509A CN 112939622 A CN112939622 A CN 112939622A
Authority
CN
China
Prior art keywords
chromium
containing sludge
powder
dehydrated
ceramsite
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.)
Pending
Application number
CN202110109509.XA
Other languages
Chinese (zh)
Inventor
侯浩波
张鹏举
李银生
叶非华
韩旭
纪建业
孙琪
游以文
陈娜娜
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Zhaoqing Wuda Institute Of Environmental Technology
Original Assignee
Zhaoqing Wuda Institute Of Environmental Technology
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Zhaoqing Wuda Institute Of Environmental Technology filed Critical Zhaoqing Wuda Institute Of Environmental Technology
Priority to CN202110109509.XA priority Critical patent/CN112939622A/en
Publication of CN112939622A publication Critical patent/CN112939622A/en
Pending legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B33/00Clay-wares
    • C04B33/02Preparing or treating the raw materials individually or as batches
    • C04B33/13Compounding ingredients
    • C04B33/132Waste materials; Refuse; Residues
    • C04B33/1321Waste slurries, e.g. harbour sludge, industrial muds
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B33/00Clay-wares
    • C04B33/02Preparing or treating the raw materials individually or as batches
    • C04B33/13Compounding ingredients
    • C04B33/132Waste materials; Refuse; Residues
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B33/00Clay-wares
    • C04B33/02Preparing or treating the raw materials individually or as batches
    • C04B33/13Compounding ingredients
    • C04B33/132Waste materials; Refuse; Residues
    • C04B33/1328Waste materials; Refuse; Residues without additional clay
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B38/00Porous mortars, concrete, artificial stone or ceramic ware; Preparation thereof
    • C04B38/009Porous or hollow ceramic granular materials, e.g. microballoons
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B2235/00Aspects relating to ceramic starting mixtures or sintered ceramic products
    • C04B2235/70Aspects relating to sintered or melt-casted ceramic products
    • C04B2235/96Properties of ceramic products, e.g. mechanical properties such as strength, toughness, wear resistance
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P40/00Technologies relating to the processing of minerals
    • Y02P40/60Production of ceramic materials or ceramic elements, e.g. substitution of clay or shale by alternative raw materials, e.g. ashes

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Ceramic Engineering (AREA)
  • Materials Engineering (AREA)
  • Structural Engineering (AREA)
  • Organic Chemistry (AREA)
  • Dispersion Chemistry (AREA)
  • Environmental & Geological Engineering (AREA)
  • Treatment Of Sludge (AREA)

Abstract

The invention discloses a method for preparing ceramsite by using chromium-containing sludge. The method comprises the steps of carrying out reduction roasting treatment on chromium-containing sludge, mixing the chromium-containing sludge with coal powder and/or sawdust, dehydrated silica-alumina tailings, limestone and water for granulation, and drying and sintering granules to obtain the ceramsite. The method realizes the resource utilization while solving the pollution to human bodies and environment in the resource process of the hexavalent chromium sludge, and has great economic and environmental benefits.

Description

Method for preparing ceramsite by using chromium-containing sludge
Technical Field
The invention relates to a harmless treatment and resource utilization method of solid waste, in particular to a method for preparing high-performance ceramsite by utilizing hexavalent chromium-containing sludge and solid waste resources such as tailings and the like, and belongs to the technical field of comprehensive utilization of mining and metallurgy solid waste resources and environmental remediation.
Background
In recent years, with the increasing speed of industrialization, more and more solid waste is generated. If a large amount of solid waste can not be harmlessly disposed in time, serious environmental pollution is caused.
At present, the treatment mode of the solid waste in China mainly comprises incineration, solidification and landfill. However, the traditional disposal method has the problems of large floor area, high energy consumption for treatment, secondary pollution and the like. The resource utilization of solid waste is limited by the factors of not mature technology, high cost and the like. Sludge is a typical solid waste, and its production is rapidly increasing. At present, the harmless treatment mode of the sludge containing heavy metals is mainly solidification landfill, and the resource utilization way of the sludge is still in the starting stage.
The ceramsite is a ceramic lightweight aggregate produced by roasting, and is widely applied to the industries of building materials, gardens and water treatment. The main raw materials for preparing the ceramsite comprise clay, shale, fly ash and the like, but with the continuous acceleration of resource consumption, the traditional production raw materials are in short supply and demand for the production of the ceramsite, and other alternative raw materials are urgently needed to be explored, so that the improvement and optimization of the ceramsite production raw materials and the process are realized. The method for preparing the ceramsite by taking the treated sludge as the raw material can realize the harmless treatment and resource utilization of the sludge, simultaneously solves the problem of limited raw materials for producing the ceramsite, and provides a new way for the consumption of solid wastes and the comprehensive utilization of resources.
Disclosure of Invention
Based on the problems of low resource utilization degree of the chromium-containing sludge and limited production raw materials of the ceramsite in the prior art, the invention aims to provide the method for preparing the high-performance building ceramsite by using the chromium-containing sludge as an addition raw material and matching with solid wastes such as tailings and the like.
The invention also provides a method for preparing ceramsite by using the chromium-containing sludge, which comprises the following steps:
1) respectively drying and dehydrating the chromium-containing sludge and the silicon-aluminum tailings to obtain dehydrated chromium-containing sludge and dehydrated silicon-aluminum tailings;
2) uniformly mixing the dehydrated chromium-containing sludge and a carbonaceous reducing agent, and placing the mixture in a protective atmosphere for reduction roasting to obtain reduced chromium-containing sludge;
3) respectively grinding the reduced chromium-containing sludge and the dehydrated alumino-silicate tailings to obtain reduced chromium-containing sludge powder and dehydrated alumino-silicate tailing powder;
4) mixing and granulating reduced chromium-containing sludge powder, coal powder and/or sawdust, dehydrated silica-alumina tailing powder, limestone powder and water to obtain granules;
5) drying and sintering the granules to obtain the finished product.
As a preferable scheme, the chromium-containing sludge and the silica-alumina tailings are dried and dehydrated until the weight loss rate is balanced to be less than 0.5 percent.
As a preferred scheme, SiO of the silicon-aluminum tailings2Is not less than 50 percent.
Preferably, the mass ratio of the dehydrated chromium-containing sludge to the carbonaceous reducing agent is 1: 0.03-1.0. Under the preferable proportion of the carbonaceous reducing agent, Cr in the chromium-containing sludge can be ensured6+Is fully reduced. Because the chromium-containing sludge contains a large amount of Cr6+,Cr6+Can generate great physiological toxic action on human body, and the chromium-containing sludge is reduced by adopting a high-temperature carbon reduction method, so that Cr in the chromium-containing sludge can be reduced6+Conversion to Cr3+And low-valent chromium such as Cr and the like, so that the toxicity is reduced, and the safety of the process of preparing the ceramsite by recycling can be ensured. The carbonaceous reducing agent is coke, coal powder and the like which are common in the industry.
As a preferred scheme, the reducing roasting conditions are as follows: the temperature is 300-700 ℃, and the time is not less than 0.5 hour. Can ensure Cr in the chromium-containing sludge under the optimized reduction condition6+Is fully reduced.
As a preferable scheme, the granularity of the reduced chromium-containing sludge and the dehydrated alumino-silicate tailings is less than 200 meshes.
As a preferred scheme, the mass percent of the reduced chromium-containing sludge powder, the coal powder and/or the saw dust, the dehydrated silica-alumina tailing powder and the limestone powder is as follows: reducing 5-30% of chromium-containing sludge powder; 3-10% of coal powder and/or sawdust; 30-70% of dehydrated silica-alumina tailing powder; 5-30% of limestone powder. The coal powder and the sawdust play important roles as follows: when the granules are calcined, gas is generated under the high-temperature condition, the expansion range of the granules is expanded, the formation of micropores in the ceramsite is facilitated, and the firing temperature of the ceramsite is reduced. Limestone powder is decomposed in the high-temperature sintering process, mainly plays a role in denuding before decomposition, and activated calcium oxide generated after decomposition mainly plays a role in a flux. According to the preferable scheme, the components of the reduced chromium-containing sludge powder, the dehydrated alumino-silica tailing powder, the limestone powder and the like are controlled within a certain range, so that the components of elements such as silicon, aluminum, iron, calcium, sodium and the like can be effectively adjusted, and the ceramsite with better performance can be obtained through high-temperature solid-phase reaction.
As a preferable scheme, after the granules are dried at the temperature of 110-130 ℃ for 10-30 minutes, the temperature is raised to 1050-1150 ℃ within 2-4 hours, and the granules are calcined for 10-20 minutes. The ceramic particle with better comprehensive performance can be obtained by controlling the temperature rise rate, the sintering temperature and the sintering time to regulate and control the density, the strength and other properties of the ceramic particle.
Compared with the prior art, the technical scheme of the invention has the following beneficial effects:
the ceramsite produced by the method takes the chromium-containing sludge and the silicon-aluminum tailings as raw materials, and can realize safe disposal and resource utilization of dangerous waste and solid waste.
The method can effectively reduce the toxicity of heavy metals in the sludge, realize the solidification and stabilization of the heavy metals in the sludge, and ensure that the solidification rate of the heavy metals in the ceramsite reaches more than 93 percent.
The method solves the problem of limited raw materials for producing the ceramsite, and provides a large amount of raw materials for preparing the ceramsite.
The method can obtain the ceramsite with better performance, and the stacking density of the ceramsite is 758-783 kg/m3The density grade is 800 grade, the cylinder pressure strength is 6.7-8.5 MPa, and the water absorption rate is 6.5-8.9%.
Detailed Description
The following specific examples are intended to further illustrate the present disclosure, but not to limit the scope of the claims.
Example 1
In this example, the tailings from the mineral separation of a certain tin ore field in the municipality of Guangxi province and the electroplating sludge produced by a certain metal product Co., Ltd. in Guangdong province were collected as raw materials, the chromium content (in terms of oxides) in the electroplating sludge was 2.47%, and the chemical composition of the tailings from the mineral separation was shown in Table 1:
TABLE 1 tailings chemistry and content of mineral processing
Chemical composition SiO2 Al2O3 FeO CaO MgO As2O3 PbO Others
Content/wt. -%) 65.12 4.57 10.03 5.65 3.21 1.04 0.25 10.13
The preparation method of the ceramsite comprises the following steps:
(1) dehydrating the chromium-containing sludge and the tailings, and balancing the weight loss rate to be below 0.5%;
(2) uniformly mixing the dried chromium-containing sludge and activated carbon in a mass ratio of 1:0.05, reducing for 1 hour at 500 ℃ in a nitrogen atmosphere, and collecting the reduced chromium-containing sludge;
(3) grinding the chromium-containing sludge and the tailings until the granularity of the chromium-containing sludge and the tailings is less than 200 meshes;
(4) uniformly mixing the reduced chromium-containing sludge, sawdust, tailings and limestone powder according to the mass ratio of 20:5:65:10, and preparing the mixed material into 1-6 mm ceramsite in a spraying type water-adding stirring mode;
(5) the prepared ceramsite is dried for 20 minutes at 120 ℃, then heated to 1100 ℃ within 3 hours, calcined for 15 minutes at the temperature, and naturally cooled to room temperature to obtain the final ceramsite product.
The obtained ceramsite has a bulk density of 763kg/m3The density grade is 800 grade, the cylinder pressure strength is 8.2MPa, the water absorption rate is 7.3 percent, and the curing rate of heavy metal chromium is 99.99 percent. The heavy metal solidification rate is based on the concentration of leached heavy metal, the test is carried out according to the national standard GB/T5085.3-2007, and an analysis instrument adopts ICP-MS.
Example 2
The preparation method of the ceramsite comprises the following steps:
(1) dehydrating the chromium-containing sludge and the tailings in the embodiment 1, and balancing the weight loss rate to be below 0.5%;
(2) uniformly mixing the dried chromium-containing sludge and activated carbon in a mass ratio of 1:0.05, reducing for 0.5 hour at 600 ℃ in a nitrogen atmosphere, and collecting the reduced chromium-containing sludge;
(3) grinding the chromium-containing sludge and the tailings until the granularity of the chromium-containing sludge and the tailings is less than 200 meshes;
(4) uniformly mixing the reduced chromium-containing sludge, sawdust, tailings and limestone powder according to the mass ratio of 25:5:65:5, and preparing the mixed material into 1-6 mm ceramsite in a spray type water-adding stirring mode;
(5) the prepared ceramsite is dried for 20 minutes at 120 ℃, then heated to 1100 ℃ within 3 hours, calcined for 15 minutes at the temperature, and naturally cooled to room temperature to obtain the final ceramsite product.
The bulk density of the obtained ceramsite is 783kg/m3The density grade is 800 grade, the cylinder pressure strength is 8.5MPa, the water absorption rate is 7.6 percent, and the curing rate of heavy metal chromium is 99.99 percent. The heavy metal solidification rate is based on the concentration of leached heavy metal, the test is carried out according to the national standard GB/T5085.3-2007, and an analysis instrument adopts ICP-MS.
Example 3
The preparation method of the ceramsite comprises the following steps:
(1) dehydrating the chromium-containing sludge and the tailings in the embodiment 1, and balancing the weight loss rate to be below 0.5%;
(2) uniformly mixing the dried chromium-containing sludge and activated carbon in a mass ratio of 1:0, calcining for 0.5 hour at 600 ℃ in a nitrogen atmosphere, and collecting the calcined chromium-containing sludge;
(3) grinding the chromium-containing sludge and the tailings until the granularity of the chromium-containing sludge and the tailings is less than 200 meshes;
(4) uniformly mixing the reduced chromium-containing sludge, sawdust, tailings and limestone powder according to the mass ratio of 25:5:65:5, and preparing the mixed material into 1-6 mm ceramsite in a spray type water-adding stirring mode;
(5) the prepared ceramsite is dried for 20 minutes at 120 ℃, then heated to 1100 ℃ within 3 hours, calcined for 15 minutes at the temperature, and naturally cooled to room temperature to obtain the final ceramsite product.
The obtained ceramsite has a bulk density of 774kg/m3The density grade is 800 grade, the cylinder pressure strength is 8.2MPa, the water absorption rate is 6.5 percent, and the curing rate of heavy metal chromium is 97.89 percent. The heavy metal solidification rate is based on the concentration of leached heavy metal, the test is carried out according to the national standard GB/T5085.3-2007, and an analysis instrument adopts ICP-MS.
Example 4
The preparation method of the ceramsite comprises the following steps:
(1) dehydrating the chromium-containing sludge and the tailings in the embodiment 1, and balancing the weight loss rate to be below 0.5%;
(2) uniformly mixing the dried chromium-containing sludge and activated carbon in a mass ratio of 1:0.05, reducing for 0.5 hour at 600 ℃ in a nitrogen atmosphere, and collecting the reduced chromium-containing sludge;
(3) grinding the chromium-containing sludge and the tailings until the granularity of the chromium-containing sludge and the tailings is less than 200 meshes;
(4) uniformly mixing the reduced chromium-containing sludge, sawdust, tailings and limestone powder according to the mass ratio of 40:5:40:15, and preparing the mixed material into 1-6 mm ceramsite in a spray type water-adding stirring mode;
(5) the prepared ceramsite is dried for 20 minutes at 120 ℃, then heated to 1100 ℃ within 3 hours, calcined for 15 minutes at the temperature, and naturally cooled to room temperature to obtain the final ceramsite product.
The obtained ceramsite has the bulk density of 758kg/m3The density grade is 800 grade, the cylinder pressure strength is 6.7MPa, the water absorption is 8.9 percent, and the curing rate of heavy metal chromium is 93.58 percent. The heavy metal solidification rate is based on the concentration of leached heavy metal, the test is carried out according to the national standard GB/T5085.3-2007, and an analysis instrument adopts ICP-MS.
The foregoing embodiments and description have been presented only to illustrate the principles and preferred embodiments of the invention, and various changes and modifications may be made therein without departing from the spirit and scope of the invention as hereinafter claimed.

Claims (8)

1. A method for preparing ceramsite by using chromium-containing sludge is characterized by comprising the following steps: the method comprises the following steps:
1) respectively drying and dehydrating the chromium-containing sludge and the silicon-aluminum tailings to obtain dehydrated chromium-containing sludge and dehydrated silicon-aluminum tailings;
2) uniformly mixing the dehydrated chromium-containing sludge and a carbonaceous reducing agent, and placing the mixture in a protective atmosphere for reduction roasting to obtain reduced chromium-containing sludge;
3) respectively grinding the reduced chromium-containing sludge and the dehydrated alumino-silicate tailings to obtain reduced chromium-containing sludge powder and dehydrated alumino-silicate tailing powder;
4) mixing and granulating reduced chromium-containing sludge powder, coal powder and/or sawdust, dehydrated silica-alumina tailing powder, limestone powder and water to obtain granules;
5) drying and sintering the granules to obtain the finished product.
2. The method for preparing ceramsite by using chromium-containing sludge as defined in claim 1, wherein the method comprises the following steps: drying and dehydrating the chromium-containing sludge and the silicon-aluminum tailings until the weight loss rate is balanced to be below 0.5 percent.
3. The method for preparing ceramsite by using chromium-containing sludge as defined in claim 1, wherein the method comprises the following steps: SiO of the silica-alumina tailings2Is not less than 50 percent.
4. The method for preparing ceramsite by using chromium-containing sludge as defined in claim 1, wherein the method comprises the following steps: the mass ratio of the dehydrated chromium-containing sludge to the carbonaceous reducing agent is 1: 0.03-1.0.
5. The method for preparing ceramsite by using chromium-containing sludge as defined in claim 1, wherein the method comprises the following steps: the reducing roasting conditions are as follows: the temperature is 300-700 ℃, and the time is not less than 0.5 hour.
6. The method for preparing ceramsite by using chromium-containing sludge as defined in claim 1, wherein the method comprises the following steps: the granularity of the reduced chromium-containing sludge and the dehydrated alumino-silico tailings is less than 200 meshes.
7. The method for preparing ceramsite by using chromium-containing sludge as defined in claim 1, wherein the method comprises the following steps: the mass percentages of the reduced chromium-containing sludge powder, the coal powder and/or the saw dust, the dehydrated silicon-aluminum tailing powder and the limestone powder are as follows: reducing 5-30% of chromium-containing sludge powder; 3-10% of coal powder and/or sawdust; 30-70% of dehydrated silica-alumina tailing powder; 5-30% of limestone powder.
8. The method for preparing ceramsite by using chromium-containing sludge as defined in claim 1, wherein the method comprises the following steps: and drying the granules at 110-130 ℃ for 10-30 minutes, then heating to 1050-1150 ℃ within 2-4 hours, and calcining for 10-20 minutes.
CN202110109509.XA 2021-01-25 2021-01-25 Method for preparing ceramsite by using chromium-containing sludge Pending CN112939622A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202110109509.XA CN112939622A (en) 2021-01-25 2021-01-25 Method for preparing ceramsite by using chromium-containing sludge

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202110109509.XA CN112939622A (en) 2021-01-25 2021-01-25 Method for preparing ceramsite by using chromium-containing sludge

Publications (1)

Publication Number Publication Date
CN112939622A true CN112939622A (en) 2021-06-11

Family

ID=76237614

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202110109509.XA Pending CN112939622A (en) 2021-01-25 2021-01-25 Method for preparing ceramsite by using chromium-containing sludge

Country Status (1)

Country Link
CN (1) CN112939622A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114349477A (en) * 2022-01-12 2022-04-15 湖南国发控股有限公司 Detoxification formula with high chromium slag amount and process for producing synergistic light aggregate
CN114920530A (en) * 2022-03-28 2022-08-19 佛山辰石环保材料有限公司 Sintering-free ceramsite and preparation method thereof
CN116396059A (en) * 2023-04-12 2023-07-07 常熟理工学院 Method for preparing ceramsite by using chromium-containing waste residues and printing and dyeing sludge and product thereof

Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2005224802A (en) * 2005-05-09 2005-08-25 Dowa Mining Co Ltd Reduction treatment method for sludge, or the like, containing hexavalent chromium
CN102584175A (en) * 2012-02-06 2012-07-18 青岛理工大学 Method for preparing ultra-thin highly-waterproof type ceramsite by taking sediments and chromium slag as raw materials
CN102875116A (en) * 2012-10-17 2013-01-16 福建微水环保技术有限公司 Method for preparing chromium-containing sludge ceramsite
CN105347837A (en) * 2015-12-09 2016-02-24 漳州微水固体废物处置有限公司 Method for preparing light ceramisite by means of chromium-containing sludge
CN106045245A (en) * 2016-07-11 2016-10-26 辽宁点石技术开发有限公司 Method for treating chromium-containing tannery sludge and recycling chromium metal
CN107353034A (en) * 2017-07-27 2017-11-17 武汉理工大学 A kind of method for preparing haydite using microwave sintering curing heavy metal chromium
CN110655339A (en) * 2018-06-29 2020-01-07 湖南万容科技股份有限公司 Process method for preparing ceramsite by sludge and inorganic solid waste
CN111116170A (en) * 2019-12-24 2020-05-08 北京大学 Ceramsite material prepared from serpentine tailings and sludge and preparation method thereof

Patent Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2005224802A (en) * 2005-05-09 2005-08-25 Dowa Mining Co Ltd Reduction treatment method for sludge, or the like, containing hexavalent chromium
CN102584175A (en) * 2012-02-06 2012-07-18 青岛理工大学 Method for preparing ultra-thin highly-waterproof type ceramsite by taking sediments and chromium slag as raw materials
CN102875116A (en) * 2012-10-17 2013-01-16 福建微水环保技术有限公司 Method for preparing chromium-containing sludge ceramsite
CN105347837A (en) * 2015-12-09 2016-02-24 漳州微水固体废物处置有限公司 Method for preparing light ceramisite by means of chromium-containing sludge
CN106045245A (en) * 2016-07-11 2016-10-26 辽宁点石技术开发有限公司 Method for treating chromium-containing tannery sludge and recycling chromium metal
CN107353034A (en) * 2017-07-27 2017-11-17 武汉理工大学 A kind of method for preparing haydite using microwave sintering curing heavy metal chromium
CN110655339A (en) * 2018-06-29 2020-01-07 湖南万容科技股份有限公司 Process method for preparing ceramsite by sludge and inorganic solid waste
CN111116170A (en) * 2019-12-24 2020-05-08 北京大学 Ceramsite material prepared from serpentine tailings and sludge and preparation method thereof

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114349477A (en) * 2022-01-12 2022-04-15 湖南国发控股有限公司 Detoxification formula with high chromium slag amount and process for producing synergistic light aggregate
CN114349477B (en) * 2022-01-12 2023-08-25 湖南国发控股有限公司 High chromium slag detoxification formula and synergistic lightweight aggregate production process
CN114920530A (en) * 2022-03-28 2022-08-19 佛山辰石环保材料有限公司 Sintering-free ceramsite and preparation method thereof
CN116396059A (en) * 2023-04-12 2023-07-07 常熟理工学院 Method for preparing ceramsite by using chromium-containing waste residues and printing and dyeing sludge and product thereof
CN116396059B (en) * 2023-04-12 2024-02-23 常熟理工学院 Method for preparing ceramsite by using chromium-containing waste residues and printing and dyeing sludge and product thereof

Similar Documents

Publication Publication Date Title
CN112939622A (en) Method for preparing ceramsite by using chromium-containing sludge
CN110282925B (en) Artificial porous aggregate of carbonized steel slag and preparation method thereof
CN108821621B (en) Light high-strength ceramsite and preparation method thereof
CN114105610A (en) Aluminum ash-based porous ceramic material and preparation method thereof
CN113336516A (en) Cementing material prepared from multi-element solid wastes and cooperative regulation and control method thereof
CN110104979B (en) Method for preparing coal gangue lightweight aggregate by adopting belt sintering
CN113213891A (en) Ceramsite preparation method by utilizing waste incineration fly ash and prepared ceramsite
CN107057705B (en) Heavy metal contaminated soil remediation material, preparation method and application
CN114368961B (en) Preparation method and new application of iron tailing ceramic filter material
CN111875274A (en) Method for preparing ceramsite and ceramsite prepared by same
CN112430066A (en) Light high-strength ceramsite and preparation method and application thereof
CN111285406A (en) Method for co-recycling alumina red mud and semi-dry desulfurization ash
CN115677248B (en) Carbon-fixing lightweight aggregate and preparation method thereof
CN112430062A (en) Preparation method of light high-strength ceramsite, prepared light high-strength ceramsite and application
CN113800941B (en) Method for preparing ceramsite by utilizing chromium-contaminated soil and ceramsite
CN111233353A (en) Method for producing general cement clinker by using iron oxide slag to partially replace iron correction raw material
CN111101002A (en) Production process for magnesium smelting and cement co-production by Pidgeon process
CN114085067A (en) Method for preparing sintered material by using secondary aluminum ash
CN112028660B (en) Composition for preparing ultra-light ceramsite, ceramsite and preparation method thereof
CN111302679B (en) Cement admixture containing vanadium titano-magnetite tailings and preparation method and application thereof
CN110106314B (en) Chromium slag innocent treatment method and composite material prepared by same
CN116332535A (en) Method for producing active micro powder by cooperatively treating manganese slag by using fluidized bed furnace
CN113979775B (en) Method for preparing ceramsite proppant by using secondary aluminum ash
CN114394845B (en) High-chromium slag amount sintering formula and synergistic foaming ceramic production process
CN111320405B (en) Solid hazardous waste base mineral admixture and preparation method thereof

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
RJ01 Rejection of invention patent application after publication

Application publication date: 20210611

RJ01 Rejection of invention patent application after publication