AU2021100066A4 - Method of increasing the thickness of the outer enamel layer of ceramsite with sludge slurry - Google Patents
Method of increasing the thickness of the outer enamel layer of ceramsite with sludge slurry Download PDFInfo
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- AU2021100066A4 AU2021100066A4 AU2021100066A AU2021100066A AU2021100066A4 AU 2021100066 A4 AU2021100066 A4 AU 2021100066A4 AU 2021100066 A AU2021100066 A AU 2021100066A AU 2021100066 A AU2021100066 A AU 2021100066A AU 2021100066 A4 AU2021100066 A4 AU 2021100066A4
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- sludge
- ceramsite
- raw materials
- sintering
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- C—CHEMISTRY; METALLURGY
- C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
- C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
- C04B38/00—Porous mortars, concrete, artificial stone or ceramic ware; Preparation thereof
- C04B38/007—Porous mortars, concrete, artificial stone or ceramic ware; Preparation thereof characterised by the pore distribution, e.g. inhomogeneous distribution of pores
- C04B38/0077—Materials with a non-porous skin
-
- C—CHEMISTRY; METALLURGY
- C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
- C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
- C04B38/00—Porous mortars, concrete, artificial stone or ceramic ware; Preparation thereof
- C04B38/009—Porous or hollow ceramic granular materials, e.g. microballoons
-
- C—CHEMISTRY; METALLURGY
- C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
- C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
- C04B2235/00—Aspects relating to ceramic starting mixtures or sintered ceramic products
- C04B2235/65—Aspects relating to heat treatments of ceramic bodies such as green ceramics or pre-sintered ceramics, e.g. burning, sintering or melting processes
Abstract
The present disclosure belongs to the field of paint and pertains to a method of increasing
the thickness of the outer enamel layer of ceramsite with sludge slurry. The method includes the
following steps: Three materials of sludge, fly ash and coal gangue are respectively ground
mechanically for 1-2 hours, and sieved over a 100-mesh screen; They are mixed uniformly
following certain weight parts for 20-30 minutes, and dried in a blast air oven at 90-105°C until
the mass is constant; A tablet press is used for pressure shaping at a shaping pressure greater than
3 MPa to get cylindrical complex green bodies of raw materials; The sieved sludge materials are
mixed with water at a certain proportion to produce sludge slurry; The green bodies are wetted in
the sludge slurry transiently and bound with the sludge slurry evenly, ready for sintering; They
are sintered at 1000°C-1250°C with an air velocity of 50-100 ml/min; and upon the completion
of sintering, they are cooled to room temperature to get the shaped ceramsite. Ceramsite binding
with sludge can effectively increase the thickness of the outer enamel layer of ceramsite products,
and the outer enamel layer of sintered ceramsite products is smooth and flat.
Description
The present disclosure belongs to the field of paint, and pertains to a method of increasing
the thickness of the outer enamel layer of ceramsite with sludge slurry.
Nowadays, China's urban sewage treatment capacity has been increasing year by year. As a
byproduct of sewage treatment, the production of sewage sludge also increases gradually, with
D the main hazards of large amount, large volume, high moisture content, high heavy metals
content and odor. Sludge contains various heavy metals and other bio-toxic substances which
may cause secondary pollution. If not treatment effectively, the heavy metals in sludge tend to
return to the ecological environment and accumulate in organisms, finally increasing the risk of
cancers to human. The existing sludge treatment methods mainly include landfill, compost,
natural drying, incineration and so on. Currently, the most effective harmless treatment method is
"drying and incineration". On the other hand, a large amount of concrete is used in the
construction of cities, and there are a lot of natural sand and stone as aggregate in concrete.
Concrete has consumed huge amounts of natural resources for a long time. The annual concrete
consumption in China is about 1 billion m3 . At present, there are many artificial ceramsite
. materials widely used in China, such as clay ceramsite, fly ash ceramsite, etc. These ceramsite
have different engineering characteristics and uses. Ceramsite has low density, high strength,
good fire resistance and low weight, thus having an economic benefit of replacing traditional
natural building materials for further development. The utilization of sludge together with other
industrial wastes for the preparation of ceramsite not only solves the pollution of sludge, but also
allows the recycling of industrial wastes to produce economical value, being a very effective and
promising method for collaborative resourcing of wastes.
It is an object of the present invention to address the foregoing problems or at least to
provide the public with a useful choice.
It is acknowledged that the term 'comprise' may, under varying jurisdictions, be attributed
with either an exclusive or an inclusive meaning. For the purpose of this specification, and unless otherwise noted, the term 'comprise' shall have an inclusive meaning - i.e. that it will be taken to mean an inclusion of not only the listed components it directly references, but also other non-specified components or elements. This rationale will also be used when the term 'comprised' or 'comprising' is used in relation to one or more steps in a method or process.
Further aspects and advantages of the present invention will become apparent from the ensuing
description which is given by way of example only. DISCLOSURE OF INVENTION The present disclosure aims to utilize the three wastes of sludge, fly ash and coal gangue in
a collaborative resourcing way and to provide an artificial lightweight aggregate building
J material with excellent performances.
The present disclosure provides a sludge mixed ceramsite, wherein the ceramsite includes
sludge, fly ash and coal gangue in the following parts by weight: 60-80 parts of sludge, 10-20
parts of fly ash, and 10-20 parts of coal gangue.
Further, the chemical compositions of the three raw materials are respectively:
Sludge ash after incineration: A1 2 0 3 27.3%, SiO 2 34.6%, P 2 05 15.9%, Fe203 6.4%, CaO
6.2%, and others 7.8%;
Fly ash: A1 2 0 3 18.3%, SiO 2 43.4%, CaO 24.3%, and others 10.1%;
Coal gangue: A1 2 0 3 38.3%, SiO 2 59.5%, Fe203 0.6%, CaO 0.2%, and others 1.4%.
According to another aspect of the present disclosure, it provides a method of increasing
o the thickness of the outer enamel layer of ceramsite with sludge slurry, the specific steps of
which are as below:
(1) Drying: Mechanically dehydrated sludge, coal gangue and fly ash are dried in a blast
air oven with the temperature maintaining at 100-105°C for a period of 48-72 hours respectively,
until the mass is constant;
(2) Crushing: the three materials in step (1) are respectively ground mechanically for 1-2
hours, and sieved over a 100-mesh screen;
(3) Mixing: the sieved fine materials from step (2) are mixed uniformly following the
above weight parts with stirring for 1-2 hours, are dried in a blast air oven with the temperature
maintaining at 100-105°C for a period of 12-24 hours, until the mass is constant;
o (4) Shaping: the dried fine materials from step (3) are pressed into shape in a tablet press at a shaping pressure greater than 3 MPa, to get complexes of raw materials;
(5) Slurry preparation: the sieved sludge powder is mixed with water at a solid-to-liquid
ratio in a range of 1:1-1:3, to produce sludge slurry;
(6) Slurry wrapping: the complex green bodies of raw materials obtained from step (4) are
bound with the sludge slurry produced in step (5) evenly, so that the surfaces of the complex
green bodies are wetted with the sludge slurry fully and then ready for sintering;
(7) Sintering: the complexes of raw materials from step (6) are sintered, during which air is
charged at a velocity of 50-100 ml/min and the temperature and the heating rate are changed so
that the complexes of raw materials expand at high temperature; and upon the completion of
J sintering, they are cooled to room temperature to get the shaped ceramsite.
Further, the sintering temperature is 1000-1200°C, and air atmosphere is charged into the
furnace. After sintering, expansive porous structures are obtained. The outer surface of the
product has a tight and smooth structure and is dark brown, and there are many air holes inside
the product.
According to a first aspect there is provided a method of increasing the thickness of the
outer enamel layer of ceramsite with sludge slurry, wherein, the ceramsite includes sludge, fly
ash and coal gangue in the following parts by weight: 60-80 parts of sludge, 10-20 parts of fly
ash, and 10-20 parts of coal gangue.
Preferably, the chemical compositions of the three raw materials are respectively:
o - Sludge after incineration lost: A1 2 0 3 27.3%, Si02 34.6%, P 2 05 15.9%, Fe203 6.4%, CaO 6.2%, and others 7.8%;
- Fly ash: A1 2 0 3 18.3%, Si02 43.4%, CaO 24.3%, and others 10.1%;
- Coal gangue: A12 0 3 38.3%, Si02 59.5%, Fe203 0.6%, CaO 0.2%, and others 1.4%.
Preferably, the method includes the following steps:
(1) Drying: Mechanically dehydrated sludge, coal gangue and fly ash are dried in a blast
air oven with the temperature maintaining at 100-105°C for a period of 48-72 hours respectively,
until the mass is constant;
(2) Crushing: the three materials in step (1) are respectively ground mechanically for 1-2
hours, and sieved over a 100-mesh screen;
o (3) Mixing: the sieved fine materials from step (2) are mixed uniformly following the above weight parts with stirring for 1-2 hours, are dried in a blast air oven with the temperature maintaining at 100-105°C for a period of 12-24 hours, until the mass is constant;
(4) Shaping: the dried fine materials from step (3) are pressed into shape in a tablet press at
a shaping pressure greater than 3 MPa, to get complexes of raw materials;
(5) Slurry preparation: the sieved sludge powder is mixed with water at a solid-to-liquid
ratio in a range of 1:1-1:3, to produce sludge slurry;
(6) Slurry wrapping: the complex green bodies of raw materials obtained from step (4) are
bound with the sludge slurry produced in step (5) evenly, so that the surfaces of the complex
green bodies are wetted with the sludge slurry fully and then ready for sintering;
9 (7) Sintering: the complexes of raw materials from step (6) are sintered, during which air is
charged at a velocity of 50-100 ml/min and the temperature and the heating rate are changed so
that the complexes of raw materials expand at high temperature; and upon the completion of
sintering, they are cooled to room temperature to get the shaped ceramsite.
Preferably, the sintering temperature in step (7) is 1000-1200°C, air atmosphere is charged
into the furnace for sintering to get expansive porous structures, the outer surface of the product
has a tight and smooth structure and is dark brown, and there are many air holes inside the
product.
The present disclosure has the following beneficial effects:
The outer enamel layer of ceramsite obtained through the solution of the present disclosure
o is smooth, flat and thick. Through the method of the present disclosure, the sintering temperature
of enamel layer on the ceramsite surface is decreased, meanwhile the thickness of enamel layer
is increased, and the resulting shaped ceramsite will have higher compressive strength, lower
water absorptivity, lower specific surface area and good environmental characteristics. Specific
component proportion, heating rate, sintering temperature, as well as the utilization of sludge as
the foaming agent and the expanding agent, all help to promote the expansion of raw materials at
high temperature and improve the quality of products. The present disclosure utilizes one
municipal waste and two industrial wastes to collaboratively prepare artificial ceramsite. The
resulting ceramsite has good performances, which is superior to simple sludge fly ash ceramsite
and has a broad application prospect. The method of the present disclosure turns sludge and other
o wastes into wealth and recycles resources, which is an environmentally friendly and economically meaningful method.
In order to make the objective, the technical solution and advantages of the present
disclosure more clearly, the present disclosure will be further illustrated in more detail
accompanying with the following embodiments. It should be understood that specific
embodiments described herein are only used to interpret the present disclosure, but not intend to
limit it.
Embodiment 1
A method of increasing the thickness of the outer enamel layer of ceramsite with sludge
J slurry, the specific steps of which were as below:
(1) Drying: Dehydrated sludge, coal gangue and fly ash were dried in a blast air oven with
the temperature maintaining at 105°C for a period of 48 hours respectively, until the mass of
materials was constant;
(2) Crushing: the three materials in step (1) were respectively ground mechanically for 2
hours and sieved over a 100-mesh screen, getting fine materials with particle sizes < 0.154 mm;
(3) Mixing: the sieved fine materials from step (2) were mixed with stirring for 1-2 hours
following the weight parts as below: 70 parts of sludge, 15 parts of fly ash and 15 parts of coal
gangue. The content of each chemical component in the mixed material was: A1 2 0 3 27.6%, Si0 2
39.66%, Fe203 4.57%, P2 0 5 11.13%, CaO 8%, and others 9.04%;
o (4) Shaping: the dried fine materials from step (3) were pressed into shape in a type HY-12
infrared tablet press at a shaping pressure of 6 MPa, to get cylindrical complexes of raw
materials with diameters of 10 mm and heights of 5 mm;
(5) Slurry preparation: the sieved sludge powder was mixed with water at a mass ratio of
1:2, to produce sludge slurry;
(6) Slurry wrapping: the complex green bodies of raw materials obtained from step (4)
were bound with the sludge slurry produced in step (5) evenly, so that the surfaces of the
complex green bodies were wetted with the sludge slurry fully and then ready for sintering;
(7) Sintering: the complexes of raw materials from step (6) were sintered, for which the
complexes of raw materials were preheated and sintered in a single zone atmosphere tube
o furnace that was connected to an air flow meter through an air compressor, and the air atmosphere was charged into the furnace at a velocity of 100 ml/min. During preheating period, the complexes of raw materials were heated to 500°C at a heating rate of 5°C/min, and then sintered by heating, during which they were heated to 800°C at a heating rate of10°C/min, then heated to 1000°C at a heating rate of 5°C/min, then heated to 1235°C at a heating rate of
3°C/min, and kept for 35 min. Upon the completion of sintering, they were cooled to 100°C at a
rate of 10°C/min, taken out with a high temperature clamp and cooled naturally to room
temperature to get the ceramsite 1.
It was determined that the ceramsite 1 has a compressive strength of 5.37 MPa, a water
absorptivity of 0.8%, and a specific surface area of 1.92 g/cm 3. They all met the national
J standard GB/T17431.1-2010 of density grade of 876 kg/m3 and were superior to the standard of
"Grade One Product". The ceramsite 1 was ground, and extracted by mixing with an extractant
(glacial acetic acid solution), and shaken by a flip oscillator for a period of 48 hours with the
temperature maintaining at 26-28°C. The extracted supernatant was tested for the concentration
of heavy metals. The leaching concentration of each heavy metal in the ceramsite 1 was
determined: Cr 0.050 mg/L, Ni 0.161 mg/L, Cu 6.928 mg/L, Zn 1.739 mg/L, all meeting the
national standards.
Embodiment 2
A method of increasing the thickness of the outer enamel layer of ceramsite with sludge
slurry, the specific steps of which were as below:
o (1) Drying: Dehydrated sludge, coal gangue and fly ash were dried in a blast air oven with
the temperature maintaining at 100-105°C for a period of 48 hours respectively, until the mass of
materials was constant;
(2) Crushing: the three materials in step (1) were respectively ground mechanically for 1-2
hours and sieved over a 100-mesh screen, getting fine materials with particle sizes < 0.154 mm;
(3) Mixing: the sieved fine materials from step (2) were mixed with stirring for 1 hour
following the weight parts as below: 80 parts of sludge, 10 parts of fly ash and 10 parts of coal
gangue. The content of each chemical component in the mixed material was: A1 2 0 3 27.5%, SiO 2
37.97%, Fe203 5.18%, P2 0 5 12.72%, CaO 7.41%, and others 10.33%;
(4) Shaping: the dried fine materials from step (3) were pressed into shape in a type HY-12
o infrared tablet press at a shaping pressure of 6 MPa, to get cylindrical complexes of raw materials with diameters of 10 mm and heights of 5 mm;
(5) Slurry preparation: the sieved sludge powder was mixed with water at a mass ratio of
1:1.5, to produce sludge slurry;
(6) Slurry wrapping: the complex green bodies of raw materials obtained from step (4)
were bound with the sludge slurry produced in step (5) evenly, so that the surfaces of the
complex green bodies were wetted with the sludge slurry fully and then ready for sintering;
(7) Sintering: the complexes of raw materials were preheated and sintered in a single zone
atmosphere tube furnace that was connected to an air flow meter through an air compressor, and
the air atmosphere was charged into the furnace at a velocity of 100 ml/min. During preheating
J period, the complexes of raw materials were heated to 500°C at a heating rate of 5°C/min, and
then sintered by heating, during which they were heated to 800°C at a heating rate of10°C/min,
then heated to 1000°C at a heating rate of 5°C/min, then heated to 1235°C at a heating rate of
3°C/min, and kept for 35 min. Upon the completion of sintering, they were cooled to 100°C at a
rate of 10°C/min, taken out with a high temperature clamp and cooled naturally to room
temperature to get the ceramsite 2.
It was determined that the ceramsite 2 has a compressive strength of 6.22 MPa, a water
absorptivity of 0.71%, and a specific surface area of 1.83 g/cm3 . They all met the national
standard GB/T17431.1-2010 of density grade of 876 kg/m3 and were superior to the standard of
"Grade One Product". The ceramsite 2 was ground, and extracted by mixing with an extractant
(glacial acetic acid solution), and shaken by a flip oscillator for a period of 48 hours with the
temperature maintaining at 26-28°C. The extracted supernatant was tested for the concentration
of heavy metals. The leaching concentration of each heavy metal in the ceramsite 2 was
determined: Cr 0.039 mg/L, Ni 0.168 mg/L, Cu 0.027 mg/L, Zn 0.110 mg/L, all meeting the
national standards.
It can be seen from the above embodiments that various performances of the sintered products were superior to those of simple sludge, fly ash or coal gangue ceramsite, and the
ceramsite sintered after binding and wrapping processes may produce more outer enamel layer
compared to ordinary ceramsite; moreover, the enamel layer of the ceramsite was more smooth,
flat, full and thick, which may provide higher compressive strength and lower water absorptivity.
o Wherein, the compressive strength was enhanced by 37.03-88.71% relatively; the water absorptivity was reduced by 11.57-19.38% relatively; and the leaching concentration of each heavy metal also decreased, meanwhile the average temperature of sintering and shaping was reduced by 100-200°C, which greatly reduced the production cost. The reasons lie in that fly ash and coal gangue contain a high proportion of SiO 2 , and coal gangue contains a high content of
A120 3 , molten matrix is easily formed on the surface of complex green bodies at high
temperature, which increases the viscosity of the surface and it is more prone to form full and
porous ceramsite structures. On the other hand, a high content of aluminosilicate mineral can
effectively inhibit the migration and leaching of heavy metals and reduce the damages to the
environment.
J The above disclosed preferred embodiments of the present disclosure are only used to
assist in elaborating the present disclosure. The preferred embodiments do not describe all the
details in detail, and not limit the present disclosure to the specific implementation ways
described herein. Obviously, many modifications and variations can be made according to the
context of the description. These embodiments are chosen and described concretely in the
description of the present disclosure to better illustrate the principle and actual application of the
present disclosure, so that those of skills in the art can understand and utilize the present
disclosure better. The present disclosure is only limited by the claims as well as the full scope
and equivalents thereof.
2021100066
Claims (4)
1. A method of increasing the thickness of the outer enamel layer of ceramsite with sludge
slurry, wherein, the ceramsite includes three raw materials, the three raw materials
including sludge, fly ash and coal gangue in the following parts by weight: 60-80 parts of
sludge, 10-20 parts of fly ash, and 10-20 parts of coal gangue.
2. The method as claimed in claim 1, wherein, the chemical compositions of the three raw
materials are respectively:
- Sludge ash after incineration: A1 2 0 3 27.3%, SiO 2 34.6%, P 2 05 15.9%, Fe203 6.4%,
CaO 6.2%, and others 7.8%;
- fly ash: A1 2 0 3 18.3%, SiO 2 43.4%, CaO 24.3%, and others 10.1%;
- coal gangue: A1 2 0 3 38.3%, SiO 2 59.5%, Fe203 0.6%, CaO 0.2%, and others 1.4%.
3. The method as claimed in claim 1 or claim 2, including the following steps:
(1) Drying: Mechanically dehydrated sludge, coal gangue and fly ash are dried in a blast
air oven with the temperature maintaining at 100-105°C for a period of 48-72 hours
respectively, until the mass is constant;
(2) Crushing: the three materials in step (1) are respectively ground mechanically for 1-2
hours, and sieved over a 100-mesh screen;
(3) Mixing: the sieved fine materials from step (2) are mixed uniformly following the
above weight parts with stirring for 1-2 hours, are dried in a blast air oven with the
temperature maintaining at 100-105°C for a period of 12-24 hours, until the mass is
constant;
(4) Shaping: the dried fine materials from step (3) are pressed into shape in a tablet press at
a shaping pressure greater than 3 MPa, to get complexes of raw materials;
(5) Slurry preparation: the sieved sludge powder is mixed with water at a solid-to-liquid
ratio in a range of 1:1-1:3, to produce sludge slurry;
(6) Slurry wrapping: the complex green bodies of raw materials obtained from step (4) are
bound with the sludge slurry produced in step (5) evenly, so that the surfaces of the
complex green bodies are wetted with the sludge slurry fully and then ready for
sintering;
(7) Sintering: the complexes of raw materials from step (6) are sintered, during which air is
charged at a velocity of 50-100 ml/min and the temperature and the heating rate are
changed so that the complexes of raw materials expand at high temperature; and upon
the completion of sintering, they are cooled to room temperature to get the shaped
ceramsite.
4. The method as claimed in claim 3, wherein, the sintering temperature in step (7) is
1000-1200°C, air atmosphere is charged into the furnace for sintering to get expansive
porous structures, the outer surface of the product has a tight and smooth structure and is
dark brown, and there are many air holes inside the product.
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Cited By (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN113200731A (en) * | 2021-05-27 | 2021-08-03 | 中国十七冶集团有限公司 | Solid waste base non-fired high-strength ceramsite and preparation method thereof |
CN113264717A (en) * | 2021-06-11 | 2021-08-17 | 东北大学 | Large-mixing-amount solid waste base-activated foam concrete and preparation method thereof |
CN113603496A (en) * | 2021-08-19 | 2021-11-05 | 北京大学 | Ceramsite prepared from high-content coal-based solid waste and preparation method thereof |
CN113880477A (en) * | 2021-08-31 | 2022-01-04 | 江西盖亚环保科技有限公司 | Building ceramsite prepared from fly ash, sludge and slag and preparation process thereof |
CN114804910A (en) * | 2022-06-02 | 2022-07-29 | 许泽胜 | Industrial and agricultural urban solid waste ceramsite and preparation method and application thereof |
CN115849935A (en) * | 2022-11-11 | 2023-03-28 | 中国恩菲工程技术有限公司 | Preparation method of coal gangue based high-strength ceramsite |
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2021
- 2021-01-07 AU AU2021100066A patent/AU2021100066A4/en active Active
Cited By (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN113200731A (en) * | 2021-05-27 | 2021-08-03 | 中国十七冶集团有限公司 | Solid waste base non-fired high-strength ceramsite and preparation method thereof |
CN113200731B (en) * | 2021-05-27 | 2022-09-27 | 中国十七冶集团有限公司 | Solid waste base non-fired high-strength ceramsite and preparation method thereof |
CN113264717A (en) * | 2021-06-11 | 2021-08-17 | 东北大学 | Large-mixing-amount solid waste base-activated foam concrete and preparation method thereof |
CN113603496A (en) * | 2021-08-19 | 2021-11-05 | 北京大学 | Ceramsite prepared from high-content coal-based solid waste and preparation method thereof |
CN113880477A (en) * | 2021-08-31 | 2022-01-04 | 江西盖亚环保科技有限公司 | Building ceramsite prepared from fly ash, sludge and slag and preparation process thereof |
CN114804910A (en) * | 2022-06-02 | 2022-07-29 | 许泽胜 | Industrial and agricultural urban solid waste ceramsite and preparation method and application thereof |
CN115849935A (en) * | 2022-11-11 | 2023-03-28 | 中国恩菲工程技术有限公司 | Preparation method of coal gangue based high-strength ceramsite |
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