CN103752285A - 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
CN103752285A
CN103752285A CN201410008599.3A CN201410008599A CN103752285A CN 103752285 A CN103752285 A CN 103752285A CN 201410008599 A CN201410008599 A CN 201410008599A CN 103752285 A CN103752285 A CN 103752285A
Authority
CN
China
Prior art keywords
solution
sorbing material
filter membrane
biological brick
brick fuel
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
CN201410008599.3A
Other languages
Chinese (zh)
Other versions
CN103752285B (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

Images

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 the biomass resource extensively existing take nature as basis, utilizes specific charring process, by the living beings carbonaceous that imperfect combustion produces under anoxia condition.Common charcoal comprises charcoal, bamboo charcoal, stalk, charcoal rice, shell charcoal etc.They are mainly comprised of aromatic hydrocarbon and simple substance carbon or the carbon with graphite-structure, contain more than 60% carbon, also comprise H, O, N, S and a small amount of trace element.Charcoal has raw material wide material sources, production cost is low, ecological safety is pollution-free, can spread etc. distinguishing feature.
Charcoal solubility is extremely low, there is height carboxylic esterification and aromatization structure, have larger porosity and specific area, these fundamental propertys make it possess absorption affinity resistance to oxidation 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 had 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 treatment be difficult for from water body, separates, this drawbacks limit 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, limited the application of Sodium Polyacrylate as water treatment agent.
What in water body, harm was larger 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 material that at present can Adsorption water body high activity pollutant exists adsorption capacity low, preparation cost compared with high, preparation difficulty is large, the follow-up shortcoming such as difficult, be restricted in the use.
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 novelty, cost are 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, mix 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 with respect to shell; at the exposed surface of sorbing material, seal three metafiltration films; described three metafiltration films are inside and outside two-layer protection filter membrane, between inside and outside two-layer protection filter membrane, Pollutants Diffusion film interlayer are set.
And; the concrete structure of described biological brick fuel is: comprise a hollow base, ring-type top cover, filling adsorption material in base are installed on base top; the upper surface of sorbing material covers inside and outside two-layer protection filter membrane, and Pollutants Diffusion film interlayer is set between two-layer filter membrane.
And described diffusion barrier allows freely to see through the molecular weight 50-1000000 of material, the aperture of outer layer protection filter membrane is 0.15-0.22 μ m, internal layer protection filter membrane aperture 0.3-0.45 μ m.
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, add successively ammonium persulfate, N, 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 that sodium borohydride is added, obtain solution A; Agarose is added in NaOH solution, constantly stir and form agarose suspension B; Solution A is added in suspension B and forms solution C, by solution C continuous stirring 12h; Mixed liquor is filtered, be 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 are as follows:
1, in the present invention, selected 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 circumnutating is stretched, facilitate the functional group with adsorptivity to be exposed to surface.Its structural formula is-[CH2CHCOONa-]-, its functional group is that carboxyl can complex reaction occur preferably with metal ion.Because PAAS belongs to water-soluble organic high molecular compound, and wrapped up with diffusion barrier, can avoid it from biological brick fuel stripping, solved PAAS and be not suitable for being directly used in the problem of wastewater treatment.
2, the present invention is directed to charcoal and remove not segregative shortcoming after pollutant, prepared a kind solid biologic brick fuel, for the charcoal problem lower to the adsorption capacity of heavy metal, added the heavy metal absorbents such as PAAS, increased the adsorption capacity of charcoal to heavy metal.
3, after the inner filling adsorption material of biological brick fuel provided by the invention, can remove water body high activity pollutant, also have adsorption capacity high, applied widely, without harmful particle stripping, adsorption efficiency advantages of higher.
4, the diffusion barrier adding in the present invention can effectively prevent PAAS or other materials stripping, and separating active substances optionally, makes this invention have the ability that endangers large pollutant in selective removal water body.
5, biological brick fuel provided by the invention has the ability of efficient removal activity, low molecule organic matter, inorganic pollution, solves the dispersiveness of charcoal to such an extent as to irretrievable shortcoming can be directly used in landfill or burning disposal after sorbing material use.
Accompanying drawing explanation
Fig. 1 is the front view of the biological brick fuel of the present invention;
Fig. 2 is the axial cutaway 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.
The specific embodiment
Below in conjunction with accompanying drawing and 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. processes.These organic wastes that form charcoal are called as " biomass ", and a lot of scientists are titled with the good reputation of charcoal " black gold ".Charcoal also can be made, and method is: in the time of temperature 500-800 ℃, by stalk, under Anaerobic Treatment 1-3 hour condition, made.
Below be divided into three parts and discuss in detail the present invention, comprising: one, the composition of sorbing material; Two, the preparation method of sorbing material; The structure of the biological brick fuel that three, sorbing material is made; 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, by charcoal and Sodium Polyacrylate (PAAS), formed, the concentration of PAAS solution is at 0.1-50g/L, describedly by 500-1000mLPAAS solution, adds 10-200g charcoal.The concentration of PAAS solution is advisable at the 60-90% of saturation moisture content with the initial water content that guarantees sorbing material at 0.1-50g/L.
Two, the preparation method of sorbing material
According to processed waste water need to prepare PAAS solution, PAAS solution is joined in charcoal, mix pressing and get final product.
The structure of the biological brick fuel that three, sorbing material is made
Comprise sorbing material and shell; sorbing material is filled in shell; sorbing material has exposed surface with respect to shell; at the exposed surface of sorbing material, seal three metafiltration films; described three metafiltration films are inside and outside two-layer protection filter membrane, between inside and outside two-layer protection filter membrane, Pollutants Diffusion film interlayer are set.
The present embodiment provides a kind of concrete structure; as shown in drawings: comprise a hollow base 2; ring-type top cover 1 is installed on base top; 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; assurance filter membrane and sorbing material are fixing base inside, and the exposed filter membrane in ring-type position in the middle of ring-type top cover is the passage of sorbing material absorption harmful substance.
The molecular weight transit dose of described diffusion barrier is that the aperture of 50-1000000, outer layer protection filter membrane is 0.15-0.22 μ m, internal layer protection filter membrane aperture 0.3-0.45 μ m.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 successively 70 μ L5-15wt% ammonium persulfates, 20 μ LN, N ,-methylene-bisacrylamide, after mixing, pour in mould, preparing aquagel membrane is diffusion barrier.
The molecular weight transit dose of the gel mould of preparing is 50-1000000, and thickness is 0.8mm.
The preparation method of crosslinking agent is: in the 10-20mL allyl glycidyl ether that 200-400mg sodium borohydride is added, 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 forms solution C, by solution C continuous stirring 12h; Mixed liquor is filtered, be 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) the PAAS solution that is mixed with 1g/L, adds 100mLPAAS solution in 1g charcoal, and charcoal is mixed with PAAS solution;
(2) mixed liquor is poured in the effigurate mould of tool, taken out brick fuel;
(3) on brick fuel, cover successively 0.45 μ m filter membrane, diffusion barrier, 0.22 μ m filter membrane, 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 not dropping to.

Claims (10)

1. for a water body purification sorbing material, it is characterized in that: 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. according to claim 1 for water body purification sorbing material, it is characterized in that: described polyacrylic molecular weight is 3,000 ten thousand.
3. according to claim 1 for water body purification sorbing material, it is characterized in that: the preparation method of described sorbing material is: first prepare PAAS solution, PAAS solution is joined in charcoal, mix pressing and get final product.
4. one kind comprises the biological brick fuel of the sorbing material described in claim 1 or 2; it is characterized in that: comprise sorbing material and shell; sorbing material is filled in shell; sorbing material has exposed surface with respect to shell; at the exposed surface of sorbing material, seal three metafiltration films; described three metafiltration films are inside and outside two-layer protection filter membrane, between inside and outside two-layer protection filter membrane, Pollutants Diffusion film interlayer are set.
5. biological brick fuel according to claim 4; 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, and Pollutants Diffusion film interlayer is set between two-layer filter membrane.
6. biological brick fuel according to claim 4, is characterized in that: described diffusion barrier allows freely to see through the molecular weight 50-1000000 of material, the aperture of outer layer protection filter membrane is 0.15-0.22 μ m, internal layer protection filter membrane aperture 0.3-0.45 μ m.
7. biological brick fuel according to claim 4, 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.
8. biological brick fuel according to claim 4, it is characterized in that: 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, add successively ammonium persulfate, N, N,-methylene-bisacrylamide, pours into after mixing in mould, and acquisition aquagel membrane is diffusion barrier.
9. biological brick fuel according to claim 8, is characterized in that: the preparation method of described crosslinking agent is: in the allyl glycidyl ether that sodium borohydride is added, obtain solution A; Agarose is added in NaOH solution, constantly stir and form agarose suspension B; Solution A is added in suspension B and forms solution C, by solution C continuous stirring 12h; Mixed liquor is filtered, be 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.
10. biological brick fuel according to claim 4, 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 true CN103752285A (en) 2014-04-30
CN103752285B 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)

Cited By (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
CN115286454A (en) * 2022-08-22 2022-11-04 四川络布新材料科技有限公司 Special fertilizer for promoting crop yield increase and preparation method thereof
CN116375301A (en) * 2023-06-05 2023-07-04 山东国宏生物科技有限公司 Soybean oil wastewater treatment method

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002253960A (en) * 2001-02-27 2002-09-10 Tanimoto Daiki Deodorant and production method therefor
CN1441751A (en) * 2000-04-21 2003-09-10 沃特维森斯国际公司 Formation of composite materials with expandable matter
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

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1441751A (en) * 2000-04-21 2003-09-10 沃特维森斯国际公司 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

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
A.EWECHAROEN等: "Nickel adsorption by sodium polyacrylate-grafted activate dcarbon", 《JOURNAL OF HAZARDOUS MATERIALS》 *
王改娟等: "纳米孔聚丙烯酸-活性炭复合材料的制备及吸附性能", 《化工新型材料》 *

Cited By (5)

* 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
CN115286454A (en) * 2022-08-22 2022-11-04 四川络布新材料科技有限公司 Special fertilizer for promoting crop yield increase and preparation method thereof
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
CN116375301A (en) * 2023-06-05 2023-07-04 山东国宏生物科技有限公司 Soybean oil wastewater treatment method
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

Also Published As

Publication number Publication date
CN103752285B (en) 2015-06-03

Similar Documents

Publication Publication Date Title
Rwiza et al. Comparative sorption isotherms and removal studies for Pb (II) by physical and thermochemical modification of low-cost agro-wastes from Tanzania
Wang et al. Adsorption of heavy metal onto biomass-derived activated carbon
CN107469768A (en) A kind of animal dung biogas residue charcoal/manganese oxide composite material and preparation method 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
CN106861642B (en) A kind of preparation and application of the biomass-based hydrogel with high absorption capacity
Putro et al. Biosorption of dyes
CN103848473A (en) Method for removing methylene blue dye in wastewater through walnut shell biomass charcoal adsorbent
Alves et al. The potential of activated carbon in the treatment of water for human consumption, a study of the state of the art and its techniques used for its development
CN104084126A (en) Preparation method of biomass-based ferroaluminium complex spherical carbon
CN104261504B (en) A kind of method utilizing modification bamboo charcoal to remove sulfamethoxazole in water body
Vieira et al. An overview of forest residues as promising low-cost adsorbents
Sanagi Recent advances in the preparation of oil palm waste-based adsorbents for removal of environmental pollutants-a review
CN107555414B (en) Garden waste biomass charcoal and preparation method and application thereof
CN103922835B (en) A kind of environment-friendly type charcoal base that utilizes adsorbs the method manufacturing organic fertilizer
Hamzeh et al. Removal of reactive Remazol Black B from contaminated water by lignocellulosic waste of canola stalks
Hui et al. Isotherm studies of methylene blue adsorption onto potassium salts-modified textile sludge
Joseph et al. Behavior of malachite green with different adsorption matrices
CN107597068B (en) Preparation method of deodorized sludge carbon cloth
CN115959808A (en) Remediation method for removing heavy metal pollution of river and lake bottom mud
CN101708873A (en) Method for purifying lead-bearing waste water with humic acid modified carbon nano-tubes
Raut et al. A review on activated carbon preparation from natural and eco-friendly raw materials
CN104667859A (en) Calcium bicarbonate modified diatomite adsorbent
CN203728605U (en) Portable and flexible water pollutant adsorption device

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

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

TR01 Transfer of patent right
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20150603

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