CN107673732A - A kind of production method of dyeing and printing sewage treatment plant firing sludge clinker bricks in environmental protection - Google Patents
A kind of production method of dyeing and printing sewage treatment plant firing sludge clinker bricks in environmental protection Download PDFInfo
- Publication number
- CN107673732A CN107673732A CN201710888552.4A CN201710888552A CN107673732A CN 107673732 A CN107673732 A CN 107673732A CN 201710888552 A CN201710888552 A CN 201710888552A CN 107673732 A CN107673732 A CN 107673732A
- Authority
- CN
- China
- Prior art keywords
- sludge
- brick
- dyeing
- sent
- moisture content
- 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
Links
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
- C04B33/00—Clay-wares
- C04B33/02—Preparing or treating the raw materials individually or as batches
- C04B33/13—Compounding ingredients
- C04B33/132—Waste materials; Refuse; Residues
- C04B33/1321—Waste slurries, e.g. harbour sludge, industrial muds
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/12—Treatment of sludge; Devices therefor by de-watering, drying or thickening
- C02F11/121—Treatment of sludge; Devices therefor by de-watering, drying or thickening by mechanical de-watering
- C02F11/122—Treatment of sludge; Devices therefor by de-watering, drying or thickening by mechanical de-watering using filter presses
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/12—Treatment of sludge; Devices therefor by de-watering, drying or thickening
- C02F11/14—Treatment of sludge; Devices therefor by de-watering, drying or thickening with addition of chemical agents
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/12—Treatment of sludge; Devices therefor by de-watering, drying or thickening
- C02F11/16—Treatment of sludge; Devices therefor by de-watering, drying or thickening using drying or composting beds
-
- 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
- C04B33/00—Clay-wares
- C04B33/02—Preparing or treating the raw materials individually or as batches
- C04B33/13—Compounding ingredients
- C04B33/1305—Organic additives
-
- 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
- C04B33/00—Clay-wares
- C04B33/02—Preparing or treating the raw materials individually or as batches
- C04B33/13—Compounding ingredients
- C04B33/1315—Non-ceramic binders
-
- 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
- C04B33/00—Clay-wares
- C04B33/02—Preparing or treating the raw materials individually or as batches
- C04B33/13—Compounding ingredients
- C04B33/132—Waste materials; Refuse; Residues
- C04B33/1324—Recycled material, e.g. tile dust, stone waste, spent refractory material
-
- 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
- C04B33/00—Clay-wares
- C04B33/02—Preparing or treating the raw materials individually or as batches
- C04B33/13—Compounding ingredients
- C04B33/132—Waste materials; Refuse; Residues
- C04B33/135—Combustion residues, e.g. fly ash, incineration waste
- C04B33/1352—Fuel ashes, e.g. fly ash
-
- 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
- Y02P40/60—Production 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)
- Organic Chemistry (AREA)
- Environmental & Geological Engineering (AREA)
- Materials Engineering (AREA)
- Dispersion Chemistry (AREA)
- Structural Engineering (AREA)
- Hydrology & Water Resources (AREA)
- Water Supply & Treatment (AREA)
- Life Sciences & Earth Sciences (AREA)
- Mechanical Engineering (AREA)
- Combustion & Propulsion (AREA)
- General Chemical & Material Sciences (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Treatment Of Sludge (AREA)
Abstract
The invention discloses a kind of production method of dyeing and printing sewage treatment plant firing sludge clinker bricks in environmental protection, mainly include the following steps that, the drying and other treatment of sludge, be pulverized and mixed uniformly, ageing, insulation brickmaking base, maintenance and roasting.Because the sludge content of organic matter is higher, play a part of pore-foaming agent during high-temperature roasting of the present invention, gained sludge brick is light, insulation sqouynd absorption lowering noise, it is function admirable ecological, environmental protective building brick, sludge can be effectively realized to economy, the environmental and social benefits of sludge treatment for the preparation of building brick;Heavy metal can be converted into indissoluble state or be completely fixed in brick body lattice by high-temperature roasting, so as to reduce potential hazard of the sludge to environment to greatest extent.
Description
Technical field
The invention belongs to Solid Waste Treatment, disposal and application technology as the second resource field, more particularly to a kind of dyeing and printing sewage
The production method for the treatment of plant's firing sludge clinker bricks in environmental protection.
Background technology
Textile industry is one of important national industry in China, in modern economy globalization and the condition of New Sci-and Tech-Revolution
Under, China is going into the period for becoming weaving power by the big country that weaves.Waste water caused by dyeing, accounts for industrial wastewater
The 1/10 of total release.According to incompletely statistics, China there are about 7.2x10 every year8m3Dyeing waste water is discharged into water environment, is current most main
One of pollution source of water body wanted.At present, the processing method of dyeing waste water is still generally based on bioanalysis, Biochemical method effect
Preferably, but can produce substantial amounts of excess sludge simultaneously, produce sludge quantity account for handling water 0.5% or so (using moisture content as
97% meter);In sewage treatment plant, handle sludge expense account for run total cost 20%-50% be even as high as 70% so that spin
Knitting printing and dyeing enterprise needs to put into excessive fund in this respect, but not necessarily obtains preferable treatment effect, and this has become system
An about big key factor of textile industry development.
At present, China is in the period of Process of Urbanization Construction high speed development, and land resource, the energy are all very in short supply, therefore
Making construction material using municipal sludge has vast potential for future development.Not only may be used using sludge as raw material in high-temperature roasting product
So that sludge is realized innoxious, secondary pollution is prevented, and contained organic matter has certain caloric value in sludge, can supplement high temperature
Heat needed for roasting, while unnecessary energy resource consumption is decreased, both it has been beneficial to develop itself benignly circulated economics, discarded object
The recycling and industrialized requirement of processing, while also comply with and forbid ruining field shoveling brickmaking, the principle of cultivated land resource is saved, was both met
The demands of a large amount of construction sintered articles, the state basic policy for the sustainable development for reducing resource consumption that reduces environmental pollution is realized again
Draw and Circular Economy.
The content of the invention
The invention aims to solve shortcoming present in prior art, and a kind of dyeing and printing sewage treatment plant proposed
The production method of firing sludge clinker bricks in environmental protection.
To achieve the above object, the present invention provides following technical scheme:
A kind of production method of dyeing and printing sewage treatment plant firing sludge clinker bricks in environmental protection, comprises the following steps:
S1, sludge drying and other treatment:The sludge that dyeing and printing sewage treatment plant in S1 is shipped to moisture content 85% enters pond, then adds and contain
The sludge water of water rate 97% or so is diluted, and obtains the sludge of moisture content 93%, then adds medicament stirring, then with screw rod high pressure
The sludge slurry of moisture content 93% is sent into sheet frame diaphragm filter press by pump, after high pressure charging, diaphragm pressing, unloads sludge cake automatically,
The drying kiln using roasting tunnel kiln waste heat of baking bricks is sent into through conveyer belt, the dewatered sludge of moisture content 35% is obtained after drying,
Be put in storage the stand-by part material for sintering heat-reserving brick processed;
S2,30-40 part printing and dyeing sludge 15-20 parts flyash, 28-38 parts building waste and the height of 1-2 parts by desiccation
Molecular adhesion agent is respectively charged into apron feeder, according to chemical analysis, carries out by PLC automatically controlling dispensing through electronic measurement,
Slightly broken through hammer coarse breaking machine, then through thin hammer-crusher thin broken, then sieve and be well mixed through rotary screen;
S3, again by weighing balance, with construction waste soil, the mixed of polymeric adhesive and water is added after thick, thin two pairs of rollers
Liquid is closed, controls the moisture content of compound to be sent into ageing storehouse after agitated 20%, it is stand-by after old 3 days;
S4, it will pass through and glued in ageing storehouse desiccation printing and dyeing sludge, flyash, building waste and the macromolecule of old more than 72 hours
Agent mixed powder particle is connect, through multi-bucket excavator feeding, is transported through conveyer belt, raw material is sent into twin rollers and carries out roll-in, broken refinement
Ground with rubbing, then through conveyer belt, into edge runner, increase the fineness and plasticity of compound, then mixer, regulation are sent into through conveyer belt
The moisture content and increase plasticity of compound, then 75 type double roller vacuum hard plastic extruders are sent into through conveyer belt, insulation adobe is made;
S5, the insulation adobe of forming passed through on the full-automatic code of manipulator to kiln car;
S6, by forming insulation adobe by hauling machine be sent into a surrounding use in brick confined space, stop 24
Hour;Atmosphere draught-free, make insulation adobe is fully quiet to stop;Desiccation printing and dyeing sludge, flyash, building waste compound between fully
Bonding, moisture content are sufficiently unanimously homogenized, and adobe surface is not ftractureed, and reach the purpose for improving insulating brick green strength;
S7, the base substrate obtained in S6 is placed in curing with carbon dioxide case conserved, curing time is 2-3 days, is taken out immediately
Obtain no-firing brick;
S8, by the no-firing brick obtained in S7 through drying cart be sent into hothouse be dried, the drying time 65~
85min, 150~190 DEG C of drying temperature, the moisture content of dried no-firing brick is 2~3%;
The no-firing brick that is obtained in S9, S8 is sent into tunnel cave and is calcined, and roasting time is 65~85min, sintering temperature
For 850~1050 DEG C.
Preferably, in S1, medicament is aluminium polychloride sludge conditioner and PAMC sludge conditioning
Agent it is one or two kinds of.
Preferably, roasting process is in the step S9:First baking inphases, when being raised to 80 DEG C from ambient temperature, heating
Speed is 100 DEG C/h, is incubated 30-40min;Second baking inphases, warm temperature is from when being raised to 450 DEG C for 80 DEG C, programming rate
For 120 DEG C/h, 35-40min is incubated;3rd baking inphases, from when being raised to 850 DEG C for 450 DEG C, programming rate is warm temperature
130 DEG C/h, it is incubated 40-50min;4th baking inphases, from when being raised to 1050 DEG C for 850 DEG C, programming rate is warm temperature
150 DEG C/h, 3-4 hours are incubated, extremely into brick;5th baking inphases, when dropping to 100 DEG C from 1050 DEG C, cooling rate 200
DEG C/h, to kiln discharge.
The technique effect and advantage of the present invention:A kind of dyeing and printing sewage treatment plant firing sludge environmental protection sintering provided by the invention
The production method of brick, compared with traditional technology, the present invention has advantages below:
(1) pore-foaming agent is played a part of because the sludge content of organic matter is higher, during high-temperature roasting, gained sludge brick is light,
Insulation sqouynd absorption lowering noise, it is function admirable ecological, environmental protective building brick, the preparation that sludge is used for building brick can be effectively
Realize economy, the environmental and social benefits of sludge treatment;
(2) heavy metal can be converted into indissoluble state or be completely fixed in brick body lattice by high-temperature roasting, so as to greatest extent
Reduce potential hazard of the sludge to environment in ground;
(3) high-temperature roasting can kill thousands of kinds of microorganisms in sludge, solve the problems, such as microorganism pollution environment;
(4) present invention can continuous treatment, improve performance, lifted product specification, it is energy-saving.
Embodiment
In order to make the purpose , technical scheme and advantage of the present invention be clearer, below in conjunction with specific embodiment, to this
Invention is further elaborated.It should be appreciated that the specific embodiments described herein are merely illustrative of the present invention, not
For limiting the present invention.Based on the embodiment in the present invention, those of ordinary skill in the art are not before creative work is made
The every other embodiment obtained is put, belongs to the scope of protection of the invention.
Embodiment 1
A kind of production method of dyeing and printing sewage treatment plant firing sludge clinker bricks in environmental protection, comprises the following steps:
S1, sludge drying and other treatment:The sludge that dyeing and printing sewage treatment plant in S1 is shipped to moisture content 85% enters pond, then adds and contain
The sludge water of water rate 97% or so is diluted, and obtains the sludge of moisture content 93%, then adds medicament stirring, then with screw rod high pressure
The sludge slurry of moisture content 93% is sent into sheet frame diaphragm filter press by pump, after high pressure charging, diaphragm pressing, unloads sludge cake automatically,
The drying kiln using roasting tunnel kiln waste heat of baking bricks is sent into through conveyer belt, the dewatered sludge of moisture content 35% is obtained after drying,
Be put in storage the stand-by part material for sintering heat-reserving brick processed;
S2, by 30 parts of printing and dyeing sludges, 15 parts of flyash, 28 parts of building wastes and 1 part of the polymeric adhesive of desiccation point
Do not load apron feeder, according to chemical analysis, carry out by PLC automatically controlling dispensing through electronic measurement, through hammer coarse breaking machine
It is thick broken, then through thin hammer-crusher thin broken, then sieve and be well mixed through rotary screen;
S3, again by weighing balance, with construction waste soil, the mixed of polymeric adhesive and water is added after thick, thin two pairs of rollers
Liquid is closed, controls the moisture content of compound to be sent into ageing storehouse after agitated 20%, it is stand-by after old 3 days;
S4, it will pass through and glued in ageing storehouse desiccation printing and dyeing sludge, flyash, building waste and the macromolecule of old more than 72 hours
Agent mixed powder particle is connect, through multi-bucket excavator feeding, is transported through conveyer belt, raw material is sent into twin rollers and carries out roll-in, broken refinement
Ground with rubbing, then through conveyer belt, into edge runner, increase the fineness and plasticity of compound, then mixer, regulation are sent into through conveyer belt
The moisture content and increase plasticity of compound, then 75 type double roller vacuum hard plastic extruders are sent into through conveyer belt, insulation adobe is made;
S5, the insulation adobe of forming passed through on the full-automatic code of manipulator to kiln car;
S6, by forming insulation adobe by hauling machine be sent into a surrounding use in brick confined space, stop 24
Hour;Atmosphere draught-free, make insulation adobe is fully quiet to stop;Desiccation printing and dyeing sludge, flyash, building waste compound between fully
Bonding, moisture content are sufficiently unanimously homogenized, and adobe surface is not ftractureed, and reach the purpose for improving insulating brick green strength;
S7, the base substrate obtained in S6 is placed in curing with carbon dioxide case conserved, curing time is 2-3 days, is taken out immediately
Obtain no-firing brick;
S8, by the no-firing brick obtained in S7 through drying cart be sent into hothouse be dried, the drying time 65min,
150 DEG C of drying temperature, the moisture content of dried no-firing brick is 2%;
The no-firing brick obtained in S9, S8 is sent into tunnel cave and is calcined, and roasting process is:First baking inphases, from room
When temperature is raised to 80 DEG C, programming rate is 100 DEG C/h, is incubated 30min;Second baking inphases, warm temperature rise from 80 DEG C
During to 450 DEG C, programming rate is 120 DEG C/h, is incubated 35min;3rd baking inphases, warm temperature are raised to 850 from 450 DEG C
DEG C when, programming rate be 130 DEG C/h, be incubated 40min;4th baking inphases, warm temperature from when being raised to 1050 DEG C for 850 DEG C,
Programming rate is 150 DEG C/h, is incubated 3 hours, extremely into brick;5th baking inphases, when dropping to 100 DEG C from 1050 DEG C, cooling speed
Spend for 200 DEG C/h, to kiln discharge.
Embodiment 2
A kind of production method of dyeing and printing sewage treatment plant firing sludge clinker bricks in environmental protection, comprises the following steps:
S1, sludge drying and other treatment:The sludge that dyeing and printing sewage treatment plant in S1 is shipped to moisture content 85% enters pond, then adds and contain
The sludge water of water rate 97% or so is diluted, and obtains the sludge of moisture content 93%, then adds medicament stirring, then with screw rod high pressure
The sludge slurry of moisture content 93% is sent into sheet frame diaphragm filter press by pump, after high pressure charging, diaphragm pressing, unloads sludge cake automatically,
The drying kiln using roasting tunnel kiln waste heat of baking bricks is sent into through conveyer belt, the dewatered sludge of moisture content 35% is obtained after drying,
Be put in storage the stand-by part material for sintering heat-reserving brick processed;
S2,0 part of flyash of 30-40 parts printing and dyeing sludge, 38 parts of building wastes and 2 parts of polymeric adhesive by desiccation
Apron feeder is respectively charged into, according to chemical analysis, carries out by PLC automatically controlling dispensing through electronic measurement, is slightly broken through hammer
Machine is slightly broken, then through thin hammer-crusher thin broken, then sieve and be well mixed through rotary screen;
S3, again by weighing balance, with construction waste soil, the mixed of polymeric adhesive and water is added after thick, thin two pairs of rollers
Liquid is closed, controls the moisture content of compound to be sent into ageing storehouse after agitated 20%, it is stand-by after old 3 days;
S4, it will pass through and glued in ageing storehouse desiccation printing and dyeing sludge, flyash, building waste and the macromolecule of old more than 72 hours
Agent mixed powder particle is connect, through multi-bucket excavator feeding, is transported through conveyer belt, raw material is sent into twin rollers and carries out roll-in, broken refinement
Ground with rubbing, then through conveyer belt, into edge runner, increase the fineness and plasticity of compound, then mixer, regulation are sent into through conveyer belt
The moisture content and increase plasticity of compound, then 75 type double roller vacuum hard plastic extruders are sent into through conveyer belt, insulation adobe is made;
S5, the insulation adobe of forming passed through on the full-automatic code of manipulator to kiln car;
S6, by forming insulation adobe by hauling machine be sent into a surrounding use in brick confined space, stop 24
Hour;Atmosphere draught-free, make insulation adobe is fully quiet to stop;Desiccation printing and dyeing sludge, flyash, building waste compound between fully
Bonding, moisture content are sufficiently unanimously homogenized, and adobe surface is not ftractureed, and reach the purpose for improving insulating brick green strength;
S7, the base substrate obtained in S6 is placed in curing with carbon dioxide case conserved, curing time is 2-3 days, is taken out immediately
Obtain no-firing brick;
S8, by the no-firing brick obtained in S7 through drying cart be sent into hothouse be dried, the drying time 65~
85min, 150~190 DEG C of drying temperature, the moisture content of dried no-firing brick is 2~3%;
The no-firing brick obtained in S9, S8 is sent into tunnel cave and is calcined, and roasting process is:First baking inphases, from room
When temperature is raised to 80 DEG C, programming rate is 100 DEG C/h, is incubated 30-40min;Second baking inphases, warm temperature is from 80
When DEG C being raised to 450 DEG C, programming rate is 120 DEG C/h, is incubated 40min;3rd baking inphases, warm temperature are raised to from 450 DEG C
At 850 DEG C, programming rate is 130 DEG C/h, is incubated 50min;4th baking inphases, warm temperature are raised to 1050 DEG C from 850 DEG C
When, programming rate is 150 DEG C/h, is incubated 3-4 hours, extremely into brick;5th baking inphases, when dropping to 100 DEG C from 1050 DEG C,
Cooling rate is 200 DEG C/h, to kiln discharge.
Embodiment 3
A kind of production method of dyeing and printing sewage treatment plant firing sludge clinker bricks in environmental protection, comprises the following steps:
S1, sludge drying and other treatment:The sludge that dyeing and printing sewage treatment plant in S1 is shipped to moisture content 85% enters pond, then adds and contain
The sludge water of water rate 97% or so is diluted, and obtains the sludge of moisture content 93%, then adds medicament stirring, then with screw rod high pressure
The sludge slurry of moisture content 93% is sent into sheet frame diaphragm filter press by pump, after high pressure charging, diaphragm pressing, unloads sludge cake automatically,
The drying kiln using roasting tunnel kiln waste heat of baking bricks is sent into through conveyer belt, the dewatered sludge of moisture content 35% is obtained after drying,
Be put in storage the stand-by part material for sintering heat-reserving brick processed;
S2,30-40 part printing and dyeing sludge 15-20 parts flyash, 28-38 parts building waste and the height of 1-2 parts by desiccation
Molecular adhesion agent is respectively charged into apron feeder, according to chemical analysis, carries out by PLC automatically controlling dispensing through electronic measurement,
Slightly broken through hammer coarse breaking machine, then through thin hammer-crusher thin broken, then sieve and be well mixed through rotary screen;
S3, again by weighing balance, with construction waste soil, the mixed of polymeric adhesive and water is added after thick, thin two pairs of rollers
Liquid is closed, controls the moisture content of compound to be sent into ageing storehouse after agitated 20%, it is stand-by after old 3 days;
S4, it will pass through and glued in ageing storehouse desiccation printing and dyeing sludge, flyash, building waste and the macromolecule of old more than 72 hours
Agent mixed powder particle is connect, through multi-bucket excavator feeding, is transported through conveyer belt, raw material is sent into twin rollers and carries out roll-in, broken refinement
Ground with rubbing, then through conveyer belt, into edge runner, increase the fineness and plasticity of compound, then mixer, regulation are sent into through conveyer belt
The moisture content and increase plasticity of compound, then 75 type double roller vacuum hard plastic extruders are sent into through conveyer belt, insulation adobe is made;
S5, the insulation adobe of forming passed through on the full-automatic code of manipulator to kiln car;
S6, by forming insulation adobe by hauling machine be sent into a surrounding use in brick confined space, stop 24
Hour;Atmosphere draught-free, make insulation adobe is fully quiet to stop;Desiccation printing and dyeing sludge, flyash, building waste compound between fully
Bonding, moisture content are sufficiently unanimously homogenized, and adobe surface is not ftractureed, and reach the purpose for improving insulating brick green strength;
S7, the base substrate obtained in S6 is placed in curing with carbon dioxide case conserved, curing time is 2-3 days, is taken out immediately
Obtain no-firing brick;
S8, by the no-firing brick obtained in S7 through drying cart be sent into hothouse be dried, the drying time 65~
85min, 150~190 DEG C of drying temperature, the moisture content of dried no-firing brick is 2~3%;
The no-firing brick obtained in S9, S8 is sent into tunnel cave and is calcined, and roasting process is:First baking inphases, from room
When temperature is raised to 80 DEG C, programming rate is 100 DEG C/h, is incubated 30-40min;Second baking inphases, warm temperature is from 80
When DEG C being raised to 450 DEG C, programming rate is 120 DEG C/h, is incubated 35-40min;3rd baking inphases, warm temperature is from 450 DEG C
When being raised to 850 DEG C, programming rate is 130 DEG C/h, is incubated 40-50min;4th baking inphases, warm temperature rise from 850 DEG C
During to 1050 DEG C, programming rate is 150 DEG C/h, is incubated 3-4 hours, extremely into brick;5th baking inphases, dropped to from 1050 DEG C
At 100 DEG C, cooling rate is 200 DEG C/h, to kiln discharge.
Finally it should be noted that:The preferred embodiments of the present invention are the foregoing is only, are not intended to limit the invention,
Although the present invention is described in detail with reference to the foregoing embodiments, for those skilled in the art, it still may be used
To be modified to the technical scheme described in foregoing embodiments, or equivalent substitution is carried out to which part technical characteristic,
Within the spirit and principles of the invention, any modification, equivalent substitution and improvements made etc., it should be included in the present invention's
Within protection domain.
Claims (3)
1. a kind of production method of dyeing and printing sewage treatment plant firing sludge clinker bricks in environmental protection, it is characterised in that comprise the following steps:
S1, sludge drying and other treatment:The sludge that dyeing and printing sewage treatment plant in S1 is shipped to moisture content 85% enters pond, then adds moisture content
97% or so sludge water is diluted, and obtains the sludge of moisture content 93%, then adds medicament stirring, then with screw rod high-pressure pump handle
The sludge slurry of moisture content 93% is sent into sheet frame diaphragm filter press, after high pressure charging, diaphragm pressing, sludge cake is unloaded automatically, through defeated
The drying kiln using roasting tunnel kiln waste heat of baking bricks with feeding is sent, the dewatered sludge of moisture content 35% is obtained after drying, is put in storage
The stand-by part material for sintering heat-reserving brick processed;
S2,30-40 part printing and dyeing sludge 15-20 parts flyash, 28-38 parts building waste and the macromolecule of 1-2 parts by desiccation
Bonding agent is respectively charged into apron feeder, according to chemical analysis, carries out by PLC automatically controlling dispensing through electronic measurement, through hammer
Formula coarse breaking machine is slightly broken, then through thin hammer-crusher thin broken, then sieve and be well mixed through rotary screen;
S3, again by weighing balance, with construction waste soil, the mixed liquor of polymeric adhesive and water is added after thick, thin two pairs of rollers,
The moisture content of compound is controlled 20%, ageing storehouse is sent into after agitated, it is stand-by after old 3 days;
S4, it will pass through in ageing storehouse desiccation printing and dyeing sludge, flyash, building waste and the polymeric adhesive of old more than 72 hours
Mixed powder particle, through multi-bucket excavator feeding, transported through conveyer belt, raw material is sent into twin rollers and carries out roll-in, broken refinement and rub
Grind, then through conveyer belt, into edge runner, increase the fineness and plasticity of compound, then mixer, regulation mixing are sent into through conveyer belt
The moisture content and increase plasticity of material, then 75 type double roller vacuum hard plastic extruders are sent into through conveyer belt, insulation adobe is made;
S5, the insulation adobe of forming passed through on the full-automatic code of manipulator to kiln car;
S6, by forming insulation adobe by hauling machine be sent into a surrounding use in brick confined space, stop 24 hours;
Atmosphere draught-free, make insulation adobe is fully quiet to stop;Desiccation printing and dyeing sludge, flyash, building waste compound between fully bond,
Moisture content is sufficiently unanimously homogenized, and adobe surface is not ftractureed, and reaches the purpose for improving insulating brick green strength;
S7, the base substrate obtained in S6 is placed in curing with carbon dioxide case conserved, curing time is 2-3 days, and taking-up obtains immediately
No-firing brick;
S8, by the no-firing brick obtained in S7 through drying cart be sent into hothouse be dried, the 65~85min of drying time,
150~190 DEG C of drying temperature, the moisture content of dried no-firing brick is 2~3%;
The no-firing brick that is obtained in S9, S8 is sent into tunnel cave and is calcined, and roasting time is 65~85min, sintering temperature 850
~1050 DEG C.
2. a kind of production method of dyeing and printing sewage treatment plant firing sludge clinker bricks in environmental protection according to claim 1, it is special
Sign is:In S1, medicament is one kind of aluminium polychloride sludge conditioner and PAMC sludge conditioner
Or two kinds.
3. a kind of production method of dyeing and printing sewage treatment plant firing sludge clinker bricks in environmental protection according to claim 1, it is special
Sign is:Roasting process is in the step S9:First baking inphases, when being raised to 80 DEG C from ambient temperature, programming rate 100
DEG C/h, it is incubated 30-40min;Second baking inphases, warm temperature from when being raised to 450 DEG C for 80 DEG C, programming rate is 120 DEG C/
Hour, it is incubated 35-40min;3rd baking inphases, for warm temperature from when being raised to 850 DEG C for 450 DEG C, programming rate is 130 DEG C/small
When, it is incubated 40-50min;4th baking inphases, for warm temperature from when being raised to 1050 DEG C for 850 DEG C, programming rate is 150 DEG C/small
When, 3-4 hours are incubated, extremely into brick;5th baking inphases, when dropping to 100 DEG C from 1050 DEG C, cooling rate is 200 DEG C/h,
To kiln discharge.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201710888552.4A CN107673732A (en) | 2017-09-27 | 2017-09-27 | A kind of production method of dyeing and printing sewage treatment plant firing sludge clinker bricks in environmental protection |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201710888552.4A CN107673732A (en) | 2017-09-27 | 2017-09-27 | A kind of production method of dyeing and printing sewage treatment plant firing sludge clinker bricks in environmental protection |
Publications (1)
Publication Number | Publication Date |
---|---|
CN107673732A true CN107673732A (en) | 2018-02-09 |
Family
ID=61137528
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201710888552.4A Pending CN107673732A (en) | 2017-09-27 | 2017-09-27 | A kind of production method of dyeing and printing sewage treatment plant firing sludge clinker bricks in environmental protection |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN107673732A (en) |
Cited By (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN110395948A (en) * | 2019-07-31 | 2019-11-01 | 淮北市菲美得环保科技有限公司 | A kind of non-sintered water-permeable brick and preparation method thereof based on printing and dyeing sludge |
CN110550934A (en) * | 2019-10-12 | 2019-12-10 | 杭州力锦环保建材有限公司 | Water permeable brick manufactured by sintering municipal sludge and construction waste and manufacturing method thereof |
CN111018556A (en) * | 2019-12-11 | 2020-04-17 | 镇江市雅盛节能环保材料有限公司 | Treating agent for cooperatively treating polluted soil in ceramsite production and preparation method thereof |
CN111499348A (en) * | 2020-04-17 | 2020-08-07 | 余姚市恒祥新型建材有限公司 | Production process of sintered brick |
CN111943645A (en) * | 2020-08-13 | 2020-11-17 | 海盐达贝尔新型建材有限公司 | Production line and production process for sintering heat-insulating bricks by using sewage sludge |
CN114292086A (en) * | 2021-12-31 | 2022-04-08 | 福建省乐普陶板制造有限公司 | Process for manufacturing raw materials of brick, tile and ceramic plate |
Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102329111A (en) * | 2011-06-21 | 2012-01-25 | 东莞市保源达房地产开发有限公司 | Lightweight brick manufactured by utilizing printing and dyeing sludge and manufacturing method thereof |
CN103090396A (en) * | 2012-12-06 | 2013-05-08 | 上海金自天正信息技术有限公司 | Two-stage drying and incineration method for sludge |
CN105439613A (en) * | 2015-11-18 | 2016-03-30 | 浙江捷丰环保技术工程有限公司 | Production method for preparing sintering thermal insulation brick from sludge |
CN106082939A (en) * | 2016-06-14 | 2016-11-09 | 湖北工业大学 | A kind of method utilizing industrial residue to prepare no-firing brick |
-
2017
- 2017-09-27 CN CN201710888552.4A patent/CN107673732A/en active Pending
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102329111A (en) * | 2011-06-21 | 2012-01-25 | 东莞市保源达房地产开发有限公司 | Lightweight brick manufactured by utilizing printing and dyeing sludge and manufacturing method thereof |
CN103090396A (en) * | 2012-12-06 | 2013-05-08 | 上海金自天正信息技术有限公司 | Two-stage drying and incineration method for sludge |
CN105439613A (en) * | 2015-11-18 | 2016-03-30 | 浙江捷丰环保技术工程有限公司 | Production method for preparing sintering thermal insulation brick from sludge |
CN106082939A (en) * | 2016-06-14 | 2016-11-09 | 湖北工业大学 | A kind of method utilizing industrial residue to prepare no-firing brick |
Cited By (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN110395948A (en) * | 2019-07-31 | 2019-11-01 | 淮北市菲美得环保科技有限公司 | A kind of non-sintered water-permeable brick and preparation method thereof based on printing and dyeing sludge |
CN110550934A (en) * | 2019-10-12 | 2019-12-10 | 杭州力锦环保建材有限公司 | Water permeable brick manufactured by sintering municipal sludge and construction waste and manufacturing method thereof |
CN111018556A (en) * | 2019-12-11 | 2020-04-17 | 镇江市雅盛节能环保材料有限公司 | Treating agent for cooperatively treating polluted soil in ceramsite production and preparation method thereof |
CN111499348A (en) * | 2020-04-17 | 2020-08-07 | 余姚市恒祥新型建材有限公司 | Production process of sintered brick |
CN111943645A (en) * | 2020-08-13 | 2020-11-17 | 海盐达贝尔新型建材有限公司 | Production line and production process for sintering heat-insulating bricks by using sewage sludge |
CN114292086A (en) * | 2021-12-31 | 2022-04-08 | 福建省乐普陶板制造有限公司 | Process for manufacturing raw materials of brick, tile and ceramic plate |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN107673732A (en) | A kind of production method of dyeing and printing sewage treatment plant firing sludge clinker bricks in environmental protection | |
CN107216126B (en) | Preparation method of ceramsite by taking municipal sludge as raw material | |
CN105439613A (en) | Production method for preparing sintering thermal insulation brick from sludge | |
CN110078530B (en) | Preparation method of high-performance sintered insulating brick | |
CN107459364B (en) | High-strength ceramsite prepared by using yellow river sludge and sludge as binder and preparation method thereof | |
CN105948576B (en) | A variety of industrial sludge produced environment friendlies non-burning brick method and its preparation system | |
CN102161562B (en) | Process for treating excess sludge by utilizing fly ash | |
CN102775113B (en) | Method for manufacturing autoclaved bricks by utilizing contaminated acid sludge | |
CN107827335B (en) | Municipal sludge harmless treatment method | |
CN101244928A (en) | Method for producing sewage sludge shale brick | |
CN107721375A (en) | A kind of method that sewage treatment plant's dewatered sludge suppresses non-autoclaved and unburned wall bulk | |
CN108794019A (en) | The formula and production method of fired brick are produced with high heating value sludge | |
CN105272159A (en) | Production method of sludge sintered brick | |
CN102786194A (en) | Method for treating sludge through aerobic fermentation at high temperature | |
CN103570326A (en) | Process for preparing baking-free bricks by using bio-degraded sludge | |
CN101565264B (en) | Method for treating sludge and method for recycling sludge building material and producing into fertilizer | |
CN103436321A (en) | Technique for preparing derived fuel from high-moisture domestic waste and municipal sludge | |
CN109912289A (en) | A kind of industrialized preparing process and system of sludge autoclaved brick | |
CN111196700A (en) | Environment-friendly baking-free brick prepared from sludge and furnace slag and preparation method thereof | |
CN104556630B (en) | The method of microwave treatment sewage sludge | |
CN105948445B (en) | A kind of leather waste water sludge treatment technique | |
CN104086159A (en) | Biogas slurry sintered brick and preparation method thereof | |
CN206244657U (en) | It is a kind of to starch the system that paper plant's sludge prepares shale brick | |
CN206396069U (en) | Sludge dynamically accelerates aerobic high-heat fermented manure equipment | |
CN107445592A (en) | A kind of multi-functional haydite and its production method that fluxing agent is made using pickling sludge |
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: 20180209 |
|
RJ01 | Rejection of invention patent application after publication |