CN106345411A - Rare metal-based sludge activated carbon and application thereof in removal of sulfur, ammonia and phosphorus - Google Patents

Rare metal-based sludge activated carbon and application thereof in removal of sulfur, ammonia and phosphorus Download PDF

Info

Publication number
CN106345411A
CN106345411A CN201610871905.5A CN201610871905A CN106345411A CN 106345411 A CN106345411 A CN 106345411A CN 201610871905 A CN201610871905 A CN 201610871905A CN 106345411 A CN106345411 A CN 106345411A
Authority
CN
China
Prior art keywords
sludge
rare metal
powder
carbon
active sludge
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
CN201610871905.5A
Other languages
Chinese (zh)
Other versions
CN106345411B (en
Inventor
李风浪
李舒歆
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.)
Xu Haiyan
Original Assignee
Dongguan Lianzhou Intellectual Property Operation and Management 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 Dongguan Lianzhou Intellectual Property Operation and Management Co Ltd filed Critical Dongguan Lianzhou Intellectual Property Operation and Management Co Ltd
Priority to CN201610871905.5A priority Critical patent/CN106345411B/en
Publication of CN106345411A publication Critical patent/CN106345411A/en
Application granted granted Critical
Publication of CN106345411B publication Critical patent/CN106345411B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/20Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising free carbon; comprising carbon obtained by carbonising processes
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/02Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by adsorption, e.g. preparative gas chromatography
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/06Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising oxides or hydroxides of metals not provided for in group B01J20/04
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/281Treatment of water, waste water, or sewage by sorption using inorganic sorbents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/283Treatment of water, waste water, or sewage by sorption using coal, charred products, or inorganic mixtures containing them
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/288Treatment of water, waste water, or sewage by sorption using composite sorbents, e.g. coated, impregnated, multi-layered
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2257/00Components to be removed
    • B01D2257/30Sulfur compounds
    • B01D2257/304Hydrogen sulfide
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2257/00Components to be removed
    • B01D2257/40Nitrogen compounds
    • B01D2257/406Ammonia
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2257/00Components to be removed
    • B01D2257/55Compounds of silicon, phosphorus, germanium or arsenic
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J2220/00Aspects relating to sorbent materials
    • B01J2220/40Aspects relating to the composition of sorbent or filter aid materials
    • B01J2220/48Sorbents characterised by the starting material used for their preparation
    • B01J2220/4875Sorbents characterised by the starting material used for their preparation the starting material being a waste, residue or of undefined composition
    • B01J2220/4887Residues, wastes, e.g. garbage, municipal or industrial sludges, compost, animal manure; fly-ashes
    • 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
    • C02F2101/101Sulfur compounds
    • 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
    • C02F2101/105Phosphorus compounds
    • 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
    • C02F2101/16Nitrogen compounds, e.g. ammonia

Abstract

The invention provides a rare metal-based sludge activated carbon and application thereof in the removal of sulfur, ammonia and phosphorus. The rare metal-based sludge activated carbon includes sludge activated carbon and metal elements such as manganese, cerium, praseodymium, neodymium, promethium, samarium, europium, gadolinium, terbium, dysprosium, holmium, erbium and the like, and is specifically prepared by a method comprising the following steps: mixing pyrolusite powder with activated sludge, adding a zinc chloride compounded activating agent into the mixture, activating the mixture at a high temperature, carbonizing the mixture to obtain pyrolusite compounded activated sludge, mixing the activated sludge with rare earth oxide powder and a chelating agent after the activated sludge is modified by potassium hydroxide solution, heating the mixture in a microwave oven, carbonizing the mixture to obtain rare earth compounded activated sludge, and mixing the compounded activated sludge to obtain a product. The rare metal-based sludge activated carbon prepared by the method has the advantages of high activity, high porosity, uniform pore size distribution, high adsorption capacity, capability of chelating a plurality of metals and microorganisms, high capacity of adsorbing sulfur, ammonia and phosphorus and high rate of removing the sulfur, the ammonia and the phosphorus in sewage and waste.

Description

A kind of active sludge carbon based on rare metal and the application in terms of sulphur removal ammonia phosphorus
Technical field
The invention belongs to active sludge carbon field of material technology is and in particular to a kind of active sludge carbon based on rare metal And the application in terms of sulphur removal ammonia phosphorus.
Background technology
The surging, along with substantial amounts of water pollution, and at sewage of fast development with national economy and water consumption Reason and control water pollution also can produce substantial amounts of mud and odor pollution.The stench of mud mainly based on hydrogen sulfide and ammonia, Stench not only produces harm, and also has unsafe impact to society to health, animal and plant growth.At present, both at home and abroad The main method processing foul smell has absorption method, absorption process, combustion method and the biological clarification, wherein absorption method and biological clarification to be Main methods, are because that biological clarification is with low cost, absorption method using method, and removal effect is stable.
The main material of absorption method is activated carbon, and activated carbon is easy to get due to raw material, and manufacturing process is simple and efficient, adsorption effect Stablize and obtain the pro-gaze of people.Active sludge carbon be using activated sludge as raw material prepare, in activated sludge contain antibacterial, The xenogeneic subject group such as funguses, protozoacide and Organic substance, because the physical absorption performance of active sludge carbon not only active charcoal, Also contain a large amount of microorganisms, physics, biological and chemical process are carried out to the source of stench, comprehensive control is carried out to stench.China The disclosed method preparing active sludge carbon using mud of patent cn 101423212b, will add flocculant and a huge sum of money in mud Belong to chelating agen, after stirring thickening dry, be subsequently placed in half carbonization gasified boiler and carry out half dry distilling process, take out stone and After irony, add Colophonium or tar as adhesive, black liquor, smokeless coal powder, potassium chloride, potassium hydroxide or hydrogen-oxygen Change sodium as adjusting hole agent, mix homogeneously, pelletize, dry in the sun, be placed in activation processing in activation furnace, sieve powder processed and obtain sludge activity Charcoal.In the active sludge carbon of the method preparation, macropore, mesopore and transitional pore enrich, and adsorption equilibrium ability projects, and adsorption rate is fast, But it is not targeted to the process of waste water, waste gas.The system of active sludge carbon disclosed in Chinese patent cn 103495399b Preparation Method and application, drying sludge is divided water to sieve, and is pyrolyzed, adds in hydrogen peroxide solution in ammonia atmosphere, vibration oxidation Obtain sludge activity char combustion powdered carbon, then heat treated under ammonia atmosphere, obtain active sludge carbon ammonification powdered carbon, last submergence In methylating reagent, washing is dried to obtain active sludge carbon.The active sludge carbon of the method preparation is to low concentration perchlorate There is good removal effect, and do not result in secondary pollution.A kind of load manganese mud disclosed in Chinese patent cn 105833835a Active carbon material and preparation method thereof, pulverizes after mud is dried and forms Granular sludge charcoal base, immerses acid solution and hydrochlorate Activate in the composite activating agent of solution, take out and dry, then be placed in charing process in high temperature furnace, with acid solution rinsing, eluting, baking Dry, finally it is placed in manganese metal loading solution, ultrasonic, dry, heating frozen obtains carrying the active sludge carbon of manganese.Prepared by the method Load manganese active sludge carbon aperture flourishing, even particle distribution, activity function is good.
From above-mentioned prior art, by being modified to active sludge carbon arranging, the suction of mud not only can be improved Attached performance, but also can be with the absorption property of object.But inhale for active sludge carbon currently for elements such as sulfur ammonia phosphorus The research of attached dose of aspect is actually rare.
Content of the invention
The technical problem to be solved in the present invention is to provide a kind of active sludge carbon based on rare metal and in sulphur removal ammonia phosphorus The application of aspect, should based in the active sludge carbon of rare metal contain active sludge carbon and manganese cerium praseodymium neodymium promethium sm-eu-gd terbium dysprosium holmium The metallic elements such as erbium, method particularly includes: pyrolusite powder is mixed with activated sludge, adds zinc chloride composite activating agent, high temperature Activation, carbonization obtains soft manganese complex enzyme/activated sludge, activated sludge is modified through potassium hydroxide solution, with RE oxide powder With chelating agen mixing, microwave-oven-heating, carbonization obtains rare earth complex enzyme/activated sludge, and this complex enzyme/activated sludge is mixed to get product Product.The sludge activity carbon activity based on rare metal of present invention preparation is big, and hole is high, even aperture distribution, high adsorption capacity, Chelating various metals and microorganism, all have good absorbability to sulfur ammonia phosphorus, to sewage and discarded in sulfur ammonia phosphorus ligands Rate is high.
For solving above-mentioned technical problem, the technical scheme is that
A kind of active sludge carbon based on rare metal, described based in the active sludge carbon of rare metal contain mud live Property charcoal and rare metal, described rare metal provides by pyrolusite powder and RE oxide powder, and described rare metal includes Manganese element, lanthanum element, Ce elements, praseodymium element, neodymium element, promethium element, samarium element, europium element, gadolinium element, terbium element, dysprosium element, Holmium element, er element, thulium element, ytterbium element and lutecium element, described rare metal is 0.1 with the mass ratio of active sludge carbon: 99.9-5:95.
Preferred as technique scheme, in described pyrolusite powder, the content of manganese element is not less than 50%, described dilute The particle diameter of native oxide powder is 150-300 mesh.
The main component of currently preferred pyrolusite powder is manganese dioxide, and manganese dioxide itself has good surface Adsorption effect, redox and catalytic effect etc. act on, and aboundresources, cheap, environmental friendliness.
, in 150-300 mesh, air hole structure is good, high mechanical strength for the particle diameter of currently preferred RE oxide powder, raw Produce simple, easy industrialized production.
Preferred as technique scheme, the preparation method of the described active sludge carbon based on rare metal includes following Step:
(1) mud is dried after 24h, grind to form sewage sludge powder, pyrolusite powder is mixed homogeneously with sewage sludge powder, add Zinc chloride and the composite activating agent of dilute sulfuric acid, the uniform 1-6h of ultrasonic mixing, stand 24h, dry activation 24- at 80-130 DEG C 72h, is placed in 550-650 DEG C of tube furnace, and high temperature carbonization reacts 1-5h, is washed to neutrality and obtains soft manganese composite sludge work after cooling Property charcoal;
(2) sewage sludge powder prepared by step (1) is pyrolyzed under ammonia atmosphere, forms sludge activity powdered carbon, mud is lived Property powdered carbon impregnated in potassium hydroxide solution, sealing stirring, wash drying, add RE oxide powder and citric acid, then Microwave heating 2-3min under 400-500w, is placed in tube furnace, and by nitrogen and vapor, high-temperature activation reacts, water after cooling It is washed till neutrality and obtain rare earth composite sludge activated carbon;
(3) the rare earth composite sludge activated carbon that soft manganese composite sludge activated carbon prepared by step (1) is prepared with step (2) Mixing, grinds screening, obtains the active sludge carbon based on rare metal.
Preferred as technique scheme, the mud of preparation method step (1) is remaining dilute mud or dehydrated sludge cake, Moisture content is 85-90%, and the ash content of coal is 35-50%.
Preferred as technique scheme, the particle diameter of the sewage sludge powder of preparation method step (1) or (2) is 200- 300 mesh.
Preferred as technique scheme, the pyrolusite powder of preparation method step (1) and the mass ratio of sewage sludge powder For 0.1:45-5:45.
Preferred as technique scheme, in the zinc chloride of preparation method step (1) and the composite activating agent of dilute sulfuric acid The volume of zinc chloride and dilute sulfuric acid is 3:1-6:1, and chlorination zinc concentration is 4-6mol/l, and the mass fraction of dilute sulfuric acid is 20- 45%.
Preferred as technique scheme, the RE oxide powder of preparation method step (2) and the matter of sewage sludge powder Amount ratio is 0.1:45-5:45.
Preferred as technique scheme, the soft manganese composite sludge activated carbon of preparation method step (3) is combined with rare earth The mass ratio of active sludge carbon is 1:0.7-1.3.
Additionally, the present invention also provides a kind of active sludge carbon based on rare metal in the application of sewage sulphur removal nitrogen phosphorus, wrap Include following steps: after mud is diluted, add the active sludge carbon based on rare metal, quick stirring, absorption staticly settles;Will It is placed in exhaust environment based on the active sludge carbon of rare metal, air-supply, standing adsorption.
Compared with prior art, the method have the advantages that
(1) manganese element, lanthanum element, Ce elements, praseodymium are contained in the active sludge carbon based on rare metal of present invention preparation Element, neodymium element, promethium element, samarium element, europium element, gadolinium element, terbium element, dysprosium element, holmium element, er element, thulium element, ytterbium Element and lutecium element, these yttriums have stronger catalysed oxidn, and yttrium adds lives to mud Property charcoal in, be remarkably improved the adsorption effect to sulfur nitrogen phosphorus, be better achieved sewage separate, but the amount mistake of yttrium Do not reach facilitation effect less, excessively can affect the absorption of sulfur nitrogen phosphorus on the contrary.
(2) active sludge carbon in the active sludge carbon based on rare metal of present invention preparation is molten through potassium hydroxide basic After liquid is processed, the activity of active sludge carbon becomes apparent from, adsorption effect more preferably, to the clearance of sulfur nitrogen phosphorus up to more than 90%, Can effectively purify water, prevent water pollution.
(3) porosity of the active sludge carbon based on rare metal of present invention preparation is high, and pore structure is flourishing and sews and mend Uniformly, obvious projection is contained on the surface of active sludge carbon, and specific surface area is high, and adsorption activity point position is many, and active sludge carbon Microorganism is contained on surface and rare metal can promote the absorption of sulfur nitrogen phosphorus, solves existing sludge activity poor to the absorption of sulfur nitrogen phosphorus Problem.
(4) preparation method of the present invention is simple, and controllability is strong, preparing raw material wide material sources, cheap, the economy of product Profitable, there is the very strong market competitiveness and promotional value, and good stability in water body for this absorption, do not result in water The secondary pollution of body, has good application prospect.
Specific embodiment
To describe the present invention, the illustrative examples of the here present invention and explanation below in conjunction with specific embodiment in detail It is used for explaining the present invention, but not as a limitation of the invention.
Embodiment 1:
(1) by moisture content be 85%, the ash content of coal be 35% the dilute mud of residue dry 24h after, grind to form 200-300 mesh Sewage sludge powder, mass ratio is 0.1:45, particle diameter is that the pyrolusite powder of 150 mesh is mixed homogeneously with sewage sludge powder, add chlorine Change the composite activating agent of zinc and dilute sulfuric acid, the wherein volume of zinc chloride and dilute sulfuric acid is 3:1, and chlorination zinc concentration is 4mol/l, The mass fraction of dilute sulfuric acid is 20%, the uniform 1h of ultrasonic mixing, stands 24h, dries activation 24h, be placed in 550 DEG C of pipes at 80 DEG C In formula stove, high temperature carbonization reacts 1h, is washed to neutrality and obtains soft manganese composite sludge activated carbon after cooling.
(2) sewage sludge powder of 200 mesh is pyrolyzed under ammonia atmosphere, forms sludge activity powdered carbon, by weight, by matter Amount impregnated in 20% potassium hydroxide solution than the sludge activity powdered carbon for 45 parts, sealing stirring 60min, washs drying, plus Enter the citric acid of the RE oxide powder that 0.1 part of particle diameter is 150 mesh and 2 parts, microwave heating 2min, is placed in pipe under 400w In formula stove, by the nitrogen for 1:1 for the volume ratio and vapor, high-temperature activation reaction 1h at 900 DEG C, it is washed to neutral after cooling To rare earth composite sludge activated carbon.
(3) by mass ratio, the soft manganese composite sludge activated carbon for 1:0.7 is mixed with rare earth composite sludge activated carbon, grinds sieve Point, obtain the active sludge carbon based on rare metal.
Embodiment 2:
(1) by moisture content be 90%, the ash content of coal be 50% dehydrated sludge cake dry 24h after, grind to form the mud of 300 mesh Powder, mass ratio is 5:45, and particle diameter is that the pyrolusite powder of 300 mesh is mixed homogeneously with sewage sludge powder, adds zinc chloride and dilute The volume of the composite activating agent of sulphuric acid, wherein zinc chloride and dilute sulfuric acid is 6:1, and chlorination zinc concentration is 6mol/l, dilute sulfuric acid Mass fraction is 45%, the uniform 6h of ultrasonic mixing, stands 24h, dries activation 72h, be placed in 650 DEG C of tube furnaces at 130 DEG C, High temperature carbonization reacts 5h, is washed to neutrality and obtains soft manganese composite sludge activated carbon after cooling.
(2) sewage sludge powder of 300 mesh is pyrolyzed under ammonia atmosphere, forms sludge activity powdered carbon, by weight, by matter Amount impregnated in 20% potassium hydroxide solution than the sludge activity powdered carbon for 45 parts, sealing stirring 60min, washs drying, plus Enter the citric acid of the RE oxide powder that 5 parts of particle diameter is 300 mesh and 10 parts, microwave heating 3min, is placed in pipe under 500w In formula stove, by the nitrogen for 1:1 for the volume ratio and vapor, high-temperature activation reaction 5h at 900 DEG C, it is washed to neutral after cooling To rare earth composite sludge activated carbon.
(3) by mass ratio, the soft manganese composite sludge activated carbon for 1:1.3 is mixed with rare earth composite sludge activated carbon, grinds sieve Point, obtain the active sludge carbon based on rare metal.
Embodiment 3:
(1) by moisture content be 88%, the ash content of coal be 45% the dilute mud of residue dry 24h after, grind to form the dirt of 250 mesh Mud powder, mass ratio is 1:45, and particle diameter is that the pyrolusite powder of 200 mesh is mixed homogeneously with sewage sludge powder, add zinc chloride and The volume of the composite activating agent of dilute sulfuric acid, wherein zinc chloride and dilute sulfuric acid is 4:1, and chlorination zinc concentration is 5mol/l, dilute sulfuric acid Mass fraction be 25%, the uniform 3h of ultrasonic mixing, stand 24h, at 100 DEG C dry activation 36h, be placed in 600 DEG C of tube furnaces Interior, high temperature carbonization reacts 2h, is washed to neutrality and obtains soft manganese composite sludge activated carbon after cooling.
(2) sewage sludge powder of 250 mesh is pyrolyzed under ammonia atmosphere, forms sludge activity powdered carbon, by weight, by matter Amount impregnated in 20% potassium hydroxide solution than the sludge activity powdered carbon for 45 parts, sealing stirring 60min, washs drying, plus Enter the citric acid of the RE oxide powder that 2 parts of particle diameter is 250 mesh and 8 parts, microwave heating 2.5min, is placed in pipe under 450w In formula stove, by the nitrogen for 1:1 for the volume ratio and vapor, high-temperature activation reaction 3h at 900 DEG C, it is washed to neutral after cooling To rare earth composite sludge activated carbon.
(3) by mass ratio, the soft manganese composite sludge activated carbon for 1:1 is mixed with rare earth composite sludge activated carbon, grinds sieve Point, obtain the active sludge carbon based on rare metal.
Embodiment 4:
(1) by moisture content be 89%, the ash content of coal be 42% dehydrated sludge cake dry 24h after, grind to form the mud of 300 mesh Powder, mass ratio is 2.5:45, and particle diameter is that the pyrolusite powder of 150-300 mesh is mixed homogeneously with sewage sludge powder, adds chlorination Zinc and the composite activating agent of dilute sulfuric acid, the wherein volume of zinc chloride and dilute sulfuric acid are 5:1, and chlorination zinc concentration is 5mol/l, dilute The mass fraction of sulphuric acid is 35%, the uniform 3h of ultrasonic mixing, stands 24h, dries activation 50h, be placed in 650 DEG C of pipes at 110 DEG C In formula stove, high temperature carbonization reacts 2h, is washed to neutrality and obtains soft manganese composite sludge activated carbon after cooling.
(2) sewage sludge powder of 200 mesh is pyrolyzed under ammonia atmosphere, forms sludge activity powdered carbon, by weight, by matter Amount impregnated in 20% potassium hydroxide solution than the sludge activity powdered carbon for 45 parts, sealing stirring 60min, washs drying, plus Enter the citric acid of the RE oxide powder that 3 parts of particle diameter is 300 mesh and 8 parts, microwave heating 2min, is placed in tubular type under 450w In stove, by the nitrogen for 1:1 for the volume ratio and vapor, at 900 DEG C, high-temperature activation reaction 3h, is washed to neutrality and obtains after cooling Rare earth composite sludge activated carbon.
(3) by mass ratio, the soft manganese composite sludge activated carbon for 1:1.1 is mixed with rare earth composite sludge activated carbon, grinds sieve Point, obtain the active sludge carbon based on rare metal.
Embodiment 5:
(1) by moisture content be 90%, the ash content of coal be 45% the dilute mud of residue dry 24h after, grind to form the dirt of 200 mesh Mud powder, mass ratio is 1.5:45, and particle diameter is that the pyrolusite powder of 250 mesh is mixed homogeneously with sewage sludge powder, adds zinc chloride Volume with the composite activating agent of dilute sulfuric acid, wherein zinc chloride and dilute sulfuric acid is 5:1, and chlorination zinc concentration is 1.5mol/l, dilute The mass fraction of sulphuric acid is 35%, the uniform 4h of ultrasonic mixing, stands 24h, dries activation 72h, be placed in 550 DEG C of tubular types at 90 DEG C In stove, high temperature carbonization reacts 4h, is washed to neutrality and obtains soft manganese composite sludge activated carbon after cooling.
(2) sewage sludge powder of 200 mesh is pyrolyzed under ammonia atmosphere, forms sludge activity powdered carbon, by weight, by matter Amount impregnated in 20% potassium hydroxide solution than the sludge activity powdered carbon for 45 parts, sealing stirring 60min, washs drying, plus Enter the citric acid of the RE oxide powder that 3 parts of particle diameter is 200 mesh and 6 parts, microwave heating 2min, is placed in tubular type under 500w In stove, by the nitrogen for 1:1 for the volume ratio and vapor, high-temperature activation reaction 3.5h at 900 DEG C, it is washed to neutral after cooling To rare earth composite sludge activated carbon.
(3) by mass ratio, the soft manganese composite sludge activated carbon for 1:1.2 is mixed with rare earth composite sludge activated carbon, grinds sieve Point, obtain the active sludge carbon based on rare metal.
Embodiment 6:
(1) by moisture content be 90%, the ash content of coal be 40% dehydrated sludge cake dry 24h after, grind to form the mud of 300 mesh Powder, mass ratio is 0.1:45, and particle diameter is that the pyrolusite powder of 300 mesh is mixed homogeneously with sewage sludge powder, add zinc chloride and The volume of the composite activating agent of dilute sulfuric acid, wherein zinc chloride and dilute sulfuric acid is 3:1, and chlorination zinc concentration is 6mol/l, dilute sulfuric acid Mass fraction be 20%, the uniform 6h of ultrasonic mixing, stand 24h, at 80 DEG C dry activation 72h, be placed in 650 DEG C of tube furnaces Interior, high temperature carbonization reacts 1h, is washed to neutrality and obtains soft manganese composite sludge activated carbon after cooling.
(2) sewage sludge powder of 300 mesh is pyrolyzed under ammonia atmosphere, forms sludge activity powdered carbon, by weight, by matter Amount impregnated in 20% potassium hydroxide solution than the sludge activity powdered carbon for 45 parts, sealing stirring 60min, washs drying, plus Enter the citric acid of the RE oxide powder that 5 parts of particle diameter is 150 mesh and 10 parts, microwave heating 3min, is placed in pipe under 400w In formula stove, by the nitrogen for 1:1 for the volume ratio and vapor, high-temperature activation reaction 1h at 900 DEG C, it is washed to neutral after cooling To rare earth composite sludge activated carbon.
(3) by mass ratio, the soft manganese composite sludge activated carbon for 1:1.3 is mixed with rare earth composite sludge activated carbon, grinds sieve Point, obtain the active sludge carbon based on rare metal.
The preparation of embodiment 1-6 is used for sewage and the absorption of discarded sulfur nitrogen phosphorus based on the active sludge carbon of rare metal In, method particularly includes:
After mud is diluted, add the active sludge carbon based on rare metal, quick stirring, absorption staticly settles.
To be placed in exhaust environment based on the active sludge carbon of rare metal, air-supply, standing adsorption.
After testing, embodiment 1-6 preparation the active sludge carbon based on rare metal and prior art unmodified The clearance result to sewage and discarded sulfur nitrogen phosphorus of activated carbon is as follows:
In sewage:
In waste gas:
As seen from the above table, the active sludge carbon based on rare metal of present invention preparation and unmodified active sludge carbon phase Ratio significantly improves to the adsorption effect of sulfur nitrogen phosphorus, clearance is up to 90%.
Above-described embodiment only principle of the illustrative present invention and its effect, not for the restriction present invention.Any ripe The personage knowing this technology all can carry out modifications and changes without prejudice under the spirit and the scope of the present invention to above-described embodiment.Cause This, those of ordinary skill in the art is complete with institute under technological thought without departing from disclosed spirit such as All equivalent modifications becoming or change, must be covered by the claim of the present invention.

Claims (10)

1. a kind of active sludge carbon based on rare metal it is characterised in that: described based in the active sludge carbon of rare metal Containing active sludge carbon and rare metal, described rare metal is provided by pyrolusite powder and RE oxide powder, described dilute Metal is had to include manganese element, lanthanum element, Ce elements, praseodymium element, neodymium element, promethium element, samarium element, europium element, gadolinium element, terbium unit The quality of element, dysprosium element, holmium element, er element, thulium element, ytterbium element and lutecium element, described rare metal and active sludge carbon Than for 0.1:99.9-5:95.
2. a kind of active sludge carbon based on rare metal according to claim 1 is it is characterised in that described pyrolusite powder In end, the content of manganese element is not less than 50%, and the particle diameter of described RE oxide powder is 150-300 mesh.
3. a kind of active sludge carbon based on rare metal according to claims 1 or 2 is it is characterised in that described base Preparation method in the active sludge carbon of rare metal comprises the following steps:
(1) mud is dried after 24h, grind to form sewage sludge powder, pyrolusite powder is mixed homogeneously with sewage sludge powder, add chlorination Zinc and the composite activating agent of dilute sulfuric acid, the uniform 1-6h of ultrasonic mixing, stand 24h, dry activation 24-72h at 80-130 DEG C, put In 550-650 DEG C of tube furnace, high temperature carbonization reacts 1-5h, is washed to neutrality and obtains soft manganese composite sludge activated carbon after cooling;
(2) sewage sludge powder prepared by step (1) is pyrolyzed under ammonia atmosphere, forms sludge activity powdered carbon, by active sludge carbon Powder impregnated in potassium hydroxide solution, sealing stirring, washs drying, adds RE oxide powder and citric acid, then 400- Microwave heating 2-3min under 500w, is placed in tube furnace, and by nitrogen and vapor, high-temperature activation reacts, is washed to after cooling Neutrality obtains rare earth composite sludge activated carbon;
(3) the rare earth composite sludge activated carbon being prepared soft manganese composite sludge activated carbon prepared by step (1) with step (2) is mixed Close, grind screening, obtain the active sludge carbon based on rare metal.
4. a kind of active sludge carbon based on rare metal according to claim 3 is it is characterised in that preparation method step (1) mud is remaining dilute mud or dehydrated sludge cake, and moisture content is 85-90%, and the ash content of coal is 35-50%.
5. a kind of active sludge carbon based on rare metal according to claim 3 is it is characterised in that preparation method step (1) or (2) sewage sludge powder particle diameter be 200-300 mesh.
6. a kind of active sludge carbon based on rare metal according to claim 3 is it is characterised in that preparation method step (1) pyrolusite powder is 0.1:45-5:45 with the mass ratio of sewage sludge powder.
7. a kind of active sludge carbon based on rare metal according to claim 3 is it is characterised in that preparation method step (1) in zinc chloride and the composite activating agent of dilute sulfuric acid, the volume of zinc chloride and dilute sulfuric acid is 3:1-6:1, and chlorination zinc concentration is 4-6mol/l, the mass fraction of dilute sulfuric acid is 20-45%.
8. a kind of active sludge carbon based on rare metal according to claim 3 is it is characterised in that preparation method step (2) RE oxide powder is 0.1:45-5:45 with the mass ratio of sewage sludge powder.
9. a kind of active sludge carbon based on rare metal according to claim 3 is it is characterised in that preparation method step (3) soft manganese composite sludge activated carbon is 1:0.7-1.3 with the mass ratio of rare earth composite sludge activated carbon.
10. a kind of active sludge carbon based on rare metal sewage sulphur removal nitrogen phosphorus application it is characterised in that: include following step Rapid: after mud is diluted, add the active sludge carbon based on rare metal, quick stirring, absorption staticly settles;Will be based on rare The active sludge carbon of metal is placed in exhaust environment, air-supply, standing adsorption.
CN201610871905.5A 2016-09-30 2016-09-30 A kind of active sludge carbon based on rare metal and the application in terms of sulphur removal ammonia phosphorus Active CN106345411B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201610871905.5A CN106345411B (en) 2016-09-30 2016-09-30 A kind of active sludge carbon based on rare metal and the application in terms of sulphur removal ammonia phosphorus

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201610871905.5A CN106345411B (en) 2016-09-30 2016-09-30 A kind of active sludge carbon based on rare metal and the application in terms of sulphur removal ammonia phosphorus

Publications (2)

Publication Number Publication Date
CN106345411A true CN106345411A (en) 2017-01-25
CN106345411B CN106345411B (en) 2019-09-27

Family

ID=57866897

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201610871905.5A Active CN106345411B (en) 2016-09-30 2016-09-30 A kind of active sludge carbon based on rare metal and the application in terms of sulphur removal ammonia phosphorus

Country Status (1)

Country Link
CN (1) CN106345411B (en)

Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107445362A (en) * 2017-09-12 2017-12-08 潍坊学院 A kind of integrated apparatus and method of ozone composite catalytic oxidation processing chemical engineering sewage
CN108355607A (en) * 2018-02-09 2018-08-03 长江水利委员会长江科学院 It is a kind of to utilize the functional material for selecting copper tailings to prepare and its preparation process
CN108889116A (en) * 2018-07-24 2018-11-27 宁波高新区诠宝绶新材料科技有限公司 A kind of Portable deodorization carrier of oxygen clarifier using new catalytic material
CN110922276A (en) * 2019-11-15 2020-03-27 江苏省农业科学院 Preparation of modified sludge hydrothermal carbon material and application of modified sludge hydrothermal carbon material in non-point source pollution emission reduction
CN111450799A (en) * 2020-03-24 2020-07-28 天津科技大学 Preparation method of magnetic activated carbon based on black liquor lignin and Fenton sludge
CN113145096A (en) * 2021-04-30 2021-07-23 四川大学 Preparation method of composite photocatalyst for sewage treatment and product thereof
CN113145074A (en) * 2021-04-23 2021-07-23 桂林理工大学 Preparation method and application of biochar prepared from lanthanum-modified excess sludge
CN113145073A (en) * 2021-04-23 2021-07-23 桂林理工大学 Preparation method and application of secondary lanthanum carbide modified sludge biochar
CN113457624A (en) * 2021-06-18 2021-10-01 广西大学 Modified mushroom dreg biochar and preparation method thereof

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104624153A (en) * 2014-12-09 2015-05-20 邹仕放 Method for preparingadsorbing material by utilizing sludge
CN104772143A (en) * 2015-03-18 2015-07-15 昆明理工大学 Preparation method of supported sludge-base catalyst for removing low-concentration carbon disulfide
CN105833835A (en) * 2016-05-23 2016-08-10 上海理工大学 Manganese-loaded sludge activated carbon material and preparation method thereof

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104624153A (en) * 2014-12-09 2015-05-20 邹仕放 Method for preparingadsorbing material by utilizing sludge
CN104772143A (en) * 2015-03-18 2015-07-15 昆明理工大学 Preparation method of supported sludge-base catalyst for removing low-concentration carbon disulfide
CN105833835A (en) * 2016-05-23 2016-08-10 上海理工大学 Manganese-loaded sludge activated carbon material and preparation method thereof

Non-Patent Citations (3)

* Cited by examiner, † Cited by third party
Title
YING YING SUN ET AL.: "Research Progress on Producing Sludge Activated Carbon Doped with Ce", 《ADVANCED MATERIALS RESEARCH》 *
何莹等: "污泥活性炭的制备及其在污水处理中的应用研究现状", 《材料导报A:综述篇》 *
汪莉等: "软锰矿改性污泥活性炭对Cu2+吸附特性的研究", 《环境科学与技术》 *

Cited By (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107445362A (en) * 2017-09-12 2017-12-08 潍坊学院 A kind of integrated apparatus and method of ozone composite catalytic oxidation processing chemical engineering sewage
CN108355607A (en) * 2018-02-09 2018-08-03 长江水利委员会长江科学院 It is a kind of to utilize the functional material for selecting copper tailings to prepare and its preparation process
CN108355607B (en) * 2018-02-09 2020-10-27 长江水利委员会长江科学院 Functional material prepared by using copper-selecting tailings and preparation process thereof
CN108889116A (en) * 2018-07-24 2018-11-27 宁波高新区诠宝绶新材料科技有限公司 A kind of Portable deodorization carrier of oxygen clarifier using new catalytic material
CN110922276A (en) * 2019-11-15 2020-03-27 江苏省农业科学院 Preparation of modified sludge hydrothermal carbon material and application of modified sludge hydrothermal carbon material in non-point source pollution emission reduction
CN110922276B (en) * 2019-11-15 2021-08-24 江苏省农业科学院 Preparation of modified sludge hydrothermal carbon material and application of modified sludge hydrothermal carbon material in non-point source pollution emission reduction
CN111450799A (en) * 2020-03-24 2020-07-28 天津科技大学 Preparation method of magnetic activated carbon based on black liquor lignin and Fenton sludge
CN113145074A (en) * 2021-04-23 2021-07-23 桂林理工大学 Preparation method and application of biochar prepared from lanthanum-modified excess sludge
CN113145073A (en) * 2021-04-23 2021-07-23 桂林理工大学 Preparation method and application of secondary lanthanum carbide modified sludge biochar
CN113145096A (en) * 2021-04-30 2021-07-23 四川大学 Preparation method of composite photocatalyst for sewage treatment and product thereof
CN113457624A (en) * 2021-06-18 2021-10-01 广西大学 Modified mushroom dreg biochar and preparation method thereof

Also Published As

Publication number Publication date
CN106345411B (en) 2019-09-27

Similar Documents

Publication Publication Date Title
CN106345411B (en) A kind of active sludge carbon based on rare metal and the application in terms of sulphur removal ammonia phosphorus
CN106076335B (en) A kind of preparation method and application of heterogeneous Fenton catalyst
CN110240386A (en) A kind of stalk cooperates with the devices and methods therefor of processing with sludge
CN104084126B (en) The preparation method of biomass-based iron aluminium complex spherical charcoal
CN105056882A (en) Preparation method of modified charcoal-based adsorbent for removing hydrogen sulfide
CN102728339B (en) Porous inorganic ceramic membrane-graphene-TiO2 photocatalyst composite material and its preparation method
CN103495434B (en) Desulphurization and denitration agent based on waste biomass and preparation method thereof
CN100515940C (en) Method for preparing active charcoal of smartweed stalk
CN105126754A (en) Method for removing chromium in water through biochar through corn straw
CN102658084B (en) Preparation method of nickel nitrate modified sludge activated carbon
CN101716491A (en) Method for preparing heavy metal adsorbent by carbonizing lakebed sludge
CN110172569A (en) The method of iron ore concentrate is produced using agricultural crop straw as reducing agent suspending magnetization roasting
CN112058271A (en) Method for preparing SCR (selective catalytic reduction) low-temperature flue gas denitration catalyst by acid-modified low-titanium blast furnace slag
CN102614829A (en) Method for preparing mycotoxin adsorbent for efficient carbon silicon feed by taking rice hulls as raw materials
CN103496700A (en) Method for preparing active carbon from pyrolysis residues of cedarwood sawdust
CN106185881A (en) A kind of method that in utilization, low-carbon (LC) Fine particle processing prepares sulphur-free expanded graphite
CN103007954B (en) Multi-phase catalytic ozone oxidation catalyst and preparation method thereof
Xiao et al. Transformation of phosphorous during incineration of sewage sludge: Influence of steam and mineral
CN107159121A (en) A kind of modified activated carbon and its preparation method and application
CN102674345A (en) Method for using waste cotton stems to prepare catalyst carriers for desulfurization
CN107128912A (en) A kind of preparation method of the Chinese medicine slag activated carbon of supported ion liquid
CN103623776A (en) Method for preparing iron-based magnetic activated carbon by catalytic activation of radix puerariae waste residue with compound enzyme
CN112624559A (en) Preparation method of modified sludge-based porous biochar
CN103691448B (en) The preparation method of magnetic sludge base ozone catalyst and application
CN207786614U (en) The system for preparing magnetic bio carbon composite

Legal Events

Date Code Title Description
C06 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: 20190902

Address after: 318000 Zhonglin Village, Xinqiao Town, Luqiao District, Taizhou City, Zhejiang Province

Applicant after: Xu Haiyan

Address before: 523000 Guangdong province Dongguan City Songshan Lake high tech Industrial Zone Building 406 industrial development productivity

Applicant before: Dongguan Lianzhou Intellectual Property Operation Management Co.,Ltd.

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