CN103752285B - Absorbent material for water body purification and biological carbon brick - Google Patents

Absorbent material for water body purification and biological carbon brick Download PDF

Info

Publication number
CN103752285B
CN103752285B CN201410008599.3A CN201410008599A CN103752285B CN 103752285 B CN103752285 B CN 103752285B CN 201410008599 A CN201410008599 A CN 201410008599A CN 103752285 B CN103752285 B CN 103752285B
Authority
CN
China
Prior art keywords
solution
biological brick
brick fuel
filter membrane
sorbing material
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.)
Expired - Fee Related
Application number
CN201410008599.3A
Other languages
Chinese (zh)
Other versions
CN103752285A (en
Inventor
赵玉杰
夏青
刘潇威
周其文
张铁亮
林繁
潘杨
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 Fu Xiang Ecological Environmental Polytron Technologies Inc
Original Assignee
Agro Environmental Protection Institute Ministry of Agriculture
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 Agro Environmental Protection Institute Ministry of Agriculture filed Critical Agro Environmental Protection Institute Ministry of Agriculture
Priority to CN201410008599.3A priority Critical patent/CN103752285B/en
Publication of CN103752285A publication Critical patent/CN103752285A/en
Application granted granted Critical
Publication of CN103752285B publication Critical patent/CN103752285B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Landscapes

  • Water Treatment By Sorption (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)
  • Solid Fuels And Fuel-Associated Substances (AREA)

Abstract

The invention relates to an absorbent material for water body purification and a biological carbon brick; the absorbent material disclosed by the invention is composed of biological carbon and sodium polyacrylate (PAAS); the concentration of the PAAS solution is 0.1-50g/L; 10-200 g of biological carbon is added into 500-1000 mL of PAAS solution; the biological carbon brick comprises a hollow base; an annular top cover is installed on the top end of the base; the absorbent material is filled in the base; two layers of protective filter films cover the upper surface of the absorbent material; and a diffusion film interlayer is arranged between the two layers of filter films. According to the invention, due to the added diffusion film, PAAS and biological carbon can be effectively prevented from being dissolved; pollutants having high activity and low molecular weight are allowed to freely diffuse to enter the biological carbon brick, and therefore, the absorbent material for water body purification and the biological carbon brick disclosed by the invention have the capability of selectively eliminating hazard pollutants in a water body.

Description

For water body purification sorbing material and biological brick fuel
Technical field
The invention belongs to environmental science, relate to the sorbing material for water body purification, especially a kind of for water body purification sorbing material and biological brick fuel.
Background technology
Charcoal typically refers to based on the biomass resource that extensively exists by nature, utilizes specific charring process, by the living beings carbonaceous that produces of imperfect combustion under anoxic conditions.Common charcoal comprises charcoal, bamboo charcoal, stalk, charcoal rice, shell charcoal etc.They, primarily of aromatic hydrocarbon and simple substance carbon or the carbon composition with graphite-structure, containing the carbon of more than 60%, also comprise H, O, N, S and a small amount of trace element.Charcoal has that raw material sources is extensive, production cost is low, ecological safety is pollution-free, can the distinguishing feature such as spread.
Charcoal solubility is extremely low, there is height carboxylic esterification and aromatization structure, have larger porosity and specific area, these fundamental propertys absorption affinity resistance to oxidation that made it possess and the strong characteristic of antibiont capacity of decomposition, can be widely used in removing the organic and inorganic pollution in water.
Charcoal is owing to having larger porosity, specific area, it is made to have great advantage on Adsorption of Heavy Metals and organic pollution, but because biological carbon is the black puffy solid matter that particle is careful, quality is lighter, charcoal after process is not easily separated from water body, and this shortcoming limits the application of charcoal.
Sodium Polyacrylate is-kind of water-soluble high-molecular compound, water soluble forms thick liquid, to the heavy metal in water body particularly bivalent metal ion have superpower sequestering power, but because Sodium Polyacrylate after the restriction chelating of content of beary metal is still water miscible, cannot be removed, be limited the application of Sodium Polyacrylate as water treatment agent.
Endangering larger in water body is active pollutant, active pollutant is as ionic state heavy metal, agricultural chemicals, low molecule POPs etc. can produce direct harm to biological and ecological environment, eliminating and processing active pollutant in water body is problem in urgent need to solve, and at present can the material of Adsorption water body high activity pollutant to there is adsorption capacity low, preparation cost compared with high, preparation difficulty is large, the follow-up shortcoming such as difficult, use is restricted.
Summary of the invention
The object of the invention is to overcome the deficiencies in the prior art part, provide that a kind of material is novel, cost is low, advantages of good adsorption effect for water body purification sorbing material and biological brick fuel.
The technical scheme that the present invention realizes object is as follows:
A kind of for water body purification sorbing material, the solution that described material is formed by charcoal and Sodium Polyacrylate, the concentration of described PAAS is at 0.1-50g/L, and the content of described charcoal is 20-400g/L.
And described polyacrylic molecular weight is 3,000 ten thousand.
And the preparation method of described sorbing material is: first prepare PAAS solution, PAAS solution is joined in charcoal, mixes pressing and get final product.
A kind of biological brick fuel of sorbing material; comprise sorbing material and shell; sorbing material is filled in shell; sorbing material has exposed surface relative to shell; three metafiltration films are sealed at the exposed surface of sorbing material; described three metafiltration films are inside and outside two-layer protection filter membrane, between inside and outside two-layer protection filter membrane, arrange Pollutants Diffusion film interlayer.
And; the concrete structure of described biological brick fuel is: comprise a hollow base, installs ring-type top cover, filling adsorption material in base on base top; the upper surface of sorbing material covers inside and outside two-layer protection filter membrane, arranges Pollutants Diffusion film interlayer between two-layer filter membrane.
And it is 0.15-0.22 μm through the molecular weight 50-1000000 of material, the aperture of outer layer protection filter membrane that described diffusion barrier allows free, internal layer protection filter sizes 0.3-0.45 μm.
And the thickness of described diffusion barrier is 0.8mm, the thickness of inside and outside layer protection filter membrane is 0.1mm.
And, the preparation method of described diffusion barrier is: by acrylamide, crosslinking agent, ammonium persulfate, N, N, the hydrogel that-methylene-bisacrylamide is made, its preparation method is: acrylamide solution, crosslinking agent, high purity water are mixed, and adds ammonium persulfate, N successively, N,-methylene-bisacrylamide, pours into after mixing in mould, and acquisition aquagel membrane is diffusion barrier.
And the preparation method of described crosslinking agent is: in the allyl glycidyl ether added by sodium borohydride, obtain solution A; Agarose is added in NaOH solution, constantly stir and form agarose suspension B; Solution A is added in suspension B and form solution C, solution C is stirred 12h continuously; Mixed liquor is filtered, is washed till neutrality with distilled water; Dehydration, vacuum drying, obtains required crosslinking agent, described sodium borohydride: allyl glycidyl ether: agarose: NaOH weight ratio=0.2-0.4:9-20:5-15:3.6-6.
And described diffusion barrier is by acrylamide, crosslinking agent, ammonium persulfate, N, N, the hydrogel that-methylene-bisacrylamide is made.
Beneficial effect of the present invention and good effect as follows:
1, selected in the present invention Sodium Polyacrylate (PAAS) is the macromolecular compound of a kind of wire, solubility, carboxyl on its strand is due to electrostatic repulsion effect, the polymer chain circumnutated is stretched, facilitates the functional group with adsorptivity to be exposed to surface.Its structural formula is-[-CH2CHCOONa-]-, its functional group is that carboxyl preferably complex reaction can occur with metal ion.Because PAAS belongs to water-soluble organic high molecular compound, and wrapped up with diffusion barrier, it can be avoided from biological brick fuel stripping, solve the problem that PAAS is not suitable for being directly used in wastewater treatment.
2, the present invention is directed to charcoal and remove not segregative shortcoming after pollutant, prepare a kind solid biologic brick fuel, for the problem that the adsorption capacity of charcoal heavy metal is lower, add the heavy metal absorbents such as PAAS, add the adsorption capacity of charcoal heavy metal.
3, after the inner filling adsorption material of biological brick fuel provided by the invention, water body high activity pollutant can be removed, also have adsorption capacity high, applied widely, without unwanted particles stripping, adsorption efficiency advantages of higher.
4, the diffusion barrier added in the present invention effectively can prevent PAAS or other materials stripping, and optionally separating active substances, make this invention have the ability endangering large pollutant in selective removal water body.
5, biological brick fuel provided by the invention has the ability efficiently removing activity, low molecule organic matter, inorganic pollution, solves the dispersiveness of charcoal to such an extent as to irretrievable shortcoming, and sorbing material can be directly used in landfill or burning disposal after using.
Accompanying drawing explanation
Fig. 1 is the front view of the biological brick fuel of the present invention;
Fig. 2 is the axial sectional view of Fig. 1;
Fig. 3 is the top view of Fig. 1;
Fig. 4 is the structural representation (axially analysing and observe) of another biological carbon brick.
Detailed description of the invention
Below in conjunction with accompanying drawing, also by specific embodiment, the invention will be further described, and following examples are descriptive, are not determinate, can not limit protection scope of the present invention with this.
The present invention's raw material used is commercially available, and wherein, charcoal is by organic waste, as animal wastes, and animal bone, plant roots and stems, a kind of porous carbon that wood chip and Wheat Straw etc. process.These organic wastes forming charcoal are called as " biomass ", and a lot of scientist is titled with the good reputation of charcoal " black gold ".Charcoal also can make, and method is: be made up under condition at Anaerobic Treatment 1-3 hour of stalk when temperature 500-800 DEG C.
Below be divided into three parts and discuss the present invention in detail, comprising: one, the composition of sorbing material; Two, the preparation method of sorbing material; Three, the structure of biological brick fuel made of sorbing material; Four, the preparation method of diffusion barrier in biological brick fuel; Five, the absorption example of biological brick fuel.
One, the composition of sorbing material
For water body purification sorbing material, be made up of charcoal and Sodium Polyacrylate (PAAS), the concentration of PAAS solution, at 0.1-50g/L, describedly adds 10-200g charcoal by 500-1000mLPAAS solution.The concentration of PAAS solution at 0.1-50g/L to ensure that the initial water content of sorbing material is advisable at the 60-90% of saturation moisture content.
Two, the preparation method of sorbing material
Need preparation PAAS solution according to handled waste water, PAAS solution is joined in charcoal, mixes pressing and get final product.
Three, the structure of biological brick fuel made of sorbing material
Comprise sorbing material and shell; sorbing material is filled in shell; sorbing material has exposed surface relative to shell; three metafiltration films are sealed at the exposed surface of sorbing material; described three metafiltration films are inside and outside two-layer protection filter membrane, between inside and outside two-layer protection filter membrane, arrange Pollutants Diffusion film interlayer.
The present embodiment provides a kind of concrete structure; as shown in drawings: comprise a hollow base 2; on base top, ring-type top cover 1 is installed; filling adsorption material 6 in base; the upper surface of sorbing material covers internal layer protection filter membrane 5, outer layer protection filter membrane 3; Pollutants Diffusion film interlayer 4 is set between two-layer filter membrane; the superiors' filter membrane is concordant with the upper surface of base; by the pressing of ring-type top cover; ensure fixing at chassis interior of filter membrane and sorbing material, the exposed filter membrane in the ring-type position of ring-type top cover centre is the passage of sorbing material adsorb harmful components.
The molecular weight transit dose of described diffusion barrier is 50-1000000, the aperture of outer layer protection filter membrane is 0.15-0.22 μm, internal layer protection filter sizes 0.3-0.45 μm.The thickness of described diffusion barrier is 0.8mm, and the thickness of inside and outside layer protection filter membrane is 0.1mm.
Four, the preparation method of diffusion barrier in biological brick fuel
Described diffusion barrier is by acrylamide, crosslinking agent, ammonium persulfate, N, N, the hydrogel that-methylene-bisacrylamide is made; In 100ml, weight ratio is acrylamide: crosslinking agent: ammonium persulfate: N, N ,-methylene-bisacrylamide=20:0.3:0.0035:0.2.
Its preparation method is: the crosslinking agent of the acrylamide solution of 50mL30-50wt%, 10mL1-3wt%, 40mL high purity water are mixed, add 70 μ L5-15wt% ammonium persulfates, 20 μ LN successively, N ,-methylene-bisacrylamide, pour into after mixing in mould, preparing aquagel membrane is diffusion barrier.
The molecular weight transit dose of the gel mould prepared is 50-1000000, and thickness is 0.8mm.
The preparation method of crosslinking agent is: in the 10-20mL allyl glycidyl ether added by 200-400mg sodium borohydride, obtain solution A; 5-15g agarose is added in 300mL0.3-0.5mol/LNaOH solution, constantly stir and form agarose suspension B; Solution A is added in suspension B and form solution C, solution C is stirred 12h continuously; Mixed liquor is filtered, is washed till neutrality with distilled water; Dehydration, vacuum drying, obtains required crosslinking agent.
Described sodium borohydride: allyl glycidyl ether: agarose: NaOH weight ratio=0.2-0.4:9-20:5-15:3.6-6.
Five, the absorption example of biological brick fuel
(1) be mixed with the PAAS solution of 1g/L, 100mLPAAS solution is added in 1g charcoal, charcoal is mixed with PAAS solution;
(2) mixed liquor is poured in the effigurate mould of tool, take out brick fuel;
(3) on brick fuel, cover 0.45 μm of filter membrane, diffusion barrier, 0.22 μm of filter membrane successively, and fix with support, be prepared into biological brick fuel; Diffusion barrier is diffusion barrier prepared by step 4;
(4) biological brick fuel is put into the Pb2+ solution of 500mL200mg/L, after 24h, in solution, Pb2+ concentration does not detect for dropping to.

Claims (7)

1. a biological brick fuel, it is characterized in that: comprise sorbing material and shell, sorbing material is filled in shell, sorbing material has exposed surface relative to shell, three metafiltration films are sealed at the exposed surface of sorbing material, described three metafiltration films are inside and outside two-layer protection filter membrane, between inside and outside two-layer protection filter membrane, arrange Pollutants Diffusion film interlayer;
The solution that described material is formed by charcoal and Sodium Polyacrylate, the concentration of described PAAS is at 0.1-50g/L, and the content of described charcoal is 20-400g/L.
2. biological brick fuel according to claim 1; it is characterized in that: the concrete structure of described biological brick fuel is: comprise a hollow base; on base top, ring-type top cover is coaxially installed; filling adsorption material in base; the upper surface of sorbing material covers inside and outside two-layer protection filter membrane, arranges Pollutants Diffusion film interlayer between two-layer filter membrane.
3. biological brick fuel according to claim 1, is characterized in that: it is 0.15-0.22 μm through the molecular weight 50-1000000 of material, the aperture of outer layer protection filter membrane that described diffusion barrier allows free, internal layer protection filter sizes 0.3-0.45 μm.
4. biological brick fuel according to claim 1, is characterized in that: the thickness of described diffusion barrier is 0.8mm, and the thickness of inside and outside layer protection filter membrane is 0.1mm.
5. biological brick fuel according to claim 1, it is characterized in that: the preparation method of described diffusion barrier is: acrylamide solution, crosslinking agent, high purity water are mixed, add ammonium persulfate, N successively, N,-methylene-bisacrylamide, pour into after mixing in mould, acquisition aquagel membrane is diffusion barrier.
6. biological brick fuel according to claim 5, is characterized in that: the preparation method of described crosslinking agent is: in the allyl glycidyl ether added by sodium borohydride, obtain solution A; Agarose is added in NaOH solution, constantly stir and form agarose suspension B; Solution A is added in suspension B and form solution C, solution C is stirred 12h continuously; Mixed liquor is filtered, is washed till neutrality with distilled water; Dehydration, vacuum drying, obtains required crosslinking agent, described sodium borohydride: allyl glycidyl ether: agarose: NaOH weight ratio=0.2-0.4:9-20:5-15:3.6-6.
7. biological brick fuel according to claim 1, is characterized in that: described diffusion barrier is by acrylamide, crosslinking agent, ammonium persulfate, N, N, the hydrogel that-methylene-bisacrylamide is made.
CN201410008599.3A 2014-01-08 2014-01-08 Absorbent material for water body purification and biological carbon brick Expired - Fee Related CN103752285B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201410008599.3A CN103752285B (en) 2014-01-08 2014-01-08 Absorbent material for water body purification and biological carbon brick

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201410008599.3A CN103752285B (en) 2014-01-08 2014-01-08 Absorbent material for water body purification and biological carbon brick

Publications (2)

Publication Number Publication Date
CN103752285A CN103752285A (en) 2014-04-30
CN103752285B true CN103752285B (en) 2015-06-03

Family

ID=50519692

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201410008599.3A Expired - Fee Related CN103752285B (en) 2014-01-08 2014-01-08 Absorbent material for water body purification and biological carbon brick

Country Status (1)

Country Link
CN (1) CN103752285B (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112774633A (en) * 2021-01-15 2021-05-11 复旦大学 Method for preparing biochar from wet garbage and application of biochar
CN115286454B (en) * 2022-08-22 2023-10-13 四川络布新材料科技有限公司 Special fertilizer for promoting crop yield increase and preparation method thereof
CN116375301B (en) * 2023-06-05 2023-08-18 山东国宏生物科技有限公司 Soybean oil wastewater treatment method

Family Cites Families (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2001081249A1 (en) * 2000-04-21 2001-11-01 Watervisions International, Inc. Formation of composite materials with expandable matter
JP2002253960A (en) * 2001-02-27 2002-09-10 Tanimoto Daiki Deodorant and production method therefor
CN101234341A (en) * 2008-02-28 2008-08-06 上海交通大学 Method for preparing functional polymer-active carbon composite material for water treatment

Also Published As

Publication number Publication date
CN103752285A (en) 2014-04-30

Similar Documents

Publication Publication Date Title
Qiu et al. Application of biochar for the adsorption of organic pollutants from wastewater: Modification strategies, mechanisms and challenges
Rwiza et al. Comparative sorption isotherms and removal studies for Pb (II) by physical and thermochemical modification of low-cost agro-wastes from Tanzania
Selvakumar et al. Biosorption of Rhodamine B onto novel biosorbents from Kappaphycus alvarezii, Gracilaria salicornia and Gracilaria edulis
Ait Haki et al. Efficient removal of crystal violet dye from aqueous solutions using sodium hydroxide-modified avocado shells: kinetics and isotherms modeling
CN105289524A (en) Shaddock peel heavy metal adsorbent and preparation method and application thereof
CN104289177A (en) Preparation method of charcoal for heavy metal wastewater purification
CN110577218B (en) Impregnation method biomass-based activated coke and preparation method thereof
CN103752285B (en) Absorbent material for water body purification and biological carbon brick
Vieira et al. An overview of forest residues as promising low-cost adsorbents
Gupta et al. Adsorptive remediation of Cu (II) and Ni (II) by microwave assisted H3PO4 activated carbon
Dos Santos et al. Syagrus oleracea–activated carbon prepared by vacuum pyrolysis for methylene blue adsorption
Putro et al. Biosorption of dyes
CN104261504B (en) A kind of method utilizing modification bamboo charcoal to remove sulfamethoxazole in water body
CN103848473A (en) Method for removing methylene blue dye in wastewater through walnut shell biomass charcoal adsorbent
CN106861642A (en) A kind of preparation and application of the biomass-based hydrogel with high absorption capacity
Hanafiah et al. Methylene blue adsorption on Aloe vera rind powder: Kinetics, Isotherm and Mechanisms
Sanagi Recent advances in the preparation of oil palm waste-based adsorbents for removal of environmental pollutants-a review
Xia et al. Mesoporous activated biochar for as (III) adsorption: a new utilization approach for biogas residue
Song et al. Adsorption of crystal violet onto epichlorohydrin modified corncob
Hui et al. Isotherm studies of methylene blue adsorption onto potassium salts-modified textile sludge
El Hajam et al. Adsorptive removal of brilliant green dye from aqueous solutions using cedar and mahogany sawdusts
CN107511141A (en) A kind of composite cellulosic membrane for adsorbing heavy metal and preparation method thereof
Hamzeh et al. Removal of reactive Remazol Black B from contaminated water by lignocellulosic waste of canola stalks
Joseph et al. Behavior of malachite green with different adsorption matrices
CN108176371B (en) Kaolin composite adsorption material and preparation method and application 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
C14 Grant of patent or utility model
GR01 Patent grant
TR01 Transfer of patent right
TR01 Transfer of patent right

Effective date of registration: 20170619

Address after: 201315 room, room 2, No. 506, Pu Pu Road, Shanghai, Pudong New Area, China, 2388

Patentee after: Shanghai Fu Xiang ecological environmental Polytron Technologies Inc.

Address before: 300191 Tianjin city Nankai District Fukang Road No. 31

Patentee before: Agro-Environmental Protection Institute of Ministry of Agriculture

CF01 Termination of patent right due to non-payment of annual fee
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20150603