CN109133778A - The preparation method of residual active sludge and mud mixed type foamed plastics lightweight concrete - Google Patents

The preparation method of residual active sludge and mud mixed type foamed plastics lightweight concrete Download PDF

Info

Publication number
CN109133778A
CN109133778A CN201810966580.8A CN201810966580A CN109133778A CN 109133778 A CN109133778 A CN 109133778A CN 201810966580 A CN201810966580 A CN 201810966580A CN 109133778 A CN109133778 A CN 109133778A
Authority
CN
China
Prior art keywords
active sludge
residual active
mud
weight
added
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.)
Granted
Application number
CN201810966580.8A
Other languages
Chinese (zh)
Other versions
CN109133778B (en
Inventor
张健
胡晨晨
顾云凡
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.)
Nanjing Institute of Technology
Original Assignee
Nanjing Institute of Technology
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Nanjing Institute of Technology filed Critical Nanjing Institute of Technology
Priority to CN201810966580.8A priority Critical patent/CN109133778B/en
Publication of CN109133778A publication Critical patent/CN109133778A/en
Application granted granted Critical
Publication of CN109133778B publication Critical patent/CN109133778B/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
    • C04B28/00Compositions of mortars, concrete or artificial stone, containing inorganic binders or the reaction product of an inorganic and an organic binder, e.g. polycarboxylate cements
    • C04B28/02Compositions of mortars, concrete or artificial stone, containing inorganic binders or the reaction product of an inorganic and an organic binder, e.g. polycarboxylate cements containing hydraulic cements other than calcium sulfates
    • C04B28/04Portland cements
    • 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
    • C02F11/02Biological treatment
    • C02F11/04Anaerobic treatment; Production of methane by such processes
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/18Treatment of sludge; Devices therefor by thermal conditioning
    • 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
    • C04B28/00Compositions of mortars, concrete or artificial stone, containing inorganic binders or the reaction product of an inorganic and an organic binder, e.g. polycarboxylate cements
    • C04B28/02Compositions of mortars, concrete or artificial stone, containing inorganic binders or the reaction product of an inorganic and an organic binder, e.g. polycarboxylate cements containing hydraulic cements other than calcium sulfates
    • 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
    • C04B2111/00Mortars, concrete or artificial stone or mixtures to prepare them, characterised by specific function, property or use
    • C04B2111/20Resistance against chemical, physical or biological attack
    • C04B2111/27Water resistance, i.e. waterproof or water-repellent materials
    • 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
    • C04B2111/00Mortars, concrete or artificial stone or mixtures to prepare them, characterised by specific function, property or use
    • C04B2111/40Porous or lightweight materials
    • 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
    • C04B2201/00Mortars, concrete or artificial stone characterised by specific physical values
    • C04B2201/20Mortars, concrete or artificial stone characterised by specific physical values for the density
    • 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
    • C04B2201/00Mortars, concrete or artificial stone characterised by specific physical values
    • C04B2201/50Mortars, concrete or artificial stone characterised by specific physical values for the mechanical strength

Abstract

The invention discloses the preparation methods of residual active sludge and mud mixed type foamed plastics lightweight concrete, residual active sludge and mud is taken to be placed in anaerobic sludge pond, add distilled water and surfactant, then white lime and sodium thiosulfate are added, anaerobic fermentation after stirring, it is passed through oxygen again and cationic polyacrylamide is added, then carries out heated at constant temperature, saturation FeCl is added dropwise3Solution, alkaline fungicide is added after stirring, it is first placed in high pressure sterilization kettle and handles, it is ultrasonically treated again, curing agent cement, adhesive, chelating agent, flyash and fiber are added after being finally separated by solid-liquid separation, raw material soil paste is obtained after being stirred, and light material then is added and silicon powder obtains lightweight concrete.The present invention can be effectively improved the mechanical property of lightweight concrete, and lightweight concrete intensity obtained is high, and commodity are not easy to crack, have waterproof performance, can be widely applied to construction industry, play promotion and impetus for the effective use of residual active sludge and dredging silt.

Description

The preparation method of residual active sludge and mud mixed type foamed plastics lightweight concrete
Technical field
The invention belongs to transportation building engineering material technical fields, mixed more particularly to a kind of residual active sludge and mud The preparation method of mould assembly formed plastic light concrete.
Background technique
Residual active sludge is from the activated sludge outside secondary sedimentation tank (or settling zone) discharge system.In biochemical treatment Cheng Zhong, the microorganism in activated sludge constantly consume the organic substance in waste water.In the organic substance being consumed, a part It being oxidized with energy needed for providing microbial life activity, another part is then utilized by microorganism to synthesize new cytoplasm, To make microbial proliferation reproduction, microorganism is while metabolism, and some old microorganism is dead, therefore produces Residual active sludge.Residual active sludge is the by-product generated in sewage disposal process, the basic improvement of residual active sludge Outlet is resource utilization.
China is limited currently used for the earthwork resource of engineering construction, and China coast harbour coastal engineering, cruiseway are dredged Starting for engineering and inland lake environmental improvement engineering is dredged, the generation of a large amount of dredging silt has become certainty.But it dredges It dredges the nearest of mud and abandons that the pollutant buried can generate when occupying cultivated land, stacking is spread, the environment such as polluted river and marine environment are asked Topic, therefore environmental pollution brought by the dredging silt largely generated, it has also become our current urgent problems to be solved.
The soil source of current formed plastic light concrete is generally dredging silt, the bubble prepared using dredging silt Foam plastics lightweight concrete has soil property light, and the high feature of intensity, general wet density theoretical value is between 0.5-1.2g/cm3Between, Dry density theoretical value is between 0.4-0.8 g/cm3Between, 28 days theoretical value intensity can disappear generally between 100-1000kPa Change dredging silt, used foamed plastics, there is waste utilization and environmental protection double benefit.
But in practical applications, it is mixed often to there is such as low strength, commodity for existing formed plastic light concrete The problems such as solidifying soil cracking or water suction, seriously affect its being widely used in construction industry.How formed plastic light is effectively improved The intensity of concrete prevents crack in commodity concrete, reduces its water imbibition, at the same realize residual active sludge and dredging silt this The comprehensive utilization of two kinds of wastes is an important technological problems urgently to be resolved at present.
Summary of the invention
The purpose of the present invention is for low strength existing for existing formed plastic light concrete, product cracking or water suction The problems such as, the preparation method of a kind of residual active sludge and mud mixed type foamed plastics lightweight concrete is provided, which is effectively improved The mechanical property of lightweight concrete, lightweight concrete intensity obtained is high, and commodity are not easy to crack, has waterproof performance, can be extensive Applied to construction industry, promotion and impetus are played for the effective use of residual active sludge and dredging silt.
The present invention is achieved by the following technical solutions:
The preparation method of residual active sludge and mud mixed type foamed plastics lightweight concrete, comprising the following steps:
(1) residual active sludge of 20-40 parts by weight and the mud merging anaerobic sludge pond of 40-60 parts by weight are taken, distilled water is added After dilution, surfactant is added, is stood overnight after stirring 4-5 h, obtains mixed liquor I;
(2) white lime of 10-20 parts by weight and the thiosulfuric acid of 5-10 parts by weight are added in the mixed liquor I obtained to step (1) Sodium stirs at a temperature of 45-50 DEG C, and anaerobic fermentation 2-3 days to mixed liquor I in sposh state;Oxygen is passed through again to carry out at aeration Reason, and the cationic polyacrylamide that 3-8 parts by weight are added is dehydrated mud mixture, after separation of solid and liquid, washes Solid content 2-3 It is secondary, obtain deodorization residual active sludge and mud mixed liquor II;
(3) heated at constant temperature at a temperature of the mixed liquor II for obtaining step (2) is placed in 60-70 DEG C, is added dropwise mass fraction 4- 8% saturation FeCl3Solution, it is stirring while adding, it stands overnight at room temperature, obtains modified residual active sludge and mud mixed liquor Ⅲ;
(4) the alkaline fungicide of mass fraction 5-10% is added in the mixed liquor III that step (3) obtains, first sets after mixing evenly Enter in high pressure sterilization kettle and inactivate 45-60min at 120-130 DEG C, after carry out ultrasonic treatment 1-2h again, finally carry out solid-liquid point From washing Solid content obtains inactivating modified residual active sludge and mud mixed liquor IV;
(5) the curing agent cement of 10-20 parts by weight, the bonding of 2-5 parts by weight are added in the mixed liquor IV that step (4) obtains Agent, the chelating agent of 1-5 parts by weight, the flyash of 5-10 parts by weight and the fiber of 5-10 parts by weight, through blender at mixing Raw material soil paste is obtained after uniform stirring mixing in reason device;
(6) light material of 1-5 parts by weight and the silicon powder of 4-10 parts by weight are added in the raw material soil paste that step (5) obtains, stirs Residual active sludge and mud mixed type foamed plastics particle light mixed soil are obtained after mixing uniformly.
The technical solution that the present invention further solves is that the additional amount of distilled water described in step (1) is that residual activity is dirty The 40-50% of mud and mud total weight, the additional amount of the surfactant are the 4- of residual active sludge and mud total weight 6%。
The technical solution that the present invention further solves is that the surfactant includes dodecyl sodium sulfate, dodecane One of base sodium sulphate, cetyl trimethylammonium bromide or 4 bromide are a variety of.
The technical solution that the present invention further solves is that the muddy water of sposh state is mixed in Air Exposure described in step (2) Closing dissolved oxygen content in object is 2.0-2.5mg/L.
The technical solution that the present invention further solves is that alkalinity fungicide described in step (4) is lime sulfur or bohr More liquid.
The technical solution that the present invention further solves is that in ultrasonic treatment described in step (4), the frequency of ultrasonic wave is 30-40 KHz, ultrasound intensity 80-100DB.
The technical solution that the present invention further solves is, in step (5), the curing agent cement include portland cement, Any one of pozzolan cement, portland blast-furnace slag cement;Described adhesive includes starch-hydrocolloid or polyethylene glycol colloid;The chela Mixture is cyclic chelators;The fiber is the basalt fibre that is chopped.
The technical solution that the present invention further solves is that the cyclic chelators include that porphyrin analog derivative or crown ether-like are spread out Biology;The chopped basalt fibre length is 5-10mm, density 3.0-3.5g/cm3
The technical solution that the present invention further solves is that light material described in step (6) includes expanded polystyrene (EPS) Any one of grain, waste plastic foam and waste tire particle.
The technical solution that the present invention further solves is that the density of the expanded polystyrene particle is 0.02-0.04g/ cm3, partial size 1-3mm.
Method of the present invention, step (1) is middle to be added surfactant, the live end and residual activity of surfactant The affine absorption of biological surface in sludge and dredging silt, is then presented lipophilicity without live end, make residual active sludge and Substance in dredging silt is uniformly dispersed, and is conducive to handle in next step;In step (2) be passed through oxygen can effective deodorization, make residue Biomass in activated sludge and dredging silt corrupt will not foul, and becoming residual active sludge applied to lightweight concrete can Energy;Saturation FeCl is added dropwise in step (3)3Solution forms ferric hydroxide colloid, and ferric hydroxide colloid makes residual active sludge and dredges It dredges mud and generates gelatinization results, micro- aggregation that gelling forms ionic bond absorption is cementing, and cementing micro- aggregation is in evenly dispersed shape State is conducive to handle in next step;Alkaline fungicide is added in step (4), the hydrochloric acid that on the one hand can be generated in neutralization procedure (3), separately On the one hand sterilization inactivation treatment can be further carried out to residual active sludge and dredging silt, ultrasound is combined with what is be separated by solid-liquid separation Using realizing the high-efficiency dehydration to residual active sludge and dredging silt;It becomes silted up in step (5) in residual active sludge and dredging After curing agent cement is added in mud, curing agent cement particle aquation generates silicate cement compound, with residual active sludge and dredging The cementing biggish granule body of formation of micro- aggregation in mud, meanwhile, web trellis, the rod of the generation of curing agent hydrated cementitious Shape, hexagonal plate product are filled in the hole between granule body, and it is chain to play the role of drawknot, and residual active sludge and dredging are become silted up The microstructure of mud is transformed into extremely strong network-like cement structure, and the raw material soil paste in the present invention plays skeleton function, is used for Undertake most load;The addition of portland cement in curing agent cement increases the free hydroxyl in raw material, promotes Reaction between each material composition, meanwhile, hydrated calcium silicate can be equally generated after hydrated cementitious, can also further increase gelling The generation of substance guarantees the gelatinization results of raw material obtained to the greatest extent, has wider application range;Flyash is added Afterwards, the silica in flyash, aluminium oxide are reacted with the inorganic matter in residual active sludge and dredging silt, generate aquation silicic acid Calcium and drated calcium aluminate promote the generation of gum material;The addition of adhesive and chelating agent further enhances micro- aggregation glue The crosslinked action of knot, starch-hydrocolloid or polyethylene glycol colloid in adhesive play the role of physical adherence, and chelating agent then plays The effect of chemical adhesion, the two complement each other, make micro- aggregation it is cementing between cross link force it is strong, granule body stable structure;Fiber It is added, further enhances the skeleton function of raw material soil paste, fiber inhibits to shrink, increases toughness, and skeleton is made to undertake load capacity It further enhances, while guaranteeing that commodity are not easy to crack;There is the particle of light material metathesis and space to imitate in step (6) It answers, reduces a part of intensity of raw material soil paste skeleton, so that soil property lightens, while playing waterproof performance;The addition of silicon powder rises To catalysis, early cure material effects;The silicon powder in flyash and step (6) in step (5) interacts, and is effectively improved original The mechanical property for expecting soil paste, makes raw material soil paste unconfined compressive strength reach as high as 400kPa, while cost is reduced, into one Step expands the application field of lightweight concrete.
The invention has the benefit that
1, a kind of preparation method of residual active sludge and mud mixed type foamed plastics lightweight concrete provided by the invention, the method have Effect improves the mechanical property of lightweight concrete, and lightweight concrete intensity obtained is high, and commodity are not easy to crack, has waterproof performance, It can be widely applied to construction industry, play promotion and impetus for the effective use of residual active sludge and dredging silt.
2, alkaline fungicide is added in the present invention in processing step, on the one hand can neutralize the hydrochloric acid of generation, on the other hand may be used Sterilization inactivation treatment, ultrasound and the use in conjunction being separated by solid-liquid separation further are carried out to residual active sludge and dredging silt, it is real The high-efficiency dehydration to residual active sludge and dredging silt is showed.
3, curing agent cement is added in residual active sludge and dredging silt and forms biggish granule body by the present invention, together When, web trellis, rod shape, the hexagonal plate product of curing agent hydrated cementitious generation are filled in the hole between granule body, It is chain to play the role of drawknot;After flyash is added, silica, aluminium oxide and residual active sludge and dredging silt in flyash In inorganic matter reaction, generate hydrated calcium silicate and drated calcium aluminate, promote the generation of gum material.
4, the present invention in adhesive and chelating agent addition, further enhance the cementing crosslinked action of micro- aggregation, glue Starch-hydrocolloid or polyethylene glycol colloid in mixture play the role of physical adherence, and chelating agent then plays chemical adhesion, The two complements each other, make micro- aggregation it is cementing between cross link force it is strong, granule body stable structure.
5, the particle of light material has metathesis and three-dimensional effect in the present invention, reduces the one of raw material soil paste skeleton Partial intensities so that soil property lightens, while playing waterproof performance;Catalysis, early cure material effects are played in the addition of silicon powder; Flyash and silicon powder interact, and are effectively improved the mechanical property of raw material soil paste, make raw material soil paste unconfined compressive strength highest Up to 400kPa, while cost is reduced, the further expansion application field of lightweight concrete.
Specific embodiment
Summary of the invention of the invention is further described below with reference to embodiment.
Embodiment 1
The preparation method of residual active sludge and mud mixed type foamed plastics lightweight concrete, comprising the following steps:
(1) residual active sludge of 20 parts by weight and the mud merging anaerobic sludge pond of 40 parts by weight are taken, distilled water is added to dilute, The additional amount of distilled water is the 40% of residual active sludge and mud total weight, adds dodecyl sodium sulfate, dodecyl sulphur The addition weight of sour sodium is the 4% of residual active sludge and mud total weight, stands overnight after stirring 4h, obtains mixed liquor I;
(2) white lime and 5 parts by weight sodium thiosulfate of 10 parts by weight are added into mixed liquor I, is stirred, and temperature is maintained at 45 DEG C, anaerobic fermentation 2 days, until mixed liquor I is in sposh state, then it is passed through oxygen, carries out Air Exposure, make the muddy water of sposh state Dissolved oxygen reaches 2.0mg/L in mixture, adds the cationic polyacrylamide of 3 parts by weight, is dehydrated mud mixture, from It after the heart, washes Solid content 2 times, then is centrifuged to get deodorization residual active sludge and mud mixed liquor II is arrived;
(3) saturation for being equivalent to II weight 4% of mixed liquor is added dropwise in the at a temperature of heated at constant temperature by mixed liquor II at 60 DEG C FeCl3Solution, it is stirring while adding, it is saturated FeCl3It after solution is added, is stored at room temperature overnight, obtains modified residual active sludge With mud mixed liquor III;
(4) lime sulfur for being equivalent to III weight 5% of mixed liquor is added in mixed liquor III, is placed in high pressure sterilization after mixing evenly 45min is inactivated in kettle at 121 DEG C, then ultrasonic treatment 1h is carried out using low frequency high-strength ultrasonic, control ultrasonic power is 30KHz, ultrasound intensity 80DB, is then separated by solid-liquid separation, and is washed Solid content, then be centrifuged, is obtained inactivating modified residual activity Sludge and mud mixed liquor IV;
(5) portland cement of 10 parts by weight, the starch-hydrocolloid of 2 parts by weight, the ring-type of 1 parts by weight are added in mixed liquor IV The chopped basalt fibre of chelating agent, the flyash of 5 parts by weight and 5 parts by weight is carried out in hybrid processor by blender It is stirred, until being uniformly mixing to obtain raw material soil paste;The cyclic chelators are porphyrin analog derivative, the chopped basalt Fibre length is 5mm, density 3.0g/cm3
(6) silicon powder of the expanded polystyrene particle of 1 parts by weight and 4 parts by weight is added to the soil of the raw material in hybrid processor In slurry, residual active sludge and mud mixed type foamed plastics particle light mixed soil are then obtained after mixing evenly;The hair The density of foamed polystyrene particle is 0.03g/cm3, partial size 2mm.
Show by test: the residual active sludge and mud mixed type foamed plastics lightweight that the present embodiment is prepared are mixed Solidifying soil conserves under standard atmospheric pressure, 20 DEG C of the temperature standard conditions with humidity 100%, and the real density of 28d is 0.942g/cm3, Unconfined compressive strength is 389kPa, and the total amount of the cementitious material of lightweight concrete is suitable in product, makes lightweight concrete surface Closely knit solidification will not generate the crack caused by dry shrink while having water-proof function, receive in addition, fiber can play inhibition Contracting, the effect for increasing toughness, therefore the product prepared is not easy to crack, good product quality, use scope is extensive.
Embodiment 2
The preparation method of residual active sludge and mud mixed type foamed plastics lightweight concrete, comprising the following steps:
(1) residual active sludge of 40 parts by weight and the mud merging anaerobic sludge pond of 60 parts by weight are taken, distilled water is added to dilute, The additional amount of distilled water is the 50% of residual active sludge and mud total weight, adds cetyl trimethylammonium bromide, 16 The addition weight of alkyl trimethyl ammonium bromide is the 6% of residual active sludge and mud total weight, stands overnight, obtains after stirring 5h To mixed liquor I;
(2) white lime and 10 parts by weight sodium thiosulfate of 20 parts by weight are added into mixed liquor I, is stirred, and temperature is maintained at 50 DEG C, anaerobic fermentation 3 days, until mixed liquor I is in sposh state, then it is passed through oxygen, carries out Air Exposure, make the muddy water of sposh state Dissolved oxygen reaches 2.5mg/L in mixture, adds the cationic polyacrylamide of 8 parts by weight, is dehydrated mud mixture, from It after the heart, washes Solid content 3 times, then is centrifuged to get deodorization residual active sludge and mud mixed liquor II is arrived;
(3) saturation for being equivalent to II weight 8% of mixed liquor is added dropwise in the at a temperature of heated at constant temperature by mixed liquor II at 70 DEG C FeCl3Solution, it is stirring while adding, it is saturated FeCl3It after solution is added, is stored at room temperature overnight, obtains modified residual active sludge With mud mixed liquor III;
(4) Bordeaux mixture for being equivalent to III weight 10% of mixed liquor is added in mixed liquor III, is placed in high pressure after mixing evenly and goes out 60min is inactivated in bacterium kettle at 130 DEG C, then ultrasonic treatment 2h is carried out using low frequency high-strength ultrasonic, control ultrasonic power is 40KHz, ultrasound intensity 100DB, is then separated by solid-liquid separation, and is washed Solid content, then be centrifuged, is obtained inactivating modified residual activity Sludge and mud mixed liquor IV;
(5) it is added the pozzolan cement of 20 parts by weight in mixed liquor IV, the polyethylene glycol colloid of 5 parts by weight, 5 parts by weight The chopped basalt fibre of cyclic chelators, the flyash of 10 parts by weight and 10 parts by weight, passes through stirring in hybrid processor Machine is stirred mixing, until being uniformly mixing to obtain raw material soil paste;The cyclic chelators are crown ether analog derivative, described to be chopped Basalt fibre length is 10mm, density 3.5g/cm3
(6) the raw material soil paste being added to the silicon powder of the waste plastic foam of 5 parts by weight and 10 parts by weight in hybrid processor In, residual active sludge and mud mixed type foamed plastics particle light mixed soil are then obtained after mixing evenly.
Show by test: the residual active sludge and mud mixed type foamed plastics lightweight that the present embodiment is prepared are mixed Solidifying soil conserves under standard atmospheric pressure, 18 DEG C of the temperature standard conditions with humidity 100%, and the real density of 28d is 0.971g/cm3, Unconfined compressive strength is 402kPa, and the total amount of the cementitious material of lightweight concrete is suitable in product, makes lightweight concrete surface Closely knit solidification will not generate the crack caused by dry shrink while having water-proof function, receive in addition, fiber can play inhibition Contracting, the effect for increasing toughness, therefore the product prepared is not easy to crack, good product quality, use scope is extensive.
What has been described above is only a preferred embodiment of the present invention, it is noted that for those of ordinary skill in the art For, without departing from the concept of the premise of the invention, various modifications and improvements can be made, these belong to the present invention Protection scope.

Claims (10)

1. the preparation method of residual active sludge and mud mixed type foamed plastics lightweight concrete, which is characterized in that including following step It is rapid:
(1) residual active sludge of 20-40 parts by weight and the mud merging anaerobic sludge pond of 40-60 parts by weight are taken, distilled water is added After dilution, surfactant is added, is stood overnight after stirring 4-5 h, obtains mixed liquor I;
(2) white lime of 10-20 parts by weight and the thiosulfuric acid of 5-10 parts by weight are added in the mixed liquor I obtained to step (1) Sodium stirs at a temperature of 45-50 DEG C, and anaerobic fermentation 2-3 days to mixed liquor I in sposh state;Oxygen is passed through again to carry out at aeration Reason, and the cationic polyacrylamide that 3-8 parts by weight are added is dehydrated mud mixture, after separation of solid and liquid, washes Solid content 2-3 It is secondary, obtain deodorization residual active sludge and mud mixed liquor II;
(3) heated at constant temperature at a temperature of the mixed liquor II for obtaining step (2) is placed in 60-70 DEG C, is added dropwise mass fraction 4- 8% saturation FeCl3Solution, it is stirring while adding, it stands overnight at room temperature, obtains modified residual active sludge and mud mixed liquor Ⅲ;
(4) the alkaline fungicide of mass fraction 5-10% is added in the mixed liquor III that step (3) obtains, first sets after mixing evenly Enter in high pressure sterilization kettle and inactivate 45-60min at 120-130 DEG C, after carry out ultrasonic treatment 1-2h again, finally carry out solid-liquid point From washing Solid content obtains inactivating modified residual active sludge and mud mixed liquor IV;
(5) the curing agent cement of 10-20 parts by weight, the bonding of 2-5 parts by weight are added in the mixed liquor IV that step (4) obtains Agent, the chelating agent of 1-5 parts by weight, the flyash of 5-10 parts by weight and the fiber of 5-10 parts by weight, through blender at mixing Raw material soil paste is obtained after uniform stirring mixing in reason device;
(6) light material of 1-5 parts by weight and the silicon powder of 4-10 parts by weight are added in the raw material soil paste that step (5) obtains, stirs Residual active sludge and mud mixed type foamed plastics particle light mixed soil are obtained after mixing uniformly.
2. the preparation method of residual active sludge according to claim 1 and mud mixed type foamed plastics lightweight concrete, It is characterized in that, the additional amount of distilled water described in step (1) is the 40-50% of residual active sludge and mud total weight, the table The additional amount of face activating agent is the 4-6% of residual active sludge and mud total weight.
3. the preparation method of residual active sludge according to claim 2 and mud mixed type foamed plastics lightweight concrete, It is characterized in that, the surfactant includes dodecyl sodium sulfate, lauryl sodium sulfate, cetyl trimethylammonium bromide Or one of 4 bromide or a variety of.
4. the preparation method of residual active sludge according to claim 1 and mud mixed type foamed plastics lightweight concrete, It is characterized in that, dissolved oxygen content is 2.0-2.5mg/L in the mud mixture of sposh state in Air Exposure described in step (2).
5. the preparation method of residual active sludge according to claim 1 and mud mixed type foamed plastics lightweight concrete, It is characterized in that, alkalinity fungicide described in step (4) is lime sulfur or Bordeaux mixture.
6. the preparation method of residual active sludge according to claim 1 and mud mixed type foamed plastics lightweight concrete, It is characterized in that, in ultrasonic treatment described in step (4), the frequency of ultrasonic wave is 30-40 KHz, ultrasound intensity 80- 100DB。
7. the preparation method of residual active sludge according to claim 1 and mud mixed type foamed plastics lightweight concrete, It is characterized in that, in step (5), the curing agent cement includes portland cement, pozzolan cement, appointing in portland blast-furnace slag cement It is a kind of;Described adhesive includes starch-hydrocolloid or polyethylene glycol colloid;The chelating agent is cyclic chelators;The fiber is short Cut basalt fibre.
8. the preparation method of residual active sludge according to claim 7 and mud mixed type foamed plastics lightweight concrete, It is characterized in that, the cyclic chelators include porphyrin analog derivative or crown ether analog derivative;The chopped basalt fibre length For 5-10mm, density 3.0-3.5g/cm3
9. the preparation method of residual active sludge according to claim 1 and mud mixed type foamed plastics lightweight concrete, It is characterized in that, light material described in step (6) includes expanded polystyrene particle, waste plastic foam and waste tire particle Any one of.
10. the preparation method of residual active sludge according to claim 9 and mud mixed type foamed plastics lightweight concrete, It is characterized in that, the density of the expanded polystyrene particle is 0.02-0.04g/cm3, partial size 1-3mm.
CN201810966580.8A 2018-08-23 2018-08-23 Method for preparing residual activated sludge and sludge mixed type foamed plastic lightweight concrete Active CN109133778B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201810966580.8A CN109133778B (en) 2018-08-23 2018-08-23 Method for preparing residual activated sludge and sludge mixed type foamed plastic lightweight concrete

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201810966580.8A CN109133778B (en) 2018-08-23 2018-08-23 Method for preparing residual activated sludge and sludge mixed type foamed plastic lightweight concrete

Publications (2)

Publication Number Publication Date
CN109133778A true CN109133778A (en) 2019-01-04
CN109133778B CN109133778B (en) 2021-01-05

Family

ID=64791117

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201810966580.8A Active CN109133778B (en) 2018-08-23 2018-08-23 Method for preparing residual activated sludge and sludge mixed type foamed plastic lightweight concrete

Country Status (1)

Country Link
CN (1) CN109133778B (en)

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH06134500A (en) * 1992-10-21 1994-05-17 Nippon Steel Corp Treatment of sludge
CN103011538A (en) * 2012-12-07 2013-04-03 常州大学 Treatment method for anaerobic sludge in sewage
WO2013063774A1 (en) * 2011-11-02 2013-05-10 Empire Technology Development Llc Solidifying sludge
CN103496890A (en) * 2013-09-03 2014-01-08 北京四方如钢混凝土制品有限公司 Method for manufacturing solid block by using sludge, solid block, and backfilling method
CN106186106A (en) * 2016-08-24 2016-12-07 米桂琼 A kind of acid domestic sewage treating compound
CN108101329A (en) * 2016-11-25 2018-06-01 中国石油化工股份有限公司 A kind of excess sludge anaerobism desiccation treatment process

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH06134500A (en) * 1992-10-21 1994-05-17 Nippon Steel Corp Treatment of sludge
WO2013063774A1 (en) * 2011-11-02 2013-05-10 Empire Technology Development Llc Solidifying sludge
CN103011538A (en) * 2012-12-07 2013-04-03 常州大学 Treatment method for anaerobic sludge in sewage
CN103496890A (en) * 2013-09-03 2014-01-08 北京四方如钢混凝土制品有限公司 Method for manufacturing solid block by using sludge, solid block, and backfilling method
CN106186106A (en) * 2016-08-24 2016-12-07 米桂琼 A kind of acid domestic sewage treating compound
CN108101329A (en) * 2016-11-25 2018-06-01 中国石油化工股份有限公司 A kind of excess sludge anaerobism desiccation treatment process

Also Published As

Publication number Publication date
CN109133778B (en) 2021-01-05

Similar Documents

Publication Publication Date Title
CN102515827B (en) Method for preparing light foam concrete by using compound protein foaming agent
KR102141914B1 (en) Eco-friendly solidification agent composition for solidifying weak ground and method for solidifying weak ground using the same
CN108558295A (en) A kind of light-high-strength concrete
CN108516755A (en) A kind of inorganic polymer expanded material and preparation method thereof prepared using sludge
CN108752540A (en) The amphipathic multi-functional hybridized nanometer particle of one kind, preparation method and its application
CN108503285A (en) A kind of preparation method of light-high-strength concrete
CN108218264A (en) It is a kind of using lime-sodium carbonate as the one-component alkali-activated carbonatite cementitious material of exciting agent
CN110015824A (en) A kind of soft clay microorganism curing agent, the application in soft clay solidifies and application method
CN113277815A (en) Sludge curing agent for ecological planting and preparation method thereof
CN106045457A (en) High-strength waterproof foamed heat insulation board and preparation method thereof
CN105985092A (en) Energy-saving thermal-insulation material for wall
CN109133778A (en) The preparation method of residual active sludge and mud mixed type foamed plastics lightweight concrete
CN101891367A (en) Solidification and stabilization method of urban sludge
CN1686875B (en) Method for treating sludge in pipe trench
CN115974503B (en) Underwater anti-dispersion fluid sludge curing agent and preparation method and application thereof
CN105565852A (en) Green pollution-free wall thermal-insulation material
CN105565754A (en) Crack-resistant wall thermal-insulation material
CN105985093A (en) Antibacterial environment-friendly heat-insulation wall material
CN105541393A (en) Environmentally-friendly wall insulation material
CN105541377A (en) Composite wall insulation material
CN113121194B (en) System and method for preparing building 3D printing material by using urban waste and industrial solid waste
CN108516742A (en) A kind of preparation method of Light-weight composite concrete plank
CN105565753A (en) High-strength flame-retardant wall insulating material
CN102951889A (en) Resin-modified desulfurized gypsum-mining (steel) slag-straw-based wall material and preparation method thereof
CN105565755A (en) Low-cost wall thermal-insulation material

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
TA01 Transfer of patent application right

Effective date of registration: 20200812

Address after: No. 629 Jiangning Science Park longmian Road District of Nanjing City, Jiangsu province 210000

Applicant after: NANJING COMMUNICATIONS INSTITUTE OF TECHNOLOGY

Address before: No. 1 Jiangning Road, Nanjing District hirokage 211167 cities in Jiangsu Province

Applicant before: NANJING INSTITUTE OF TECHNOLOGY

TA01 Transfer of patent application right
TA01 Transfer of patent application right

Effective date of registration: 20200927

Address after: 210000 1 Hong Kong Avenue, Science Park, Jiangning District, Nanjing, Jiangsu.

Applicant after: NANJING INSTITUTE OF TECHNOLOGY

Address before: No. 629 Jiangning Science Park longmian Road District of Nanjing City, Jiangsu province 210000

Applicant before: NANJING COMMUNICATIONS INSTITUTE OF TECHNOLOGY

TA01 Transfer of patent application right
GR01 Patent grant
GR01 Patent grant