CN101905954B - Binding material prepared from construction waste and preparation method thereof - Google Patents
Binding material prepared from construction waste and preparation method thereof Download PDFInfo
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- CN101905954B CN101905954B CN2010102305646A CN201010230564A CN101905954B CN 101905954 B CN101905954 B CN 101905954B CN 2010102305646 A CN2010102305646 A CN 2010102305646A CN 201010230564 A CN201010230564 A CN 201010230564A CN 101905954 B CN101905954 B CN 101905954B
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- 239000000463 material Substances 0.000 title claims abstract description 84
- 239000002699 waste material Substances 0.000 title claims abstract description 77
- 238000002360 preparation method Methods 0.000 title claims description 12
- 238000010276 construction Methods 0.000 title abstract description 11
- CDBYLPFSWZWCQE-UHFFFAOYSA-L Sodium Carbonate Chemical compound [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 claims abstract description 28
- 239000002893 slag Substances 0.000 claims abstract description 28
- 238000000034 method Methods 0.000 claims abstract description 17
- PMZURENOXWZQFD-UHFFFAOYSA-L Sodium Sulfate Chemical compound [Na+].[Na+].[O-]S([O-])(=O)=O PMZURENOXWZQFD-UHFFFAOYSA-L 0.000 claims abstract description 14
- DIZPMCHEQGEION-UHFFFAOYSA-H aluminium sulfate (anhydrous) Chemical compound [Al+3].[Al+3].[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O DIZPMCHEQGEION-UHFFFAOYSA-H 0.000 claims abstract description 14
- 239000010881 fly ash Substances 0.000 claims abstract description 14
- 229910000029 sodium carbonate Inorganic materials 0.000 claims abstract description 14
- 229910052938 sodium sulfate Inorganic materials 0.000 claims abstract description 14
- 235000011152 sodium sulphate Nutrition 0.000 claims abstract description 14
- OBSZRRSYVTXPNB-UHFFFAOYSA-N tetraphosphorus Chemical compound P12P3P1P32 OBSZRRSYVTXPNB-UHFFFAOYSA-N 0.000 claims abstract description 14
- 239000000654 additive Substances 0.000 claims abstract description 13
- 239000002994 raw material Substances 0.000 claims abstract description 10
- 230000000996 additive effect Effects 0.000 claims abstract description 9
- 239000000843 powder Substances 0.000 claims description 17
- 235000017550 sodium carbonate Nutrition 0.000 claims description 13
- 238000013467 fragmentation Methods 0.000 claims description 6
- 238000006062 fragmentation reaction Methods 0.000 claims description 6
- 239000004033 plastic Substances 0.000 claims description 6
- 229920003023 plastic Polymers 0.000 claims description 6
- 238000012545 processing Methods 0.000 claims description 6
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 claims description 4
- 239000004411 aluminium Substances 0.000 claims description 2
- 229910052782 aluminium Inorganic materials 0.000 claims description 2
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 claims description 2
- 239000011449 brick Substances 0.000 abstract description 13
- 239000004568 cement Substances 0.000 abstract description 11
- 230000004913 activation Effects 0.000 abstract description 6
- 239000000126 substance Substances 0.000 abstract description 4
- 238000004137 mechanical activation Methods 0.000 abstract description 3
- 238000004134 energy conservation Methods 0.000 abstract description 2
- 235000019738 Limestone Nutrition 0.000 abstract 1
- 238000005265 energy consumption Methods 0.000 abstract 1
- 239000006028 limestone Substances 0.000 abstract 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 11
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 10
- 238000012360 testing method Methods 0.000 description 10
- 239000004567 concrete Substances 0.000 description 8
- 230000006835 compression Effects 0.000 description 6
- 238000007906 compression Methods 0.000 description 6
- 238000004519 manufacturing process Methods 0.000 description 6
- 238000011056 performance test Methods 0.000 description 6
- 229910052742 iron Inorganic materials 0.000 description 5
- 238000004064 recycling Methods 0.000 description 5
- 238000005516 engineering process Methods 0.000 description 4
- 238000012423 maintenance Methods 0.000 description 4
- 239000000203 mixture Substances 0.000 description 4
- 239000004570 mortar (masonry) Substances 0.000 description 4
- 238000001514 detection method Methods 0.000 description 3
- 238000000465 moulding Methods 0.000 description 3
- 230000008929 regeneration Effects 0.000 description 3
- 238000011069 regeneration method Methods 0.000 description 3
- 238000011160 research Methods 0.000 description 3
- 238000003756 stirring Methods 0.000 description 3
- 235000008733 Citrus aurantifolia Nutrition 0.000 description 2
- 235000011941 Tilia x europaea Nutrition 0.000 description 2
- 239000010426 asphalt Substances 0.000 description 2
- 238000003763 carbonization Methods 0.000 description 2
- 239000004571 lime Substances 0.000 description 2
- 238000002156 mixing Methods 0.000 description 2
- 239000010813 municipal solid waste Substances 0.000 description 2
- 239000011734 sodium Substances 0.000 description 2
- 235000017166 Bambusa arundinacea Nutrition 0.000 description 1
- 235000017491 Bambusa tulda Nutrition 0.000 description 1
- 241001330002 Bambuseae Species 0.000 description 1
- 235000015334 Phyllostachys viridis Nutrition 0.000 description 1
- 239000011425 bamboo Substances 0.000 description 1
- 238000009412 basement excavation Methods 0.000 description 1
- 239000004566 building material Substances 0.000 description 1
- 239000000567 combustion gas Substances 0.000 description 1
- 238000002485 combustion reaction Methods 0.000 description 1
- 238000005202 decontamination Methods 0.000 description 1
- 230000003588 decontaminative effect Effects 0.000 description 1
- 238000005034 decoration Methods 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 230000018109 developmental process Effects 0.000 description 1
- 239000000428 dust Substances 0.000 description 1
- 239000012634 fragment Substances 0.000 description 1
- 238000000227 grinding Methods 0.000 description 1
- 238000009413 insulation Methods 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 239000002245 particle Substances 0.000 description 1
- 238000000197 pyrolysis Methods 0.000 description 1
- 230000001172 regenerating effect Effects 0.000 description 1
- 239000004576 sand Substances 0.000 description 1
- 238000005245 sintering Methods 0.000 description 1
- 239000002689 soil Substances 0.000 description 1
- 239000002910 solid waste Substances 0.000 description 1
- 239000004575 stone Substances 0.000 description 1
- 238000003860 storage Methods 0.000 description 1
- 238000009423 ventilation Methods 0.000 description 1
Images
Classifications
-
- 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
- C04B7/00—Hydraulic cements
- C04B7/24—Cements from oil shales, residues or waste other than slag
- C04B7/246—Cements from oil shales, residues or waste other than slag from waste building materials, e.g. waste asbestos-cement products, demolition waste
-
- 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
- C04B2111/00—Mortars, concrete or artificial stone or mixtures to prepare them, characterised by specific function, property or use
- C04B2111/00474—Uses not provided for elsewhere in C04B2111/00
- C04B2111/0075—Uses not provided for elsewhere in C04B2111/00 for road construction
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P40/00—Technologies relating to the processing of minerals
- Y02P40/10—Production of cement, e.g. improving or optimising the production methods; Cement grinding
Abstract
The invention provides a binding material prepared from construction waste, which consists of the following components in part by mass: 80 to 90 parts of construction waste, 10 to 30 parts of auxiliary material, and 1.0 to 2.8 parts of additive, wherein the auxiliary material is one or both of yellow phosphorus slag and flyash, or one or both of lime stone and carbide slag; and the additive is two or three of 0.5 to 1 part of aluminum sulfate, 0.2 to 0.6 part of sodium sulfate and 0.5 to 1.2 parts of sodium carbonate. The hydraulic binding material produced by high temperature activation, mechanical activation and chemical activation can replace cement to be widely applied to producing baking-free bricks and roadbase materials. The binding material has the advantages of conveniently available raw materials, low cost, energy conservation and consumption reduction; and compared with the traditional cementing material, the binding material has the same using method and is convenient to promote and apply.
Description
Technical field
The present invention relates to a kind of recycling of building waste, specifically a kind of gelling material that building waste processes and preparation method thereof of utilizing belongs to the material of construction preparing technical field.
Background technology
Building waste is the solid waste that produces in the construction, maintenance, demolishing process at buildings; Comprise waste material, various wrapping material and other wastes etc. that the mortar that is scattered in waste concrete piece, useless fragment of brick, bituminous concrete piece, the construction process and concrete, brickbat slag, metal, bamboo timber, decorations produce, its staple is main with concrete and sintering common brick.
In Europe, developed country such as U.S.A, day, the recycling of building waste has become the hot issue of present research.To the building waste of different sources and composition, processing mode is different, like the CYCLEAN company of the U.S. building waste to road excavation, adopts microwave technology, reclaims the old asphalt pavement material, and its quality is with newly to mix asphalt road surface material identical, and cost can reduce by 1/3.And the building waste that building demolition is obtained, Singapore is then building waste recycling be processed into iron, timber, leatheroid etc.To pretreated building waste, handle according to its composition, to material of construction such as concrete, sand, stones,, produce recycled cement and regeneration aggregate through certain means preparation material of construction of regenerating.And to flammable building waste, the destructive distillation combustion refuse treatment process of Siemens exploitation can make the various recyclable materials in the rubbish very separate neatly, is recycled, and the combustion gas that produces in the treating processes then is used for generating.Generally speaking, the recycling of building waste has all been obtained substantial progress from theoretical and actual two aspects abroad.
In China, the recycling of building waste has also caused numerous investigators' attention and has carried out big quantity research.In general, its basic ideas are carries out sorting with building waste, thereby carries out classified use, different according to investigator's research object, has obtained a large amount of theoretical property conclusions.As with blue bricks or common brick particle as light-weight aggregate, be aided with less fine aggregate of density or powder again, can make cement products such as better road brick of light in structure aggregate concrete member, ventilation property with load-bearing, heat insulation function and ornamental slab for paving the floor.As with sorting after the waste and old concrete fragmentation, modification is as regeneration aggregate; Waste and old mortar is pulverized the back be used as dry-mixed mortar etc.In the application facet of reality, real mass-producing utilizes the report of building waste, and is at present domestic less.
Analyzing China's building waste treatment technology can find; Although China's building waste is handled thinking and external basically identical; But on concrete technology and implement scale, still be in the junior stage, also do not having sophisticated mass-producing and the complete technological line that utilizes for the urban architecture rubbish of a large amount of complicated components.
At present, the quantity of China's building waste has accounted for 40%~50% of municipal wastes total amount.And most building wastes are handled with the mode of air storage or landfill, consume a large amount of soils, bury great potential safety hazard also for people's living environment.Therefore, building waste being recycled, turned waste into wealth, is to solve the building waste optimal path, also is simultaneously the effective way that economizes on resources, protects existing fragile ecological environment.Because the chemical constitution and the mineralogical character of building castoff are developed its recycle utilization at building field, can finally solve the handling problem of building waste.Amount of literature data shows, utilizes building waste to produce the adulterant of non-burning brick, roadbase, the steady layer of water, regeneration aggregate, dry-mixed mortar, manufacture of cement, is the focus of studying at present.
Say from the meaning of Eco-economy System; Waste is " resource that has misplaced the position "; It is recycled to produce building material, is decontamination, makes one of main method of its resource utilization; Not only can alleviate the pressure of China's urban environment load, also can realize Sustainable development economic and society.
Comprehensive existing document can be found out: aspect building waste production gelling material, mainly be in the form adding grog with adulterant, compare with the cement of producing equal label, reduce the grog parameter; Simultaneously, because its grindability is practiced thrift power consumption.Therefore, can reduce the manufacture of cement cost, reach the purpose of energy-saving and emission-reduction.It is gelling material with cement mainly that building waste is produced non-burning brick, is aided with other industrial slag, under natural or steam-cured condition, produces non-burning brick.When producing road basement material with building waste, building waste mainly is that its gelling material then adopts cement, lime, flyash etc. as aggregate.With the building waste is main raw, and through high-temperature activation, mechanical activation and chemical activation, preparation has the gelling material of the hydraulicity, does not appear in the newspapers yet and leads.
Summary of the invention
The object of the present invention is to provide a kind of gelling material of processing with building waste.
Another object of the present invention is to provide a kind of method with building waste production gelling material.
First purpose of the present invention is accomplished through following technical proposal: a kind of gelling material of processing with building waste is characterized in that being made up of following mass component:
80~90 parts of building wastes
10~30 parts of subsidiary material
1.0~2.8 parts of additives
Said subsidiary material are one or both and yellow phosphorus furnace slag, in the flyash one or both in Wingdale, the carbide slag;
Said additive is two or three in Tai-Ace S 150, sodium sulfate, the yellow soda ash, makes Na wherein
2O: SO
4=1: 0.2~0.5 mass ratio.
Second purpose of the present invention realizes through following technical proposal: a kind of method with building waste production gelling material; It is main raw material with the building waste; With lime or/and carbide slag and yellow phosphorus furnace slag or/and flyash is subsidiary material; Be additive with Tai-Ace S 150, sodium sulfate, yellow soda ash again; Produce hydraulic cementing materials through high-temperature activation, mechanical activation and chemical activation, can replace cement to be widely used in and produce non-burning brick, road basement material, it is characterized in that through the following step:
A. get the raw materials ready by following mass component:
80~90 parts of building wastes
10~30 parts of subsidiary material
1.0~2.8 parts of additives
Wherein:
Said subsidiary material are one or both in Wingdale, the carbide slag, and in the yellow phosphorus furnace slag, flyash one or both;
Said additive is two or three in Tai-Ace S 150, sodium sulfate, the yellow soda ash, makes Na wherein
2O: SO
4=1: 0.2~0.5 mass ratio;
B. in building waste that steps A was equipped with and subsidiary material Wingdale, the carbide slag one or both are mixed, at 800~900 ℃ of roasting temperature 1~3h, roasting material;
C. with step B gained roasting material, the subsidiary material yellow phosphorus furnace slag that is equipped with steps A, in the flyash one or both, and two or three in the additive sulfuric acid aluminium, sodium sulfate, yellow soda ash mixes, levigate to granularity less than 0.083mm, the gelling material powder.
Said building waste is a building castoff of removing plastics, timber and daily necessities, and it is crushed to granularity is 5~50mm, and with ordinary method and equipment deironing.
Said Wingdale is the Wingdale through fragmentation, and granularity is 5~30mm.
The examination of the performance of gained gelling material can be through following method:
(1) non-burning brick preparation: with 10~20 parts in step C gained gelling material powder, granularity is 80~90 parts of the building wastes of 0.2~2mm, 13~15 parts in water; Mix and stir; Get green compact with conventional shaper moulding, again with green compact after conventional natural curing or vapor cure, non-burning brick; Through conventional performance test is qualified, and provable thus step C gained gelling material powder is qualified.
(2) road basement material preparation: with 5~10 parts in step C gained gelling material powder; Granularity is 85~90 parts of the building wastes of 0.2~20mm; 5~15 parts in water; Through mixing 3 minutes, the preparation aspect ratio is 1 right cylinder test specimen under the forming pressure of 2MPa, carries out the maintenance and the performance test of test specimen according to the demand of technical standard of " highway road surface construction technique normalizing " JTJ034-2000 roadbase and subbase; Get qualified road basement material, provable thus step C gained gelling material powder is qualified.
The present invention compared with prior art has following advantage:
1) gelling material of the present invention's production has hydraulicity characteristics, and raw material sources are convenient, and cost is low, and is energy-saving and cost-reducing.
2) compare with traditional cement cementitious material, the present invention is main raw material with the building waste, and maturing temperature is low, and the time is short, and roasting material is prone to grinding, energy-conservation power saving again.
3) compare with traditional cement cementitious material, method of use is identical, is convenient to it and applies.
4) the non-burning brick and road basement material of preparing with gelling material provided by the invention, performance satisfies the respective standard requirement.
Description of drawings
Fig. 1 is technical process of the present invention.
Embodiment
Embodiment 1
A. get the raw materials ready by following mass component:
Building waste 80kg carbide slag 5kg
Yellow phosphorus furnace slag 10kg Tai-Ace S 150 0.5kg
Yellow soda ash 0.5kg
Wherein:
Building waste is a building removal waste of removing plastics, timber and daily necessities, is 5mm through being crushed to granularity, removes iron wherein with conventional magnet machine magnetic;
B. building waste that steps A is equipped with is mixed with carbide slag,, obtain roasting material at 850 ℃ of roasting 1h of maturing temperature;
C. step B gained roasting material is mixed with yellow phosphorus furnace slag that steps A is equipped with, Tai-Ace S 150, yellow soda ash, levigate to granularity less than 0.083mm, be the gelling material powder;
Performance Detection: with step C gained gelling material powder 20kg; Granularity is the building waste 80kg of 0.2mm; Water 15kg after mixing stirring, gets green compact with conventional block machine moulding; Green compact were through natural curing 10 days; Carry out performance test, test result: mean compressive strength 10.67MPa, average folding strength 2.67MPa, water-intake rate 14.12%, carbonization coefficient 81.37%, coefficient of softening 85.62%, 25 freeze-thaw cycle ultimate compression strength losses 8.6%, mass losses are 1.36%, prove that thus step C gained gelling material powder is qualified.
Embodiment 2
A. get the raw materials ready by following mass component:
Building waste 90kg Wingdale 5kg
Yellow phosphorus furnace slag 5kg flyash 10kg
Tai-Ace S 150 1kg sodium sulfate 0.6kg
Wherein:
Building waste is a building removal waste of removing plastics, timber and daily necessities, is 50mm through being crushed to granularity, removes iron wherein with conventional magnet machine magnetic; Wingdale is the Wingdale through fragmentation, and granularity is 30mm;
B. with being equipped with building waste in the steps A and Wingdale mixes,, obtain roasting material with 900 ℃ of roasting 2h of maturing temperature;
C. carry out abrasive dust with being equipped with yellow phosphorus furnace slag, Tai-Ace S 150, sodium sulfate in gained roasting material and the steps A among the step B, be milled to powder granularity, promptly obtain the gelling material powder less than 0.083mm;
The performance examination: get gelling material 10kg described in the step C, getting granularity is the building waste 90kg of 2mm, adds water 13kg; Stir the back and use the block machine moulding; Green compact carry out performance test, test result through normal pressure vapor cure 18 hours: mean compressive strength 12.21MPa, average folding strength 3.17MPa; Water-intake rate 12.10%, carbonization coefficient 83.40%, coefficient of softening 86.31%; 25 freeze-thaw cycle ultimate compression strength losses 7.7%, mass loss is 1.37%, provable thus step C gained gelling material powder is qualified.
Embodiment 3
A. get the raw materials ready by following mass component:
Building waste 85kg Wingdale 2kg
Carbide slag 3kg yellow phosphorus furnace slag 3kg
Flyash 5kg Tai-Ace S 150 0.7kg
Sodium sulfate 0.3kg yellow soda ash 1.0kg
Wherein:
Building waste is a building removal waste of removing plastics, timber and daily necessities, is 25mm through being crushed to granularity again, removes iron wherein with conventional magnet machine magnetic; Wingdale is the Wingdale through fragmentation, and granularity is 5mm.
B. with being equipped with building waste in the steps A and Wingdale, carbide slag mix,, obtain roasting material with 800 ℃ of roasting 3h of maturing temperature;
C. step B gained roasting material is mixed with yellow phosphorus furnace slag that steps A is equipped with, flyash, Tai-Ace S 150, sodium sulfate, yellow soda ash, levigate to granularity less than 0.083mm, promptly obtain the gelling material powder;
Performance Detection: get gelling material 10kg described in the step C; With granularity is that to be crushed to granularity once more be 0.2~20mm to 5~50mm building waste; Get 90kg, add water 15kg, stirred 3 minutes through biaxial rneader; The preparation aspect ratio is 1 right cylinder test specimen under the forming pressure of 2MPa; Carry out the maintenance and the performance test of test specimen according to the demand of technical standard of " highway road surface construction technique normalizing " JTJ034-2000 roadbase and subbase, test result: 7 days unconfined compression strength 1.31MPa, the steady coefficient 77.40% of water; 28 days unconfined compression strength 8.47MPa, the steady coefficient 89.10% of water, provable thus step C gained gelling material powder is qualified.
Embodiment 4
A. get the raw materials ready by following mass component:
Building waste 87kg Wingdale 5kg
Flyash 5kg Tai-Ace S 150 0.9kg
Sodium sulfate 0.8kg yellow soda ash 1.1kg
Wherein:
Building waste is a building removal waste of removing plastics, timber and daily necessities, is 28mm through being crushed to granularity again, removes iron wherein with conventional magnet machine magnetic; Wingdale is the Wingdale through fragmentation, and granularity is 10mm;
B. building waste that steps A is equipped with and Wingdale are mixed,, obtain roasting material at 820 ℃ of roasting 3h of maturing temperature;
C. step B gained roasting material is mixed with flyash that steps A is equipped with, Tai-Ace S 150, sodium sulfate, yellow soda ash, levigate to granularity less than 0.083mm, promptly obtain the gelling material powder;
Performance Detection: get gelling material 5kg described in the step C; With granularity is that to be crushed to granularity once more be 0.2~20mm to 5~50mm building waste; Get 85kg, add water 5kg, stirred 3 minutes through biaxial rneader; The preparation aspect ratio is 1 right cylinder test specimen under the forming pressure of 2MPa; Carry out the maintenance and the performance test of test specimen according to the demand of technical standard of " highway road surface construction technique normalizing " JTJ034-2000 roadbase and subbase, test result: 7 days unconfined compression strength 1.38MPa, the steady coefficient 77.58% of water; 28 days unconfined compression strength 8.86MPa, the steady coefficient 89.92% of water, provable thus step C gained gelling material powder is qualified.
Claims (3)
1. gelling material of processing with building waste is characterized in that being made up of following mass component:
80~90 parts of building wastes
10~30 parts of subsidiary material
1.0~2.8 parts of additives
Wherein:
Said subsidiary material are one or both in yellow phosphorus furnace slag, the flyash, and in the Wingdale, carbide slag one or both;
Said additive is two or three in Tai-Ace S 150, sodium sulfate, the yellow soda ash.
2. the preparation method of a gelling material of processing with building waste is characterized in that through the following step:
A. get the raw materials ready by following mass component:
80~90 parts of building wastes
10~30 parts of subsidiary material
1.0~2.8 parts of additives
Wherein:
Said building waste is a building castoff of removing plastics, timber and daily necessities, is 5~50mm through being crushed to granularity again, by ordinary method and equipment deironing;
Said subsidiary material are one or both in Wingdale, the carbide slag, and in the yellow phosphorus furnace slag, flyash one or both;
Said additive is two or three in Tai-Ace S 150, sodium sulfate, the yellow soda ash;
B. in building waste that steps A is equipped with and subsidiary material Wingdale, the carbide slag one or both are mixed,, obtain roasting material at 800~900 ℃ of roasting 1~3h of maturing temperature;
C. with step B gained roasting material, and be equipped with in subsidiary material yellow phosphorus furnace slag, the flyash one or both in the steps A, and two or three in the additive sulfuric acid aluminium, sodium sulfate, yellow soda ash mixes, levigate to granularity less than 0.083mm, the gelling material powder.
3. the preparation method of gelling material according to claim 2 is characterized in that said Wingdale is the Wingdale through fragmentation, and granularity is 5~30mm.
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CN2010102305646A CN101905954B (en) | 2010-07-20 | 2010-07-20 | Binding material prepared from construction waste and preparation method thereof |
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CN101905954B true CN101905954B (en) | 2012-12-05 |
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CN110668741A (en) * | 2019-10-08 | 2020-01-10 | 广东凯恩德环保建材有限公司 | Preparation method of dry-mixed mortar |
CN110757618A (en) * | 2019-10-31 | 2020-02-07 | 梁品 | Method for producing baking-free bricks by comprehensively utilizing furnace slag |
CN113354313B (en) * | 2021-07-05 | 2022-06-28 | 常熟理工学院 | Method for preparing non-fired cement by using concrete waste residues |
CN113354314B (en) * | 2021-07-20 | 2022-03-01 | 深圳市衡骏环保科技有限公司 | High-activity cementing material based on engineering muck |
CN115353331A (en) * | 2022-07-27 | 2022-11-18 | 南京益夫新材料科技有限公司 | Preparation method of regenerated plastering mortar |
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CN1546411A (en) * | 2003-12-11 | 2004-11-17 | 阮炯正 | Clinker-free cement producing process |
CN101423344A (en) * | 2008-08-14 | 2009-05-06 | 武汉理工大学 | Hydraulicity cementitious materials and preparation method thereof |
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