CN106278373B - Utilize the water-permeable brick and preparation method thereof of heavy metal sewage sludge preparation - Google Patents

Utilize the water-permeable brick and preparation method thereof of heavy metal sewage sludge preparation Download PDF

Info

Publication number
CN106278373B
CN106278373B CN201610663310.0A CN201610663310A CN106278373B CN 106278373 B CN106278373 B CN 106278373B CN 201610663310 A CN201610663310 A CN 201610663310A CN 106278373 B CN106278373 B CN 106278373B
Authority
CN
China
Prior art keywords
sludge
heavy metal
hydrolysis solution
water
permeable brick
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.)
Active
Application number
CN201610663310.0A
Other languages
Chinese (zh)
Other versions
CN106278373A (en
Inventor
王炜
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Shanghai Emperor of Cleaning TECH Co Ltd
Original Assignee
Shanghai Emperor of Cleaning TECH Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Shanghai Emperor of Cleaning TECH Co Ltd filed Critical Shanghai Emperor of Cleaning TECH Co Ltd
Priority to CN201610663310.0A priority Critical patent/CN106278373B/en
Publication of CN106278373A publication Critical patent/CN106278373A/en
Application granted granted Critical
Publication of CN106278373B publication Critical patent/CN106278373B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B38/00Porous mortars, concrete, artificial stone or ceramic ware; Preparation thereof
    • C04B38/08Porous mortars, concrete, artificial stone or ceramic ware; Preparation thereof by adding porous substances
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01GCOMPOUNDS CONTAINING METALS NOT COVERED BY SUBCLASSES C01D OR C01F
    • C01G49/00Compounds of iron
    • C01G49/0018Mixed oxides or hydroxides
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/12Treatment of sludge; Devices therefor by de-watering, drying or thickening
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B33/00Clay-wares
    • C04B33/02Preparing or treating the raw materials individually or as batches
    • C04B33/13Compounding ingredients
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B33/00Clay-wares
    • C04B33/02Preparing or treating the raw materials individually or as batches
    • C04B33/13Compounding ingredients
    • C04B33/131Inorganic additives
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B33/00Clay-wares
    • C04B33/02Preparing or treating the raw materials individually or as batches
    • C04B33/13Compounding ingredients
    • C04B33/132Waste materials; Refuse; Residues
    • C04B33/1321Waste slurries, e.g. harbour sludge, industrial muds
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B33/00Clay-wares
    • C04B33/02Preparing or treating the raw materials individually or as batches
    • C04B33/13Compounding ingredients
    • C04B33/132Waste materials; Refuse; Residues
    • C04B33/135Combustion residues, e.g. fly ash, incineration waste
    • C04B33/1352Fuel ashes, e.g. fly ash
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B33/00Clay-wares
    • C04B33/02Preparing or treating the raw materials individually or as batches
    • C04B33/13Compounding ingredients
    • C04B33/132Waste materials; Refuse; Residues
    • C04B33/138Waste materials; Refuse; Residues from metallurgical processes, e.g. slag, furnace dust, galvanic waste
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B38/00Porous mortars, concrete, artificial stone or ceramic ware; Preparation thereof
    • C04B38/06Porous mortars, concrete, artificial stone or ceramic ware; Preparation thereof by burning-out added substances by burning natural expanding materials or by sublimating or melting out added substances
    • C04B38/063Preparing or treating the raw materials individually or as batches
    • C04B38/0635Compounding ingredients
    • C04B38/0645Burnable, meltable, sublimable materials
    • C04B38/0675Vegetable refuse; Cellulosic materials, e.g. wood chips, cork, peat, paper
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/20Heavy metals or heavy metal compounds
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B2235/00Aspects relating to ceramic starting mixtures or sintered ceramic products
    • C04B2235/02Composition of constituents of the starting material or of secondary phases of the final product
    • C04B2235/30Constituents and secondary phases not being of a fibrous nature
    • C04B2235/34Non-metal oxides, non-metal mixed oxides, or salts thereof that form the non-metal oxides upon heating, e.g. carbonates, nitrates, (oxy)hydroxides, chlorides
    • C04B2235/3418Silicon oxide, silicic acids or oxide forming salts thereof, e.g. silica sol, fused silica, silica fume, cristobalite, quartz or flint
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B2235/00Aspects relating to ceramic starting mixtures or sintered ceramic products
    • C04B2235/02Composition of constituents of the starting material or of secondary phases of the final product
    • C04B2235/30Constituents and secondary phases not being of a fibrous nature
    • C04B2235/34Non-metal oxides, non-metal mixed oxides, or salts thereof that form the non-metal oxides upon heating, e.g. carbonates, nitrates, (oxy)hydroxides, chlorides
    • C04B2235/3427Silicates other than clay, e.g. water glass
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B2235/00Aspects relating to ceramic starting mixtures or sintered ceramic products
    • C04B2235/70Aspects relating to sintered or melt-casted ceramic products
    • C04B2235/96Properties of ceramic products, e.g. mechanical properties such as strength, toughness, wear resistance
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P40/00Technologies relating to the processing of minerals
    • Y02P40/60Production of ceramic materials or ceramic elements, e.g. substitution of clay or shale by alternative raw materials, e.g. ashes

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Ceramic Engineering (AREA)
  • Organic Chemistry (AREA)
  • Structural Engineering (AREA)
  • Materials Engineering (AREA)
  • Dispersion Chemistry (AREA)
  • Environmental & Geological Engineering (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Inorganic Chemistry (AREA)
  • Hydrology & Water Resources (AREA)
  • Water Supply & Treatment (AREA)
  • Combustion & Propulsion (AREA)
  • Wood Science & Technology (AREA)
  • Treatment Of Sludge (AREA)

Abstract

The present invention relates to a kind of water-permeable bricks and preparation method thereof using heavy metal sewage sludge preparation, water-permeable brick includes following components and parts by weight content: innoxious sludge 40-45, common stone 20-23, steel slag 15-18, flyash 8-10, waterglass 12-15, quartz sand 10-12, kaolin 5-8, bamboo powder 3-4 and pore creating material 1-3, wherein, innoxious sludge is obtained after being handled by heavy metal sewage sludge, preparation process includes heavy metal sewage sludge acidolysis, heavy metal sewage sludge ultrasonic Separation, ferrite and innoxious sludge extract, the mixing of water-permeable brick raw material, green brick forming, brick bat drying, adobe roasting and etc..Compared with prior art, the present invention is while heavy metal sewage sludge is innoxious, extract ferrite product and innoxious sludge, the former can be used as the Iron Ore Powder before radiation shielding coating additive or steel-refining, the latter can be used for the preparation of sponge urban construction water-permeable brick, the useless rate of benefit is high, and the maximum resourceization for realizing heavy metal sewage sludge utilizes.

Description

Utilize the water-permeable brick and preparation method thereof of heavy metal sewage sludge preparation
Technical field
The invention belongs to solid hazardous waste recycling and the field of building materials in environmental project, more particularly, to one The water-permeable brick and preparation method thereof that kind is prepared using heavy metal sewage sludge.
Background technique
Heavy metal sewage sludge is mainly derived from the waste water such as electroplating industry, metal finishing industry, printed circuit board industry The sludged waste material containing heavy metal generated after reason, the 17th class hazardous waste being put into National Hazard waste list (HW17).Since the heavy metals such as Cu, Ni, Cr, Zn, Fe in above-mentioned industry waste water are transferred in sludge, it is heavy metal-polluted Mud is electroplating wastewater " final state object ", have the characteristics that easily accumulate, it is unstable, be easy to run off, if do not dealt carefully with, any heap It puts, the heavy metals such as Cu, Ni, Zn, Cr, Fe in sludge are under rain leaching or other effects, it will along one soil of sludge The Path Migration of one crops of earth, one human body, and may cause the secondary pollution of surface water, soil, underground water, or even jeopardize life Object chain causes serious environmental disruption.
The characteristics of for heavy metal sewage sludge and its harmfulness are examined from the angle of environmental pollution prevention and control and resource circulation utilization Consider, mainly use following two processing mode, first is that after treatment, so that sludge is not caused secondary pollution so fill or Storage, i.e. harmlessness disposing;Second is that making to carry out synthetical recovery, i.e. resource utilization to the heavy metal resources in sludge.Current nothing The method of evilization disposition has curing agent to solidify, fill, burn and fill out sea;Wherein curing technology is one in hazardous waste processing Important technology there are curing materials to be easy to get, high treating effect, advantage at low cost, i.e., fix the huge sum of money in sludge with curing agent Belong to, then processes again, but there are still certain leaching hidden danger;Landfill is that comparison is suitble to a danger of China's actual conditions useless Object harmlessness disposing approach, but the domestic Landfill for heavy metal sewage sludge is still in lower level;Sea is thrown actually to belong to In the transfer of pollutant, even across solidification, the threat caused by marine ecosystems and human health is heavy metal sewage sludge It is difficult to avoid that, the world is forbidden already;Burning heat treatment is to realize that heavy metal sewage sludge minimizing, innoxious one kind is quick, has The technology of effect still since this method energy consumption is higher, there are certain requirements burning facility and condition, and general small electroplate factory is difficult To bear huge processing cost, therefore hardly result in the popularization of large area.
Due to the aggravation of resource dilution and environmental pollution, heavy metal sewage sludge is returned as a kind of important heavy metal resources It receives and utilizes, be always the emphasis studied both at home and abroad.Wherein, main method have recycling heavy metal, ferrite comprehensive utilization technique,
Composting makes fertilizer and production modified plastics product.Chinese patent " a kind of heavy metal-polluted mud resource and nothing The processing method of evilization " (CN102433437B) disclose it is a kind of by heavy metal sewage sludge dehydration, it is dry after with flux, binder into Row ingredient, clamp dog or ball processed, then coke, block or spherical material are put into smelting furnace and carry out melting;The technique is not in sludge Heavy metal be recycled.Chinese patent " the full recycling treatment system of heavy metal sewage sludge " (CN203833780U) develops A kind of full recycling treatment system of heavy metal sewage sludge can effectively take out many useful components contained in heavy metal sewage sludge etc. again sharp With, but do not consider how the residue after extracting utilizes;Chinese patent " alkaline sludge containing heavy metal recycling processing method " (CN201245054) it proposes one kind and extracts the resources such as tapping oxygen crystal and calcium sulfate from heavy metal alkaline sludge, but this is heavy In metal alkaline sludge other than producing iron oxygen crystal, sodium sulphate, calcium sulfate, still there is the generation such as acid non-soluble substance, after washing Acid non-soluble substance etc. is innoxious, general to bury, but full resource utilization has not yet been reached in this.Chinese publication is " at a kind of collaboration The huge sum of money for being 20~50% by moisture content using synergistic effect in the method for setting heavy metal sewage sludge " (Publication No. 105271624A) Belong to sludge and calcium-based absorbents mix, is dry, crushing, obtains calcium base sludge, then mix with basic raw materials for sintering and dedusting ash, make Grain, cloth, are finally sintered, obtain sinter;Patent applicant is Baosteel Stainless Steel Co., Ltd., and the method is because of ground system Preferably, its industrial chain is taken full advantage of, but is not suitable for promoting the use of.
" sponge city " is theory and the direction of urban construction, that is, refers to that city can become as sponge adapting to environment Change and cope with natural calamity etc. has good " elasticity ", and water suction, water storage, infiltration, water purification when raining will store when needing Water " release " and be used.Existing town road road surface mostly uses the impermeable materials such as cement concrete, pitch to spread The ponding that will form large area if forming, when rainy has been not suitable with the theory of sponge urban development.And water-permeable brick is meeting substantially Road hardening, it is smooth while, also have good permeable and performance of keeping humidity, natural precipitation can be absorbed, and enter underground Water system forms good circulation.Therefore, the innoxious sludge after heavy metal sewage sludge being extracted ferrite is built as sponge city If there is good environmental benefit and economic benefit with a kind of main raw material(s) of water-permeable brick.
Summary of the invention
It is an object of the present invention to overcome the above-mentioned drawbacks of the prior art and provide a kind of using heavy metal-polluted Clay standby compression strength is high, water permeability is good, energy conservation and environmental protection and water-permeable brick of Antimicrobial preservative and preparation method thereof.
The purpose of the present invention can be achieved through the following technical solutions:
A kind of water-permeable brick prepared using innoxious sludge, including following components and parts by weight content:
Innoxious sludge 40-45, common stone 20-23, steel slag 15-18, flyash 8-10, waterglass 12-15, quartz sand 10-12, kaolin 5-8, bamboo powder 3-4 and pore creating material 1-3.
The steel slag and quartz sand crosses 10 meshes, partial size≤0.15mm of the flyash.
The pore creating material is perlite, diatomite, rice husk or boils stone.
The preparation method that water-permeable brick is prepared using innoxious sludge, specifically includes the following steps:
(1) acid hydrolysis solution stirring is added in heavy metal sewage sludge, reacts heavy metal ion with acid and is leached, pH in system When being adjusted to 2.2-3.2, acidolysis reaction terminates;
(2) mixed liquor of step (1) is subjected to ultrasonication, sludge and acid hydrolysis solution is made to come into full contact with and react;
(3) mixed liquor after ultrasound in step (2) is separated by solid-liquid separation, obtains acid hydrolysis solution and remains the dirt of acid hydrolysis solution Mud;
(4) sludge of residual acid hydrolysis solution in step (3) is rinsed with clear water, sloughs remaining acid hydrolysis solution and heavy metal, Obtain innoxious sludge;
(5) liquid generated after the acid hydrolysis solution and the middle sludge for rinsing residual acid hydrolysis solution of step (4) in step (3) is carried out Ferrous sulfate is added in mixing, is uniformly mixed and heats, adds lye, and be passed through oxygen, sufficiently generates after reaction containing iron member The ferrite crystal of element and heavy metal ion, ferrite crystal are separated with alkaline waste liquor, are dried, and obtain ferrite, alkaline waste liquor Handle qualified discharge;
(6) the innoxious sludge for obtaining step (4) and common stone, steel slag, flyash, waterglass, quartz sand, kaolinite Soil, bamboo powder and pore creating material stir into pug after mixing by charge ratio, and control moisture content;
(7) pug of step (6) is put into dry-pressing formed machine is dry-pressing formed, the water-permeable brick brick of different shape and size is made Base;
(8) permeable brick adobe obtained in step (7) is dry by spontaneously drying or being put into drying box;
(9) the permeable brick adobe of step (8) after dry is sintered to get water-permeable brick is arrived.
Acid hydrolysis solution described in step (1) is the mixture of sulfuric acid, nitric acid, hydrofluoric acid and hydrogen peroxide, sulfuric acid, nitric acid, hydrogen fluorine 8-10:2-4:2-4:1 is prepared by volume for acid and hydrogen peroxide, and the volume that acid hydrolysis solution is added is the 30- of heavy metal sewage sludge volume 50%.
The frequency of oscillation of ultrasonic wave described in step (2) is 15-30KHz, duration of oscillation 1-2h, and step (4) is described clear The number that water rinses is 3-5 times.
The additive amount of ferrous sulfate described in step (5) is 8-12 times of heavy metal gross mass in liquid, heats liquid temperature Degree is to 55-65 DEG C, and the lye is NaOH or KOH, and the pH value that lye amount is added to liquid is 8.5-9.
The moisture control of step (6) described pug is in 14-18wt%, the pressure of dry-pressing formed machine described in step (7) For 25-35Mpa.
Drying box described in step (8) is thermostatic drying chamber, and temperature is 103-108 DEG C, it is dry after adobe moisture content not Greater than 6wt%.
It is warming up to 1020-1150 DEG C with the speed of 3.5-4.0 DEG C/min when step (9) is sintered, is persistently sintered 2.5-3.5h After be down to room temperature.
Compared with prior art, the invention has the following advantages that
1, heavy metal sewage sludge by can extract after acidolysis, ultrasonic separation, ferrous sulfate and salkali waste curing heavy metal first Ferrite can also be using remaining innoxious sludge as preparation as the Iron Ore Powder before radiation shielding coating additive or steel-refining The raw material of sponge urban construction water-permeable brick maximize the recycling for realizing resource;
2, the water-permeable brick of this method preparation, due to joined steel slag, common stone as coarse aggregate, innoxious sludge, powder Coal ash has high intensity, high temperature resistant, corrosion resistant characteristic as binder, quartz sand as fine aggregate, waterglass, and kaolin has Viscosity and high temperature resistant, bamboo powder can Antimicrobial preservative, be also added into pore creating material, therefore last water-permeable brick compression strength obtained is high, thoroughly It is aqueous good, there is the excellent performance of absorbing sound and lowering noise and Antimicrobial preservative, meets " water-permeable brick " (CJ/T945~2005) professional standard, Simultaneously it is low in cost, can industrialized production, responded sponge the idea of the city, can be used as Building wood important in sponge urban construction Material;
3, the acid hydrolysis solution that this method is formulated using certain proportion sulfuric acid, nitric acid, hydrofluoric acid and hydrogen peroxide is to heavy metal Sludge carries out thorough acidolysis, and wherein sulfuric acid plays main resolution, and hydrogen peroxide oxidation can remove organic matter a small amount of in sludge, add The nitric acid and hydrofluoric acid entered can be improved digestion condition, accelerates oxidation rate and improve resolution effect, it ensure that subsequent water-permeable brick Sludge is innoxious in raw material, and then ensure that the water-permeable brick of preparation is harmless, environmentally friendly;
4, invention is suitble to the various sludge containing heavy metal ion of processing, and not only versatility is good for this method, and process conditions are simple, Strong operability can more realize large-scale production, be a kind for the treatment of of wastes with processes of wastes against one another, and energy-saving and emission-reduction, innoxious and resource regeneration contain The processing technique of heavy metal sewage sludge.
The present invention extracts ferrite product and innoxious sludge, Qian Zheke while heavy metal sewage sludge harmless treatment As the Iron Ore Powder before radiation shielding coating additive or steel-refining, the latter can be used for the preparation of sponge urban construction water-permeable brick, The water-permeable brick that compression strength is high, water permeability is good and durable can be made, suitable for the road surface in sponge urban construction It is laid with.The present invention can largely dissolve heavy metal sewage sludge, and after extracting ferrite, innoxious sludge is alternatively arranged as water-permeable brick preparation Main raw material(s), the useless rate of benefit is high, and the maximum resourceization for realizing heavy metal sewage sludge utilizes.
Detailed description of the invention
Fig. 1 is process flow chart of the invention.
Specific embodiment
The present invention is described in detail with specific embodiment below in conjunction with the accompanying drawings.
Embodiment 1
For handling East China automobile electroplating workshop heavy metal sewage sludge, implementation steps are further described, technique Flow chart is as shown in Figure 1.
Step 1: heavy metal sewage sludge of the 100Kg moisture content not less than 60% is weighed in acidolysis slot, according to heavy metal sewage sludge Volume 30% be added acid hydrolysis solution, acid hydrolysis solution is with sulfuric acid: nitric acid: hydrofluoric acid: hydrogen peroxide=9:3:3:1 volume ratio prepare and At being sufficiently stirred in adding procedure, make heavy metal ion by Ore Leaching.
Step 2: the mixed liquor in step 1 acidolysis slot is put into ultrasonic tank, ultrasonic wavelength-division is carried out with the frequency of 15KHz Solution, so that sludge and acid hydrolysis solution come into full contact with and react.
Step 3: the mixed liquor after ultrasound in step 2 is separated by solid-liquid separation, pickle liquor is obtained and has acid hydrolysis solution residual Sludge.
Step 4: will there is the remaining sludge of acid hydrolysis solution to be flushed three times in step 3 with clear water, to slough remaining heavy metal, Obtain innoxious sludge.
Step 5: the liquid rinsed after having acid hydrolysis solution to remain sludge in the pickle liquor and step 4 in step 3 is added It is mixed in ferrite reaction tank, ferrous sulfate is added, the quality being added is 8 of all heavy metal quality in mixed liquor Times, it is uniformly mixed, and heat liquid to 55 DEG C.Then, NaOH is slowly added into reaction tank, until when pH value is 8.5 in system, It is passed through high-purity oxygen, is sufficiently generated after reaction and contains the ferrite crystal including ferro element and heavy metal ion;It will finally give birth to At ferrite crystal separated with alkaline waste liquor after dry to get to ferrite, alkaline waste liquor is discharged into waste water treatment system processing Qualified discharge afterwards.
Step 6: by the innoxious sludge isolated in step 4 and steel slag, common stone, flyash, quartz sand, water glass Glass, kaolin, bamboo powder and pore creating material mix, wherein parts by weight (Kg) are as follows: and innoxious sludge is 40, common stone 20, steel slag 18, Flyash 10, waterglass 15, quartz sand 10, kaolin 5, bamboo powder 3, pore creating material 1.Suitable water is added, be put into blender with 130 revs/min of speed stirs into pug, and control moisture content is 15%.
Step 7: by the pug mixed in step 6 be put into pressure be 30Mpa dry-pressing formed machine it is dry-pressing formed, pass through The sponge urban construction water-permeable brick of different shape and size can be made in different molds.
Step 8: molding adobe obtained in step 7 is passed through natural drying or is put into 105 DEG C of freeze-day with constant temperature It is dry in case, so that moisture content is 5%.
Step 9: the adobe after will be dry in step 8 is sent into kiln and is sintered, 1050 are warming up to 3.5 DEG C/min speed DEG C, it is down to room temperature after continuing 3h, finally obtains that compression strength is high, water permeability is good, energy-saving and environment-friendly sponge urban construction is used Water-permeable brick.
After tested, the compression strength of sponge urban construction water-permeable brick of the invention is 55MPa, coefficient of permeability 2.48 × 102Cm/s, grinds anti-length no more than 35mm, 52.5,25 Frozen-thawed cycled compression strength loss of bending strength less than 18%, His index meets " water-permeable brick " (CJ/T945~2005) standard.
Embodiment 2
For handling electroplate factory's heavy metal sewage sludge, implementation steps are further described.
Step 1: heavy metal sewage sludge of the 100Kg moisture content not less than 60% is weighed in acidolysis slot, according to heavy metal sewage sludge Volume 40% be added acid hydrolysis solution, acid hydrolysis solution is with sulfuric acid: nitric acid: hydrofluoric acid: hydrogen peroxide=9:3:3:1 volume ratio prepare and At being sufficiently stirred in adding procedure, make heavy metal ion by Ore Leaching.
Step 2: the mixed liquor in step 1 acidolysis slot is put into ultrasonic tank, ultrasonic wavelength-division is carried out with the frequency of 25KHz Solution, so that sludge and acid hydrolysis solution come into full contact with and react.
Step 3: the mixed liquor after ultrasound in step 2 is separated by solid-liquid separation, pickle liquor is obtained and has acid hydrolysis solution residual Sludge.
Step 4: will there is the remaining sludge clear water of acid hydrolysis solution to rinse in step 3 five times, to slough remaining heavy metal, Obtain innoxious sludge.
Step 5: thering is the liquid after the remaining sludge of acid hydrolysis solution to add for rinsing in the pickle liquor and step 4 in step 3 Enter and mixed in ferrite reaction tank, ferrous sulfate is added, the quality being added is all heavy metal quality in mixed liquor It 10 times, is uniformly mixed, and heat liquid to 60 DEG C.Then, KOH is slowly added into reaction tank, until when pH value is 9 in system, It is passed through high-purity oxygen, is sufficiently generated after reaction and contains the ferrite crystal including ferro element and heavy metal ion;It will finally give birth to At ferrite crystal separated with alkaline waste liquor after dry to get to ferrite, alkaline waste liquor is discharged into waste water treatment system processing Qualified discharge afterwards.
Step 6: by the innoxious sludge isolated in step 4 and steel slag, flyash, quartz sand, waterglass and pore-creating Agent mixes, wherein parts by weight (Kg) are as follows: innoxious sludge is 45, common stone 23, steel slag 15, flyash 8, waterglass 15, stone Sand 10, kaolin 8, bamboo powder 3, pore creating material 1.Suitable water is added, is put into blender and is stirred into 130 revs/min of speed Pug, control moisture content are 16%.
Step 7: by the pug mixed in step 6 be put into pressure be 30Mpa dry-pressing formed machine it is dry-pressing formed, pass through The sponge urban construction water-permeable brick of different shape and size can be made in different molds.
Step 8: molding adobe obtained in step 7 is passed through natural drying or is put into 105 DEG C of freeze-day with constant temperature It is dry in case, so that moisture content is 5%.
Step 9: the adobe after will be dry in step 8 is sent into kiln and is sintered, 1100 are warming up to 4 DEG C/min speed DEG C, it is down to room temperature after continuing 3h, finally obtains that compression strength is high, water permeability is good, energy-saving and environment-friendly sponge urban construction is used Water-permeable brick.
After tested, the compression strength of sponge urban construction water-permeable brick of the invention is 60.5MPa, coefficient of permeability 2.2 × 102Cm/s, grinds anti-length no more than 32mm, 62.5,25 Frozen-thawed cycled compression strength loss of bending strength less than 16%, His index meets " water-permeable brick " (CJ/T945~2005) standard.
Embodiment 3
For handling printed circuit board factory heavy metal sewage sludge, implementation steps are further described.
Step 1: heavy metal sewage sludge of the 100Kg moisture content not less than 60% is weighed in acidolysis slot, according to heavy metal sewage sludge Volume 50% be added acid hydrolysis solution, acid hydrolysis solution is with sulfuric acid: nitric acid: hydrofluoric acid: hydrogen peroxide=9:3:3:1 volume ratio prepare and At being sufficiently stirred in adding procedure, make heavy metal ion by Ore Leaching.
Step 2: the mixed liquor in step 1 acidolysis slot is put into ultrasonic tank, ultrasonic wavelength-division is carried out with the frequency of 30KHz Solution, so that sludge and acid hydrolysis solution come into full contact with and react.
Step 3: the mixed liquor after ultrasound in step 2 is separated by solid-liquid separation, pickle liquor is obtained and has acid hydrolysis solution residual Sludge.
Step 4: the clear water of the sediment in step 3 is rinsed five times, to slough remaining heavy metal, obtain innoxious Sludge.
Step 5: ferrite reaction is added in the liquid after flushing sediment in the pickle liquor and step 4 in step 3 It is mixed in pond, ferrous sulfate is added, the quality being added is 12 times of all heavy metal quality in mixed liquor, and mixing is equal It is even, and liquid is heated to 65 DEG C.Then, NaOH is slowly added into reaction tank, until being passed through high-purity when pH value is 9 in system Oxygen sufficiently generates after reaction and contains the ferrite crystal including ferro element and heavy metal ion;Finally by the ferrite of generation Crystal is dried to arrive ferrite after separating with alkaline waste liquor, and alkaline waste liquor is discharged into qualified discharge after waste water treatment system processing.
Step 6: by the innoxious sludge isolated in step 4 and steel slag, flyash, quartz sand, waterglass and pore-creating Agent mixing, innoxious sludge are 45, common stone 23, steel slag 18, flyash 10, waterglass 15, quartz sand 12, kaolin 8, bamboo Powder 4, pore creating material 3.Suitable water is added, is put into blender and pug is stirred into 130 revs/min of speed, control moisture content is 18%.
Suitable water is added, is put into blender and pug is stirred into 130 revs/min of speed, control moisture content is 18%.
Step 7: by the pug mixed in step 6 be put into pressure be 30Mpa dry-pressing formed machine it is dry-pressing formed, pass through The sponge urban construction water-permeable brick of different shape and size can be made in different molds.
Step 8: molding adobe obtained in step 7 is passed through natural drying or is put into 105 DEG C of freeze-day with constant temperature It is dry in case, so that moisture content is 5%.
Step 9: the adobe after will be dry in step 8 is sent into kiln and is sintered, 1150 are warming up to 4 DEG C/min speed DEG C, it is down to room temperature after continuing 3h, finally obtains that compression strength is high, water permeability is good, energy-saving and environment-friendly sponge urban construction is used Water-permeable brick.
After tested, the compression strength of sponge urban construction water-permeable brick of the invention is 62MPa, coefficient of permeability 2.8 × 102Cm/s, grinds anti-length no more than 28mm, 56.0,25 Frozen-thawed cycled compression strength loss of bending strength less than 15%, His index meets " water-permeable brick " (CJ/T945~2005) standard.
Embodiment 4
Embodiment 4 is similar with 1 step of embodiment, sulfuric acid, nitric acid, hydrofluoric acid and hydrogen peroxide 8:2 by volume in acid hydrolysis solution: 2:1 is prepared, and the volume that acid hydrolysis solution is added is the 30% of heavy metal sewage sludge volume;The frequency of oscillation of ultrasonic wave is 15KHz, when oscillation Between be 1h;The number that clear water rinses is 3 times;The additive amount of ferrous sulfate is 8 times of heavy metal gross mass in liquid, heats liquid For temperature to 55 DEG C, lye NaOH, the pH value that lye amount is added to liquid is 8.5;Innoxious sludge, common stone, steel slag, powder Coal ash, waterglass, quartz sand, kaolin, bamboo powder and pore creating material weight part ratio are as follows: 40,20,15,8,12,10,5,3 and 1, mud The moisture control of material is in 14wt%.Steel slag and quartz sand cross 10 meshes, and the partial size of flyash is 0.1mm, and pore creating material is pearl Rock.The pressure of dry-pressing formed machine is 25Mpa.Drying box is thermostatic drying chamber, and temperature is 103 DEG C, the moisture content of adobe after drying For 5wt%.1020 DEG C are warming up to the speed of 3.5 DEG C/min when sintering, is down to room temperature after being persistently sintered 2.5h.
After tested, meet " water-permeable brick " (CJ/T945~2005) standard.
Embodiment 5
Embodiment 5 is similar with 1 step of embodiment, sulfuric acid, nitric acid, hydrofluoric acid and hydrogen peroxide 9:3 by volume in acid hydrolysis solution: 3:1 is prepared, and the volume that acid hydrolysis solution is added is the 35% of heavy metal sewage sludge volume;The frequency of oscillation of ultrasonic wave is 20KHz, when oscillation Between be 1.5h;The number that clear water rinses is 4 times;The additive amount of ferrous sulfate is 10 times of heavy metal gross mass in liquid, heating For fluid temperature to 60 DEG C, lye KOH, the pH value that lye amount is added to liquid is 9;Innoxious sludge, common stone, steel slag, Flyash, waterglass, quartz sand, kaolin, bamboo powder and pore creating material parts by weight are as follows: 43,22,16,9,13,11,7,4 and 2, mud The moisture control of material is in 16wt%.Steel slag and quartz sand cross 10 meshes, and the partial size of flyash is 0.12mm, and pore creating material is diatom Soil.The pressure of dry-pressing formed machine is 30Mpa.Drying box is thermostatic drying chamber, and temperature is 105 DEG C, the moisture content of adobe after drying For 4wt%.1040 DEG C are warming up to the speed of 3.8 DEG C/min when sintering, is down to room temperature after being persistently sintered 3h.
After tested, meet " water-permeable brick " (CJ/T945~2005) standard.
Embodiment 6
Embodiment 6 is similar with 1 step of embodiment, sulfuric acid, nitric acid, hydrofluoric acid and hydrogen peroxide by volume 10 in acid hydrolysis solution: 4:4:1 is prepared, and the volume that acid hydrolysis solution is added is the 50% of heavy metal sewage sludge volume;The frequency of oscillation of ultrasonic wave is 30KHz, oscillation Time is 2h;The number that clear water rinses is 5 times;The additive amount of ferrous sulfate is 12 times of heavy metal gross mass in liquid, heating For fluid temperature to 65 DEG C, lye NaOH, the pH value that lye amount is added to liquid is 9;Innoxious sludge, common stone, steel slag, Flyash, waterglass, quartz sand, kaolin, bamboo powder and pore creating material parts by weight are as follows: 45,23,18,10,15,12,8,4 and 3, The moisture control of pug is in 18wt%.Steel slag and quartz sand cross 10 meshes, and the partial size of the flyash is 0.15mm, pore-creating Agent is to boil stone.The pressure of dry-pressing formed machine is 35Mpa.Drying box is thermostatic drying chamber, and temperature is 108 DEG C, adobe after drying Moisture content position 5wt%.1150 DEG C are warming up to the speed of 4.0 DEG C/min when sintering, is down to room temperature after being persistently sintered 3.5h.
After tested, meet " water-permeable brick " (CJ/T945~2005) standard.

Claims (10)

1. a kind of water-permeable brick prepared using innoxious sludge, which is characterized in that including following components and parts by weight content:
Innoxious sludge 40-45, common stone 20-23, steel slag 15-18, flyash 8-10, waterglass 12-15, quartz sand 10- 12, kaolin 5-8, bamboo powder 3-4 and pore creating material 1-3,
The innoxious sludge is prepared by following steps:
(1) acid hydrolysis solution stirring is added in heavy metal sewage sludge, reacts heavy metal ion with acid and is leached, pH is adjusted in system When 2.2-3.2, acidolysis reaction terminates;
(2) mixed liquor of step (1) is subjected to ultrasonication, sludge and acid hydrolysis solution is made to come into full contact with and react;
(3) mixed liquor after ultrasound in step (2) is separated by solid-liquid separation, obtains acid hydrolysis solution and remains the sludge of acid hydrolysis solution;
(4) sludge of residual acid hydrolysis solution in step (3) is rinsed with clear water, sloughs remaining acid hydrolysis solution and heavy metal, obtains Innoxious sludge;
(5) liquid generated after the acid hydrolysis solution and the middle sludge for rinsing residual acid hydrolysis solution of step (4) in step (3) is mixed It closes, ferrous sulfate is added, be uniformly mixed and heat, add lye, and be passed through oxygen, sufficiently generated after reaction and contain ferro element With the ferrite crystal of heavy metal ion, ferrite crystal is separated with alkaline waste liquor, is dried, and obtains ferrite, at alkaline waste liquor Manage qualified discharge;
Acid hydrolysis solution described in step (1) be sulfuric acid, nitric acid, hydrofluoric acid and hydrogen peroxide mixture, sulfuric acid, nitric acid, hydrofluoric acid and 8-10:2-4:2-4:1 is prepared hydrogen peroxide by volume, and the volume that acid hydrolysis solution is added is the 30-50% of heavy metal sewage sludge volume, step Suddenly the additive amount of ferrous sulfate described in (5) is 8-12 times of heavy metal gross mass in liquid, heating fluid temperature to 55-65 DEG C, the lye is NaOH or KOH, and the pH value that lye amount is added to liquid is 8.5-9.
2. a kind of water-permeable brick prepared using innoxious sludge according to claim 1, which is characterized in that the steel slag 10 meshes, partial size≤0.15mm of the flyash are crossed with quartz sand.
3. a kind of water-permeable brick prepared using innoxious sludge according to claim 1, which is characterized in that the pore-creating Agent is perlite, diatomite, rice husk or boils stone.
4. the preparation method that one kind prepares water-permeable brick using innoxious sludge as described in claim 1, which is characterized in that specific The following steps are included:
(1) acid hydrolysis solution stirring is added in heavy metal sewage sludge, reacts heavy metal ion with acid and is leached, pH is adjusted in system When 2.2-3.2, acidolysis reaction terminates;
(2) mixed liquor of step (1) is subjected to ultrasonication, sludge and acid hydrolysis solution is made to come into full contact with and react;
(3) mixed liquor after ultrasound in step (2) is separated by solid-liquid separation, obtains acid hydrolysis solution and remains the sludge of acid hydrolysis solution;
(4) sludge of residual acid hydrolysis solution in step (3) is rinsed with clear water, sloughs remaining acid hydrolysis solution and heavy metal, obtains Innoxious sludge;
(5) liquid generated after the acid hydrolysis solution and the middle sludge for rinsing residual acid hydrolysis solution of step (4) in step (3) is mixed It closes, ferrous sulfate is added, be uniformly mixed and heat, add lye, and be passed through oxygen, sufficiently generated after reaction and contain ferro element With the ferrite crystal of heavy metal ion, ferrite crystal is separated with alkaline waste liquor, is dried, and obtains ferrite, at alkaline waste liquor Manage qualified discharge;
(6) the innoxious sludge for obtaining step (4) and common stone, steel slag, flyash, waterglass, quartz sand, kaolin, Bamboo powder and pore creating material stir into pug after mixing by charge ratio, and control moisture content;
(7) pug of step (6) is put into dry-pressing formed machine is dry-pressing formed, the permeable brick adobe of different shape and size is made;
(8) permeable brick adobe obtained in step (7) is dry by spontaneously drying or being put into drying box;
(9) the permeable brick adobe of step (8) after dry is sintered to get water-permeable brick is arrived.
5. the preparation method according to claim 4 for preparing water-permeable brick using innoxious sludge, which is characterized in that step (1) acid hydrolysis solution described in is the mixture of sulfuric acid, nitric acid, hydrofluoric acid and hydrogen peroxide, and sulfuric acid, nitric acid, hydrofluoric acid and hydrogen peroxide are pressed Volume ratio 8-10:2-4:2-4:1 is prepared, and the volume that acid hydrolysis solution is added is the 30-50% of heavy metal sewage sludge volume.
6. the preparation method according to claim 4 for preparing water-permeable brick using innoxious sludge, which is characterized in that step (2) frequency of oscillation of the ultrasonic wave described in is 15-30KHz, duration of oscillation 1-2h, the number that step (4) clear water rinses It is 3-5 times.
7. the preparation method according to claim 4 for preparing water-permeable brick using innoxious sludge, which is characterized in that step (5) additive amount of the ferrous sulfate described in is 8-12 times of heavy metal gross mass in liquid, heating fluid temperature to 55-65 DEG C, The lye is NaOH or KOH, and the pH value that lye amount is added to liquid is 8.5-9.
8. the preparation method according to claim 4 for preparing water-permeable brick using innoxious sludge, which is characterized in that step (6) for the moisture control of the pug in 14-18wt%, the pressure of dry-pressing formed machine described in step (7) is 25-35Mpa.
9. the preparation method according to claim 4 for preparing water-permeable brick using innoxious sludge, which is characterized in that step (8) drying box described in is thermostatic drying chamber, and temperature is 103-108 DEG C, and the moisture content of adobe is not more than 6wt% after drying.
10. the preparation method according to claim 4 for preparing water-permeable brick using innoxious sludge, which is characterized in that step (9) it is warming up to 1020-1150 DEG C with the speed of 3.5-4.0 DEG C/min when being sintered, is down to room temperature after being persistently sintered 2.5-3.5h.
CN201610663310.0A 2016-08-12 2016-08-12 Utilize the water-permeable brick and preparation method thereof of heavy metal sewage sludge preparation Active CN106278373B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201610663310.0A CN106278373B (en) 2016-08-12 2016-08-12 Utilize the water-permeable brick and preparation method thereof of heavy metal sewage sludge preparation

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201610663310.0A CN106278373B (en) 2016-08-12 2016-08-12 Utilize the water-permeable brick and preparation method thereof of heavy metal sewage sludge preparation

Publications (2)

Publication Number Publication Date
CN106278373A CN106278373A (en) 2017-01-04
CN106278373B true CN106278373B (en) 2019-04-30

Family

ID=57669413

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201610663310.0A Active CN106278373B (en) 2016-08-12 2016-08-12 Utilize the water-permeable brick and preparation method thereof of heavy metal sewage sludge preparation

Country Status (1)

Country Link
CN (1) CN106278373B (en)

Families Citing this family (18)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106631122B (en) * 2017-01-06 2019-10-15 山西晟科微生物建材科技有限公司 Sintered coal ash expanded perlite water-permeable brick and preparation method thereof
CN109665798A (en) * 2017-10-14 2019-04-23 梁秋云 A kind of pavement water-permeable brick prepared using construction waste
CN107879586A (en) * 2017-10-18 2018-04-06 福建汇利丰环保科技有限公司 The waste sludge recovery process of discarded Tetra Pak processing
CN108046831A (en) * 2017-12-07 2018-05-18 广州市环境保护工程设计院有限公司 A kind of multi-functional water-permeable brick and preparation method thereof
CN108285323A (en) * 2017-12-07 2018-07-17 广州市环境保护工程设计院有限公司 A kind of water-permeable brick and preparation method thereof prepared using sludge
CN108275854A (en) * 2018-01-22 2018-07-13 湖北工业大学 Added with the alkaline residue base domestic sludge curing agent of high hydroscopic resin
CN110272232A (en) * 2018-03-16 2019-09-24 焦作诺尔曼炉业有限公司 A kind of permeable building block in road surface of environmental protection and preparation method thereof
CN108585773A (en) * 2018-05-16 2018-09-28 合肥慧林建材有限公司 A kind of high intensity high water-permeability pavior brick and preparation method thereof
CN108863400A (en) * 2018-06-21 2018-11-23 湖南双晟科技信息咨询有限公司 A method of water-permeable brick is prepared using municipal sludge
CN110885241A (en) * 2018-09-07 2020-03-17 何钢 Mullite-structure ceramic porous water storage material and preparation method thereof
CN109694234A (en) * 2019-02-26 2019-04-30 北京建筑大学 The method for preparing water-permeable brick using waterworks sludge
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
CN110304870A (en) * 2019-08-12 2019-10-08 广东工业大学 A kind of baking-free water-permeable brick and preparation method thereof
CN110723961A (en) * 2019-09-23 2020-01-24 广东莞绿环保工程有限公司 Environment-friendly microporous brick prepared by comprehensively utilizing solid wastes and preparation method thereof
CN113336460B (en) * 2021-06-28 2022-05-06 武汉理工大学 Functional aggregate for radiation-proof concrete and preparation method thereof
CN113332965B (en) * 2021-07-12 2022-11-18 新疆大学 Magnetic fly ash @ PDMS sponge material for oil-water separation and preparation method thereof
CN114772883B (en) * 2022-05-16 2023-09-05 中国矿业大学 Treatment method of black and odorous water body substrate sludge and application of black and odorous water body substrate sludge in preparation of baking-free bricks
CN115536426A (en) * 2022-10-14 2022-12-30 宝武环科(湛江)资源循环利用有限公司 Ecological water-permeable sintered brick taking all-solid waste as raw material and preparation method thereof

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102040238A (en) * 2010-11-11 2011-05-04 上海集惠环保科技发展有限公司 Recycling method for treating sludge containing heavy metals
CN105330324A (en) * 2015-10-29 2016-02-17 合肥正拓装饰材料有限公司 Water-permeable brick adding with steel slags for road surfacing

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102040238A (en) * 2010-11-11 2011-05-04 上海集惠环保科技发展有限公司 Recycling method for treating sludge containing heavy metals
CN105330324A (en) * 2015-10-29 2016-02-17 合肥正拓装饰材料有限公司 Water-permeable brick adding with steel slags for road surfacing

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
利用给水厂污泥制备透水砖的实验研究;谢敏等;《环境工程学报》;20130531;第7卷(第5期);全文

Also Published As

Publication number Publication date
CN106278373A (en) 2017-01-04

Similar Documents

Publication Publication Date Title
CN106278373B (en) Utilize the water-permeable brick and preparation method thereof of heavy metal sewage sludge preparation
CN104190690B (en) A kind of method and application that utilizes ammonia-soda process alkaline residue to prepare dechlorination alkaline residue mixture
CN102614620B (en) Wet detoxification method of hexavalent chromium contained alkali waste residues
CN105622023B (en) A kind of sludge curing agent using clinker
CN108160684B (en) Combined remediation method for chromium-polluted soil
CN108774041A (en) A kind of water-permeable brick and preparation method thereof for making aggregate with artificial carbonization slag bead
CN113213789B (en) Paving brick prepared based on household garbage incineration fly ash and preparation method thereof
CN104803655A (en) Method for producing cement-based composite material for injection reinforcement from waste incineration fly ash
CN108609874A (en) A kind of preparation method of copper ashes base inorganic coagulation material
CN114292124A (en) Ceramsite fired by fly ash and preparation method and application thereof
CN116283142B (en) Commercial mixing station carbon fixation ready-mixed concrete and preparation method thereof
CN106518150B (en) A kind of composite haydite of clean water sludge and diatomite preparation
CN105294156B (en) A kind of resource utilization method of domestic waste incineration residue sorting tailings
CN107488019A (en) A kind of non-sintered gold tailings brick and its preparation technology
CN107759174A (en) It is a kind of to utilize method of the precuring prepared from steel slag for Artificial fish reef concrete that be carbonated
CN110668773B (en) Landfill seepage-proofing barrier material and preparation method thereof
CN103896541A (en) Soil curing agent
CN104591696A (en) Blast furnace heavy slag heat-preservation ceramsite and preparation method thereof
CN109734377A (en) A kind of energy saving and environment friendly construction material and preparation method thereof
CN105622022B (en) A kind of sludge curing agent using alkaline residue
CN115849824B (en) Electric furnace nickel slag carbon fixation and high-value utilization method thereof in concrete
CN115448655B (en) Pavement base material based on construction waste and preparation method thereof
CN106495511A (en) Process for preparing cementing material by using electroplating sludge
CN106811201A (en) A kind of magnesium oxide-based curing agent and its application process
CN110330360A (en) A kind of novel light aggregate foaming agent and preparation method thereof

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant