CN107321384A - The preparation method and applications of lignocellulosic ester/sodium alginate complex spherical class fenton catalyst - Google Patents

The preparation method and applications of lignocellulosic ester/sodium alginate complex spherical class fenton catalyst Download PDF

Info

Publication number
CN107321384A
CN107321384A CN201710498150.3A CN201710498150A CN107321384A CN 107321384 A CN107321384 A CN 107321384A CN 201710498150 A CN201710498150 A CN 201710498150A CN 107321384 A CN107321384 A CN 107321384A
Authority
CN
China
Prior art keywords
acid
sodium alginate
preparation
solid waste
ball
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
CN201710498150.3A
Other languages
Chinese (zh)
Other versions
CN107321384B (en
Inventor
黄祖强
张燕娟
陈彦鄂
胡华宇
覃杏珍
杨梅
黄爱民
沈芳
冯振飞
覃宇奔
伍娟
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.)
Guangxi University
Original Assignee
Guangxi University
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 Guangxi University filed Critical Guangxi University
Priority to CN201710498150.3A priority Critical patent/CN107321384B/en
Publication of CN107321384A publication Critical patent/CN107321384A/en
Application granted granted Critical
Publication of CN107321384B publication Critical patent/CN107321384B/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
    • B01J31/00Catalysts comprising hydrides, coordination complexes or organic compounds
    • B01J31/02Catalysts comprising hydrides, coordination complexes or organic compounds containing organic compounds or metal hydrides
    • B01J31/06Catalysts comprising hydrides, coordination complexes or organic compounds containing organic compounds or metal hydrides containing polymers
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00Catalysts, in general, characterised by their form or physical properties
    • B01J35/60Catalysts, in general, characterised by their form or physical properties characterised by their surface properties or porosity
    • B01J35/61Surface area
    • B01J35/612Surface area less than 10 m2/g
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00Catalysts, in general, characterised by their form or physical properties
    • B01J35/60Catalysts, in general, characterised by their form or physical properties characterised by their surface properties or porosity
    • B01J35/63Pore volume
    • B01J35/638Pore volume more than 1.0 ml/g
    • 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
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/725Treatment of water, waste water, or sewage by oxidation by catalytic oxidation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/308Dyes; Colorants; Fluorescent agents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/34Organic compounds containing oxygen
    • C02F2101/345Phenols
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2305/00Use of specific compounds during water treatment
    • C02F2305/02Specific form of oxidant
    • C02F2305/026Fenton's reagent

Landscapes

  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Engineering & Computer Science (AREA)
  • Materials Engineering (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Catalysts (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

The invention provides the preparation method of lignocellulosic ester/sodium alginate complex spherical class fenton catalyst, applied to field of waste water treatment.Cellulosic solid waste is first dried, crushed by this method, obtain cellulosic solid waste powder, it is well mixed again with esterifying agent, molysite and/or ferrous salt, add in mechanical activation solid phase reactor, ball milling simultaneously carries out esterification, separation esterification products and abrading-ball, obtains after lignocellulosic ester admixture, it is added under conditions of stirring in sodium alginate soln, obtains blended liquid;Blended liquid is instilled in calcium chloride solution, crosslinking curing, filtering, and gel ball solidified, load iron is dried, produces target product.The present invention, for raw material, is turned waste into wealth with cellulosic solid waste etc., the treatment of wastes with processes of wastes against one another, recycling, the higher value application of cellulosic solid waste are realized, products therefrom can produce Fenton effect, and be loose structure, water treatment effect is excellent, non-secondary pollution, repeats utilization rate high.

Description

The preparation method of lignocellulosic ester/sodium alginate complex spherical class fenton catalyst And its application
Technical field
The invention belongs to field of waste water treatment, it is related to lignocellulosic modification, specifically lignocellulosic ester/sea The preparation method and applications of mosanom complex spherical class fenton catalyst.
Background technology
With chemical industry and its high speed development of related industry, especially chemical industry, agricultural chemicals, medicine, papermaking, printing and dyeing, smelting The development of the industries such as gold, a large amount of industrial wastewaters not standard discharge causes the section in the whole nation more than 1/3rd to be contaminated, and 90% Urban waters above are seriously polluted, and nearly 50% key cities water head site does not meet drinking water standard.Wherein, organic wastewater Type and quantity are increasing, and existence time length, migration circle are wide in water, handle for the organic pollution of these difficult for biological degradation Difficulty is big, and the harm to ecological environment and human health is increasingly serious, and traditional treatment technology is difficult to meet higher and higher ring Guaranteed request.Therefore, the technology developed efficiently, economic has been compeled for handling difficult for biological degradation, highly toxic organic pollutant wastewater In the eyebrows and eyelashes.High-level oxidation technology is a kind of New Wastewater Treatment Technology art, active extremely strong using what is produced in chemical reaction process Free radical (such as OH, HO2Deng) organic pollution macromolecular is degraded to low toxicity or nontoxic small molecule, or even directly Mineralising is connect for water and carbon dioxide.The effect of deep oxidation degraded is reached, it is necessary to efficient oxidation catalyst.Conventional at present Containing heavy metal catalyst, easily in the solution, catalyst is difficult to biodegradation to residual after, causes secondary pollution more, and And high is required to pH value, therefore complex operation, processing cost are higher.
Processing difficult degradation industrial organic waste water mainly uses Fenton (Fenton) oxidation technology, but Fenton oxygen at present There are still following not enough in use for change system:
1st, Fenton processing labor intensity is big:Hydrogen peroxide operation difficulty is big, and it must be solid that ferrous sulfate, which is added, and sulfuric acid is sub- Iron iron content 20% or so, relative to 11% iron content of Polyferric Sulfate, considerably increases Treatment of Sludge intensity;
2nd, the cost of Fenton processing is high, and sludge is more:The oxidation of hydrogen peroxide, which can not give full play to, makes reagent cost higher, And ferrous sulfate adds the amount sludge brought, processing cost it is high (cost that present most enterprises are calculated toward contact not Including sludge increase), in addition with equipment depreciation, maintenance cost etc.;
3rd, Fenton processing easily returns color:Dosage such as hydrogen peroxide and ferrous sulfate is bad with adding ratio control, or three Valency iron does not precipitate the aqueous solution being easily caused after processing and shows slightly yellow or yellowish-brown;
4th, Fenton processing corrosivity is big:Hydrogen peroxide has strong oxidizing property, and its oxidisability is only second to fluorine gas, can aoxidize equipment Corrosion, if protection is bad a certain degree of corrosion to human body;
5th, it can not reuse.
Publication No. CN104646062A Chinese invention patent application, the applying date 2015 year 02 month 12, publication date On 05 27th, 2015, a kind of plain basis set of bamboo pulp fiber was described into fenton catalyst Fe3+C2O4/ R preparation method, main points It is to be coordinated to form complex compound Fe by ferric iron and oxalic acid3+C2O4/ R, then it is carried on the bamboo pulp fiber synthesized by bamboo pulpboard On plain base porous resin R, integrated fenton catalyst Fe is formed3+C2O4/ R, can accelerate catalyzing hydrogen peroxide to drop under visible light Solve dye class organic pollution in dyeing waste water.The patent application do not disclosed in embodiment its how to carry out wastewater treatment and The data result of processing, it is impossible to learn its effect.
Publication No. CN105289527A Chinese invention patent applications, December 03 2015 applying date, publication date 2016 In 03 day 02 month year, a kind of preparation method of cellulose esters aerogel material is described, using cellulose as raw material, with long chain fatty acids Acyl chlorides is esterifying reagent, and carrying out esterification modification to cellulose prepares cellulose esters, and cellulose esters is dissolved in certain solvent, then is passed through Solvent reclamation exchanges and prepares cellulose esters aeroge sorbing material.This method is non-solid phase reaction, using compared with multi-solvent.
China has abundant lignocellulosic sources, and southern each province is especially prominent, source such as sugarcane, cassava, wood chip, bamboo Bits, stalk, ramulus mori etc..Resource is made full use of, the renewable new material of high added value is prepared, meets national development recycling economy political affairs Plan, has important practical significance
The content of the invention
An object of the present invention be just to provide a kind of catalysis efficiency it is high, without heavy metal ion, simple production process and Can by lignocellulosic comprehensively utilize get up lignocellulosic ester/sodium alginate complex spherical class fenton catalyst, and by its For handling waste water.
The concrete scheme of the present invention is as follows:
Cellulosic solid waste is dried, crushed, and obtains cellulosic solid waste powder;
Cellulosic solid waste powder, esterifying agent, molysite and/or ferrous salt, are well mixed, obtain mixture;
Mixture is added in mechanical activation solid phase reactor, and ball milling simultaneously carries out esterification, separation esterification products and abrading-ball, Obtain lignocellulosic ester admixture;
Lignocellulosic ester admixture is added in sodium alginate soln under conditions of stirring, obtains blended liquid;
Blended liquid is instilled in calcium chloride solution, crosslinking curing, filtering, and gel ball solidified, load iron is dried, Produce target product lignocellulosic ester/sodium alginate complex spherical class fenton catalyst.
Further, cellulosic solid waste powder:Esterifying agent:Molysite and/or ferrous salt=100:5-30:1-8, the ratio It is mass ratio.
Further, the mass ratio of lignocellulosic ester admixture and sodium alginate is 4-8:1, the matter of sodium alginate soln Amount concentration is 1-5%.
Further, esterifying agent includes oxalic acid, malonic acid, butanedioic acid, glutaric acid, adipic acid, pimelic acid, suberic acid, horse Come any of sour, butene dioic acid, glutaconate, malic acid, amino acid, citric acid or two or more combinations.Esterifying agent Occurs esterification with cellulosic solid waste.
Further, the molysite is FeCl3、Fe(NO3)3、Fe2(SO4)3Any of or two or more combinations, The ferrous salt is FeCl2、Fe(NO3)2、FeSO4Any of or two or more combinations, the effect of molysite or ferrous salt There are two aspects, one is the esterification for being catalyzed lignocellulosic, and two are carried on target product, play class fenton catalyst Effect.
Further, the mass concentration of calcium chloride solution is 3-6%, and the time of crosslinking curing is 2-12 hours, gel ball Drying means any of can be dehydrated using vacuum dehydrating at lower temperature, freeze-drying, vacuum and low temperature oil bath.
Further, mixture and grinding media heap volume are according to 100g:200-600mL ratio adds mechanical activation solid phase In reactor, carry out after ball-milling reaction, reaction 0.5-1.5h, stop in the case where rotating speed is 200-600rpm and 30-60 DEG C of constant temperature Only heat and stir, separation product and abrading-ball obtain lignocellulosic ester admixture.
Further, cellulosic solid waste is that bagasse, cassava grain stillage, Cassava stalk, wood chip, bamboo scraps, stalk, ramulus mori are any One or more kinds of combinations.
Further, cellulosic solid waste is dried, the requirement of crushing is:Water content is less than 15%, is crushed to 20-60 mesh.
Further, described mechanical activation solid phase reactor stirs for horizontal and/or verticle reinforced polysaccharide modified-high polymer Mix ball-milling reaction device.
Described Horizontal reinforced polysaccharide polymer modification agitating ball mill reactor, agent structure includes agitating device, ball milling Cylinder, mill ball, charging aperture, motor and the discharging opening being placed in ball grinding cylinder, described agitating device include the master being sequentially connected Axle, feather key, spline fitting, U-shaped frame and the blades for transmitting moment of torsion, the master that described motor passes through transmission device and agitating device Axle connects and drives U-shaped frame to radially wobble along main shaft, and described blades stirs mill ball under the drive of U-shaped frame and rolled in ball grinding cylinder Dynamic, ball-milling reaction device also includes constant temperature system.
The verticle reinforced polysaccharide modified-high polymer stirring ball-milling reaction device, it is to be driven by drive device by shaft coupling Agitating shaft, it also include cylinder cover plate, grinding inner cylinder, cooling jacket, liner plate, funneling material charging aperture, material discharging opening with And mill ball, the stirrer paddle group equipped with inclined plate type blade and the spiral blade composition of S types, described on described agitating shaft Inclined plate type blade is installed in parallel on agitating shaft, is arranged on above and below the described spiral blade of S types on agitating shaft;Described inclines Ramp type blade is provided with some through holes for being available for grinding that mill ball passes through in inner cylinder;Described agitating shaft and the spiral blade of S types It is hollow structure.Described grinding inner cylinder bottom is hemispherical.Described ball-milling reaction device is awarded from following two Two patents of power:A kind of mechanical activation reactor .ZL 201420803894.3 for strengthening polysaccharide modified-high polymer;It is horizontal strong Change polysaccharide modified-high polymer stirring ball-milling reaction device .ZL 201210466391.7.
Product after mechanical activation esterification modification, utilizes the activation one of mechanical force in mechanical activation course of reaction Aspect can improve the content of lignocellulosic hydroxyl and phenolic hydroxyl group, on the other hand access carboxyl by esterification, tool There is the ability of very strong Absorptive complex wave and chelates ferric ions, iron ion will not be lost in use.
The lignocellulosic ester group class fenton catalyst obtained present invention also offers the above method is in terms of wastewater treatment Application.
The english abbreviation of sodium alginate is NaAlg, and the english abbreviation of sodium alginate solidification bead is Alg, lignocellulosic The english abbreviation of ester is LCE.
Lignocellulosic ester-sodium alginate, abbreviation LCE-NaAlg, after immobilization have been obtained in the blended liquid of the present invention Obtain lignocellulosic ester/sodium alginate solidification bead abbreviation LCE-Alg.
In the prior art, conventional GPC ball balling-up mechanism is as follows:Sodium alginate (NaAlg) is macromolecular substances, and surface is taken The hydrophilic functional groups such as band carboxyl, are dissolved in after water, stronger hydrogen bond network can be formed between NaAlg and hydrone, is made Strong hydration occurs for NaAlg macromoleculars, causes the gelation of solution.NaAlg solution is instilled into CaCl2In solution, NaAlg Drop is rapidly and Ca2+Reaction is crosslinked, the curing molding under the supporting role of hydrone of the Alg beads after crosslinking.After drying, Hydrone volatilizees, and produces hole.Carried out because cross-linking reaction is ecto-entad, react the most abundant and successively inside on top layer Successively decrease so that Alg bead internal layer hydrones are more.Therefore during drying, the mesh-structured son that dries out of crosslinking Supporting role and collapse, and the small outer surface of ball of dried Alg is close, internal sparse layering, there is larger space.
In the present invention, forming method, the process for obtaining gel ball are different from conventional method, specific as follows:
Lignocellulosic ester (LCE) can form new hydrogen bond network structure during with the mixing of NaAlg solution, make NaAlg is covered in LCE surfaces, and adhesive effect is produced to adjacent LCE, and scattered LCE in the solution assembles in this role. LCE and NaAlg mixed liquor is instilled into CaCl2In solution, because LCE is insoluble, and wrapped up by NaAlg molecules, therefore mainly By NaAlg and Ca2+Reaction is crosslinked, while the curing molding under hydrone and LCE supporting role.And LCE addition, The mesh of crosslinking can be made to diminish, and low-moisture gasification temperature can effectively drop in LCE and NaAlg interaction, dry During, beneficial to the volatilization of hydrone, and then produce small hole.Further, since LCE supporting role, the LCE- after solidification Alg beads can't be deformed upon because son is dried out, and can keep good spherical structure and mechanical strength.
The present invention has the beneficial effect that:
1st, there are the functional groups such as substantial amounts of hydroxyl, phenolic hydroxyl group, carboxyl on products obtained therefrom surface, with catalysis, active oxidation agent Function;The organic matter in waste water can be adsorbed in these functional groups, oxidative degradation is carried out in catalyst surface, effectively increase Degradation effect;
2nd, the iron ion/ferrous ion loaded in product can produce Fenton effect, and with organic official of lignocellulosic ester It can roll into a ball and produce synergy, energy catalytic oxidant produces the hydroxyl radical free radical or peroxy radical of strong oxidizing property, the organic dirt of acceleration Contaminate the degraded of thing;
3rd, prepared interiors of products is loose structure, and specific surface area and pore capacities are big, and specific surface area is 3~5m2/ g, Absorption pore volume is 6~10cm3/ mg, the specific surface area than the lignocellulosic ester of not balling-up improves more than 50%, can be more effective The useless Organic substance in water of absorption carries out oxidative degradation;
4th, sodium alginate has substantial amounts of carboxylic group, is acted synergistically with lignocellulosic ester, iron ion formation, improves catalysis Efficiency;
5th, product is free of heavy metal, is not in the secondary pollution of leaching ability of heavy metal institute band, applied to catalysis organic wastewater Oxidative degradation can be carried out at ambient pressure, it is only necessary to the oxidative degradation device with stirring, easy to operate.Particularly apply existing Original handling process is varied without during Waste Water Treatment, can directly be applied;
6th, the high mechanical strength of this product, reusable more than 10 times;
7th, turned waste into wealth with cellulosic solid waste etc. for raw material, the treatment of wastes with processes of wastes against one another, realize cellulosic solid waste recycling, Higher value application.
Embodiment
With reference to specific embodiment, the present invention is expanded on further.It should be understood that these embodiments are merely to illustrate the present invention Rather than limitation the scope of the present invention.In addition, it is to be understood that after the content of the invention lectured has been read, people in the art Member can various modifications may be made or changes to the present invention, and these equivalent form of values equally fall within the application appended claims and limited Scope.
Following examples 1-11 be different condition under prepare catalyst
Embodiment 1
A kind of preparation method of lignocellulosic ester/sodium alginate complex spherical class fenton catalyst, the preparation method bag Include following steps:
(1) pretreatment of raw material:Bagasse fibre matter solid waste drying to water content is less than 5%, crushing and obtained 40 mesh The cellulosic solid waste powder of sieve;
(2) mixed at high speed:By cellulosic solid waste powder, esterifying agent (citric acid) and ferrous salt (FeSO4) press 100: 20:5 ratio is added to mixer and is well mixed, and obtains mixture;
(3) mechanical activation solid phase reaction:By said mixture and grinding media heap volume according to 100g:400mL ratio adds Enter in mechanical activation solid phase reactor, carry out ball-milling reaction at a temperature of rotating speed is 500rpm and 50 DEG C of water bath with thermostatic control, reach After the 1.0h reaction time, stop stirring, separation esterification products and abrading-ball, obtain lignocellulosic ester admixture;
(4) curing molding:Lignocellulosic ester admixture is added to the alginic acid of mass concentration 1% under conditions of stirring (mass ratio of lignocellulosic ester admixture and sodium alginate is 4 in sodium solution:1) blended liquid, is obtained, blended liquid instills quality The CaCl of concentration 3%2In solution, crosslinking curing 2h, gel ball freeze-drying obtains specific surface area 4.6156m2/ g, absorption pore volume 9.135cm3/ mg lignocellulosic ester/sodium alginate composite catalyst.
Embodiment 2
A kind of preparation method of lignocellulosic ester/sodium alginate complex spherical class fenton catalyst, the preparation method bag Include following steps:
(1) pretreatment of raw material:Manioc waste cellulosic solid waste drying to water content is less than 8%, crushing and obtained 20 mesh The cellulosic solid waste powder of sieve;
(2) mixed at high speed:By cellulosic solid waste powder, esterifying agent (butanedioic acid) and ferrous salt (FeCl2) press 100: 15:1 ratio is added to mixer and is well mixed, and obtains mixture;
(3) mechanical activation solid phase reaction:By said mixture and grinding media heap volume according to 100g:250mL ratio adds Enter in mechanical activation solid phase reactor, carry out ball-milling reaction at a temperature of rotating speed is 450rpm and 40 DEG C of water bath with thermostatic control, reach After the 1.5h reaction time, stop stirring, separation esterification products and abrading-ball, obtain lignocellulosic ester admixture;
(4) curing molding:Lignocellulosic ester admixture is added to the alginic acid of mass concentration 2% under conditions of stirring (mass ratio of lignocellulosic ester admixture and sodium alginate is 6 in sodium solution:1) blended liquid, is obtained, blended liquid instills quality The CaCl of concentration 5%2In solution, crosslinking curing 10h, gel ball freeze-drying obtains specific surface area 4.0273m2/ g, adsorption hole Hold 8.026cm3/ mg lignocellulosic ester/sodium alginate composite catalyst.
Embodiment 3
A kind of preparation method of lignocellulosic ester/sodium alginate complex spherical class fenton catalyst, the preparation method bag Include following steps:
(1) pretreatment of raw material:Ramulus mori cellulosic solid waste drying to water content is less than 15%, crushing and obtained 30 mesh sieves Cellulosic solid waste powder;
(2) mixed at high speed:By cellulosic solid waste powder, esterifying agent (maleic acid) and ferrous salt (Fe (NO3)2) press 100: 10:2 ratio is added to mixer and is well mixed, and obtains mixture;
(3) mechanical activation solid phase reaction:By said mixture and grinding media heap volume according to 100g:200mL ratio adds Enter in mechanical activation solid phase reactor, carry out ball-milling reaction at a temperature of rotating speed is 400rpm and 30 DEG C of water bath with thermostatic control, reach After the 1.2h reaction time, stop stirring, separation esterification products and abrading-ball, obtain lignocellulosic ester admixture;
(4) curing molding:Lignocellulosic ester admixture is added to the alginic acid of mass concentration 5% under conditions of stirring (mass ratio of lignocellulosic ester admixture and sodium alginate is 8 in sodium solution:1) blended liquid, is obtained, blended liquid instills quality The CaCl of concentration 4%2In solution, crosslinking curing 6h, gel ball freeze-drying obtains specific surface area 3.8674m2/ g, absorption pore volume 7.633cm3/ mg lignocellulosic ester/sodium alginate composite catalyst.
Embodiment 4
A kind of preparation method of lignocellulosic ester/sodium alginate complex spherical class fenton catalyst, the preparation method bag Include following steps:
(1) pretreatment of raw material:Cassava grain stillage cellulosic solid waste drying to water content is less than 8%, crushing and obtained 45 The cellulosic solid waste powder of mesh sieve;
(2) mixed at high speed:By cellulosic solid waste powder, esterifying agent (butene dioic acid) and molysite (Fe (NO3)3) press 100: 5:2 ratio is added to mixer and is well mixed, and obtains mixture;
(3) mechanical activation solid phase reaction:By said mixture and grinding media heap volume according to 100g:500mL ratio adds Enter in mechanical activation solid phase reactor, carry out ball-milling reaction at a temperature of rotating speed is 200rpm and 60 DEG C of water bath with thermostatic control, reach After the 0.8h reaction time, stop stirring, separation esterification products and abrading-ball, obtain lignocellulosic ester admixture;
(4) curing molding:Lignocellulosic ester admixture is added to the alginic acid of mass concentration 3% under conditions of stirring (mass ratio of lignocellulosic ester admixture and sodium alginate is 5 in sodium solution:1) blended liquid, is obtained, blended liquid instills quality The CaCl of concentration 6%2In solution, crosslinking curing 11h, gel ball vacuum dehydrating at lower temperature obtains specific surface area 3.1827m2/ g, suction Attached pore volume 6.356cm3/ mg lignocellulosic ester/sodium alginate composite catalyst.
Embodiment 5
A kind of preparation method of lignocellulosic ester/sodium alginate complex spherical class fenton catalyst, the preparation method bag Include following steps:
(1) pretreatment of raw material:Cassava stalk cellulosic solid waste drying to water content is less than 10%, crushing and obtained 25 mesh The cellulosic solid waste powder of sieve;
(2) mixed at high speed:By cellulosic solid waste powder, esterifying agent (glutaconate, malic acid are mixed) and molysite (Fe2 (SO4)3) press 100:25:8 ratio is added to mixer and is well mixed, and obtains mixture;
(3) mechanical activation solid phase reaction:By said mixture and grinding media heap volume according to 100g:400mL ratio adds Enter in mechanical activation solid phase reactor, carry out ball-milling reaction at a temperature of rotating speed is 500rpm and 50 DEG C of water bath with thermostatic control, reach After the 0.8h reaction time, stop stirring, separation esterification products and abrading-ball, obtain lignocellulosic ester admixture;
(4) curing molding:Lignocellulosic ester admixture is added to the alginic acid of mass concentration 5% under conditions of stirring (mass ratio of lignocellulosic ester admixture and sodium alginate is 7 in sodium solution:1) blended liquid, is obtained, blended liquid instills quality The CaCl of concentration 4%2In solution, crosslinking curing 9h, gel ball vacuum dehydrating at lower temperature obtains specific surface area 3.4465m2/ g, absorption Pore volume 7.013cm3/ mg lignocellulosic ester/sodium alginate composite catalyst.
Embodiment 6
A kind of preparation method of lignocellulosic ester/sodium alginate complex spherical class fenton catalyst, the preparation method bag Include following steps:
(1) pretreatment of raw material:Wood chip rod fibers matter solid waste drying to water content is less than 7%, crushing and obtained 50 mesh The cellulosic solid waste powder of sieve;
(2) mixed at high speed:By cellulosic solid waste powder, esterifying agent (amino acid, citric acid are mixed) and molysite (FeCl3) By 100:8:3 ratio is added to mixer and is well mixed, and obtains mixture;
(3) mechanical activation solid phase reaction:By said mixture and grinding media heap volume according to 100g:600mL ratio adds Enter in mechanical activation solid phase reactor, carry out ball-milling reaction at a temperature of rotating speed is 450rpm and 35 DEG C of water bath with thermostatic control, reach After the 0.5h reaction time, stop stirring, separation esterification products and abrading-ball, obtain lignocellulosic ester admixture;
(4) curing molding:Lignocellulosic ester admixture is added to the alginic acid of mass concentration 2% under conditions of stirring (mass ratio of lignocellulosic ester admixture and sodium alginate is 5 in sodium solution:1) blended liquid, is obtained, blended liquid instills quality The CaCl of concentration 5%2In solution, crosslinking curing 11h, gel ball vacuum dehydrating at lower temperature obtains specific surface area 3.2524m2/ g, suction Attached pore volume 6.832cm3/ mg lignocellulosic ester/sodium alginate composite catalyst.
Embodiment 7
A kind of preparation method of lignocellulosic ester/sodium alginate complex spherical class fenton catalyst, the preparation method bag Include following steps:
(1) pretreatment of raw material:Bamboo scraps rod fibers matter solid waste drying to water content is less than 12%, crushing and obtained 35 mesh The cellulosic solid waste powder of sieve;
(2) mixed at high speed:By cellulosic solid waste powder, esterifying agent (suberic acid, malonic acid, maleic acid are mixed) and ferrous iron Salt (FeCl2、Fe(NO3)2Mixing) press 100:30:6 ratio is added to mixer and is well mixed, and obtains mixture;
(3) mechanical activation solid phase reaction:By said mixture and grinding media heap volume according to 100g:450mL ratio adds Enter in mechanical activation solid phase reactor, carry out ball-milling reaction at a temperature of rotating speed is 400rpm and 40 DEG C of water bath with thermostatic control, reach After the 1.0h reaction time, stop stirring, separation esterification products and abrading-ball, obtain lignocellulosic ester admixture;
(4) curing molding:Lignocellulosic ester admixture is added to the alginic acid of mass concentration 4% under conditions of stirring (mass ratio of lignocellulosic ester admixture and sodium alginate is 7 in sodium solution:1) blended liquid, is obtained, blended liquid instills quality The CaCl of concentration 4%2In solution, crosslinking curing 7h, gel ball vacuum dehydrating at lower temperature obtains specific surface area 4.8546m2/ g, absorption Pore volume 9.695cm3/ mg lignocellulosic ester/sodium alginate composite catalyst.
Embodiment 8
A kind of preparation method of lignocellulosic ester/sodium alginate complex spherical class fenton catalyst, the preparation method bag Include following steps:
(1) pretreatment of raw material:Straw fiber matter solid waste drying to water content is less than 10%, crushing and obtained 40 mesh sieves Cellulosic solid waste powder;
(2) mixed at high speed:By cellulosic solid waste powder, esterifying agent (glutaric acid, glutaconate are mixed) and molysite (FeCl3、Fe(NO3)3、Fe2(SO4)3Mixing) press 100:22:7 ratio is added to mixer and is well mixed, and obtains mixture;
(3) mechanical activation solid phase reaction:By said mixture and grinding media heap volume according to 100g:400mL ratio adds Enter in mechanical activation solid phase reactor, carry out ball-milling reaction at a temperature of rotating speed is 350rpm and 55 DEG C of water bath with thermostatic control, reach After the 1.3h reaction time, stop stirring, separation esterification products and abrading-ball, obtain lignocellulosic ester admixture;
(4) curing molding:Lignocellulosic ester admixture is added to the alginic acid of mass concentration 3% under conditions of stirring (mass ratio of lignocellulosic ester admixture and sodium alginate is 5 in sodium solution:1) blended liquid, is obtained, blended liquid instills quality The CaCl of concentration 3%2In solution, crosslinking curing 10h, gel ball vacuum and low temperature oil bath is dehydrated, and obtains specific surface area 4.4238m2/ g, absorption pore volume 9.015cm3/ mg lignocellulosic ester/sodium alginate composite catalyst.
Embodiment 9
A kind of preparation method of lignocellulosic ester/sodium alginate complex spherical class fenton catalyst, the preparation method bag Include following steps:
(1) pretreatment of raw material:By bagasse, cassava grain stillage mix the drying of cellulosic solid waste to water content be less than 8%, Crush the cellulosic solid waste powder for obtaining 30 mesh sieves;
(2) mixed at high speed:By cellulosic solid waste powder, esterifying agent (adipic acid, pimelic acid, maleic acid are mixed) and molysite (Fe(NO3)3、Fe2(SO4)3Mixing) press 100:16:5 ratio is added to mixer and is well mixed, and obtains mixture;
(3) mechanical activation solid phase reaction:By said mixture and grinding media heap volume according to 100g:350mL ratio adds Enter in mechanical activation solid phase reactor, carry out ball-milling reaction at a temperature of rotating speed is 400rpm and 50 DEG C of water bath with thermostatic control, reach After the 1.5h reaction time, stop stirring, separation esterification products and abrading-ball, obtain lignocellulosic ester admixture;
(4) curing molding:Lignocellulosic ester admixture is added to the alginic acid of mass concentration 4% under conditions of stirring (mass ratio of lignocellulosic ester admixture and sodium alginate is 6 in sodium solution:1) blended liquid, is obtained, blended liquid instills quality The CaCl of concentration 4%2In solution, crosslinking curing 5h, gel ball vacuum and low temperature oil bath is dehydrated, and obtains specific surface area 4.8236m2/ g, absorption pore volume 9.704cm3/ mg lignocellulosic ester/sodium alginate composite catalyst.
Embodiment 10
A kind of preparation method of lignocellulosic ester/sodium alginate complex spherical class fenton catalyst, the preparation method bag Include following steps:
(1) pretreatment of raw material:The cellulosic solid waste drying that wood chip, bamboo scraps, stalk are mixed is to water content 10%, powder The broken cellulosic solid waste powder for obtaining 35 mesh sieves;
(2) mixed at high speed:By cellulosic solid waste powder, esterifying agent (oxalic acid, malonic acid, amino acid, citric acid are mixed) And ferrous salt (Fe (NO3)2、Fe2(SO4)2Mixing) press 100:13:3 ratio is added to mixer and is well mixed, and is mixed Thing;
(3) mechanical activation solid phase reaction:By said mixture and grinding media heap volume according to 100g:500mL ratio adds Enter in mechanical activation solid phase reactor, carry out ball-milling reaction at a temperature of rotating speed is 500rpm and 40 DEG C of water bath with thermostatic control, reach After the 0.6h reaction time, stop stirring, separation esterification products and abrading-ball, obtain lignocellulosic ester admixture;
(4) curing molding:Lignocellulosic ester admixture is added to the alginic acid of mass concentration 2% under conditions of stirring (mass ratio of lignocellulosic ester admixture and sodium alginate is 5 in sodium solution:1) blended liquid, is obtained, blended liquid instills quality The CaCl of concentration 3%2In solution, crosslinking curing 12h, gel ball vacuum dehydrating at lower temperature obtains specific surface area 4.3783m2/ g, suction Attached pore volume 8.521cm3/ mg lignocellulosic ester/sodium alginate composite catalyst.
Embodiment 11
A kind of preparation method of lignocellulosic ester/sodium alginate complex spherical class fenton catalyst, the preparation method bag Include following steps:
(1) pretreatment of raw material:The cellulosic solid waste drying that bagasse, stalk, ramulus mori are mixed is to water content 10%, powder The broken cellulosic solid waste powder for obtaining 40 mesh sieves;
(2) mixed at high speed:By cellulosic solid waste powder, esterifying agent, (adipic acid, butene dioic acid, amino acid, malic acid are mixed Close) and molysite (Fe (NO3)3、Fe2(SO4)3Mixing) press 100:25:7 ratio is added to mixer and is well mixed, and is mixed Thing;
(3) mechanical activation solid phase reaction:By said mixture and grinding media heap volume according to 100g:350mL ratio adds Enter in mechanical activation solid phase reactor, carry out ball-milling reaction at a temperature of rotating speed is 550rpm and 35 DEG C of water bath with thermostatic control, reach After the 1.3h reaction time, stop stirring, separation esterification products and abrading-ball, obtain lignocellulosic ester admixture;
(4) curing molding:Lignocellulosic ester admixture is added to the alginic acid of mass concentration 3% under conditions of stirring (mass ratio of lignocellulosic ester admixture and sodium alginate is 6 in sodium solution:1) blended liquid, is obtained, blended liquid instills quality The CaCl of concentration 4%2In solution, crosslinking curing 10h, gel ball vacuum and low temperature oil bath is dehydrated, and obtains specific surface area 4.4254m2/ g, absorption pore volume 8.639cm3/ mg lignocellulosic ester/sodium alginate composite catalyst.
Above-mentioned catalyst is applied to the experimental verification of various wastewater treatments
Embodiment 12
Application of the lignocellulosic ester/sodium alginate complex spherical class fenton catalyst in catalytic oxidation treatment paper waste
Lignocellulosic ester/sea prepared by embodiment 1 is added in initial COD concentration is 3500mg/L paper waste The quality that mosanom complex spherical class fenton catalyst and oxidant (hydrogen peroxide), catalyst and oxidant are added is respectively waste water The 1.0% of quality and 2.5%, it is that 9.0, reaction temperature is to occur redox reaction, reaction time under the conditions of 30 DEG C in pH value 90min, COD clearance reach 96%, and colourity removal efficiency reaches 94%.Catalyst is repeatable to be utilized 12 times.
Embodiment 13
Lignocellulosic ester/sodium alginate complex spherical class fenton catalyst is in catalytic oxidation treatment azo dyeing waste water Using
Lignocellulosic ester/sea prepared by embodiment 5 is added in initial concentration is 180mg/L azo dyeing waste water The quality that mosanom complex spherical class fenton catalyst and oxidant (hydrogen peroxide), catalyst and oxidant are added is respectively waste water The 0.5% of quality and 2.0%, it is that 7.0, reaction temperature is to occur redox reaction, reaction time under the conditions of 45 DEG C in pH value 60min, Dye Wastewater Decolorization removal efficiency reaches more than 99%, and dyestuff is mineralized as CO2、H2O、N2Etc. harmless small-molecule substance, mineralization rate Reach more than 93%.Catalyst is repeatable to be utilized 21 times.
Embodiment 14
Lignocellulosic ester/sodium alginate complex spherical class fenton catalyst is in catalytic oxidation treatment hydroquinones Industry Waste The application of water
The lignocellulosic prepared by embodiment 8 is added in initial concentration is 200mg/L hydroquinones industrial wastewater The quality difference that ester/sodium alginate complex spherical class fenton catalyst and oxidant (hydrogen peroxide), catalyst and oxidant are added 0.8% for wastewater quality and 1.5%, is that 4.0, reaction temperature is to occur redox reaction under the conditions of 60 DEG C in pH value, instead 120min between seasonable, hydroquinones is mineralized as CO2And H2O, mineralization rate reaches more than 90%.Catalyst is repeatable to be utilized 17 times.
Above-described embodiment 12-14 has excellent treatment effect to various waste water, repeats utilization rate high, it is contemplated that It is that other target products in embodiment 1-11 are all effective to various wastewater treatments, and the present invention is not just repeated one by one.
In addition, the mechanical strength on product of the present invention, applicant takes qualitative analysis, succinctly it is described as follows:Arbitrarily The close sample of 5 particle diameters is chosen, places it between two pieces of smooth glass plates, counterweight is added on a glass, is passed through Observe the deformed condition of immobilized spherule, the mechanical strength of qualitative analysis adsorbing sphere.
By comparing under target product bead and other products on the market, equivalent weight counterweight, the deformation of product of the present invention It is significantly less than like product, this also provides guarantee for the reuse of target product.

Claims (10)

1. the preparation method of lignocellulosic ester/sodium alginate complex spherical class fenton catalyst, it is characterised in that including as follows Step:
Cellulosic solid waste is dried, crushed, and obtains cellulosic solid waste powder;
Cellulosic solid waste powder, esterifying agent, molysite and/or ferrous salt, are well mixed, obtain mixture;
Mixture is added in mechanical activation solid phase reactor, and ball milling simultaneously carries out esterification, separation esterification products and abrading-ball, is obtained Lignocellulosic ester admixture;
Lignocellulosic ester admixture is added in sodium alginate soln under conditions of stirring, obtains blended liquid;
Blended liquid is instilled in calcium chloride solution, crosslinking curing, filtering, and gel ball solidified, load iron is dried, produced Target product lignocellulosic ester/sodium alginate complex spherical class fenton catalyst.
2. preparation method according to claim 1, it is characterised in that cellulosic solid waste powder:Esterifying agent:Molysite and/ Or ferrous salt=100:5-30:1-8, mass ratio.
3. according to any described preparation methods of claim 1-2, it is characterised in that lignocellulosic ester admixture and alginic acid The mass ratio of sodium is 4-8:1, the mass concentration of sodium alginate soln is 1-5%.
4. preparation method according to claim 3, it is characterised in that the esterifying agent includes oxalic acid, malonic acid, amber Acid, glutaric acid, adipic acid, pimelic acid, suberic acid, maleic acid, butene dioic acid, glutaconate, malic acid, amino acid, citric acid Any of or two or more combinations.
5. preparation method according to claim 3, it is characterised in that the molysite is FeCl3、Fe(NO3)3、Fe2(SO4)3 Any of or two or more combinations, the ferrous salt be FeCl2、Fe(NO3)2、FeSO4Any of or two kinds with On combination.
6. the preparation method according to claim 4 or 5, it is characterised in that the mass concentration of calcium chloride solution is 3-6%, The time of crosslinking curing is 2-12 hours, and the drying means of gel ball can be low using vacuum dehydrating at lower temperature, freeze-drying, vacuum Warm oil bath any of is dehydrated.
7. according to any described preparation methods of claim 1-2, it is characterised in that mixture and grinding media heap volume according to 100g:200-600mL ratio is added in mechanical activation solid phase reactor, is 200-600rpm and 30-60 DEG C of constant temperature in rotating speed Under the conditions of carry out ball-milling reaction, after reaction 0.5-1.5h, stop heating and stir, separation product and abrading-ball obtain wood fibre Plain ester admixture.
8. preparation method according to claim 1, it is characterised in that described cellulosic solid waste is bagasse, cassava Vinasse, Cassava stalk, wood chip, bamboo scraps, stalk, ramulus mori any one or two or more combinations.
9. preparation method according to claim 8, it is characterised in that cellulosic solid waste is dried, the requirement of crushing is:Contain Water is less than 15%, is crushed to 20-60 mesh.
10. the lignocellulosic ester that the preparation method as described in claim 1-9 is any is obtained/sodium alginate complex spherical class is fragrant The application of catalyst in the treatment of waste water.
CN201710498150.3A 2017-06-27 2017-06-27 Lignocellulosic ester/sodium alginate complex spherical class fenton catalyst preparation method and applications Active CN107321384B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201710498150.3A CN107321384B (en) 2017-06-27 2017-06-27 Lignocellulosic ester/sodium alginate complex spherical class fenton catalyst preparation method and applications

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201710498150.3A CN107321384B (en) 2017-06-27 2017-06-27 Lignocellulosic ester/sodium alginate complex spherical class fenton catalyst preparation method and applications

Publications (2)

Publication Number Publication Date
CN107321384A true CN107321384A (en) 2017-11-07
CN107321384B CN107321384B (en) 2019-10-01

Family

ID=60197591

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201710498150.3A Active CN107321384B (en) 2017-06-27 2017-06-27 Lignocellulosic ester/sodium alginate complex spherical class fenton catalyst preparation method and applications

Country Status (1)

Country Link
CN (1) CN107321384B (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110615518A (en) * 2019-05-07 2019-12-27 中冶华天工程技术有限公司 Fenton reaction ferrous iron slow release granule
CN111204896A (en) * 2020-01-15 2020-05-29 国网山东省电力公司电力科学研究院 Desulfurization wastewater pretreatment process based on flocculation-Fenton-like coupling method and activating agent
CN111233225A (en) * 2020-01-16 2020-06-05 深圳市蓝清环境科技工程有限公司 UV-FENTON wastewater treatment process

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2014099441A1 (en) * 2012-12-18 2014-06-26 E.I. Du Pont De Nemours And Company Method for enhanced recovery of oil from oil reservoirs
CN104646062A (en) * 2015-02-12 2015-05-27 浙江理工大学 Preparation method for bamboo pulp cellulose-based integrated Fenton catalyst Fe<3+>C2O4/R
CN105399963A (en) * 2015-12-17 2016-03-16 广西大学 Mechanical-activation solid-phase preparation method of lignocellulose ester group oxidation catalyst

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2014099441A1 (en) * 2012-12-18 2014-06-26 E.I. Du Pont De Nemours And Company Method for enhanced recovery of oil from oil reservoirs
CN104646062A (en) * 2015-02-12 2015-05-27 浙江理工大学 Preparation method for bamboo pulp cellulose-based integrated Fenton catalyst Fe<3+>C2O4/R
CN105399963A (en) * 2015-12-17 2016-03-16 广西大学 Mechanical-activation solid-phase preparation method of lignocellulose ester group oxidation catalyst

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110615518A (en) * 2019-05-07 2019-12-27 中冶华天工程技术有限公司 Fenton reaction ferrous iron slow release granule
CN110615518B (en) * 2019-05-07 2022-05-24 中冶华天工程技术有限公司 Fenton reaction ferrous iron slow release granule
CN111204896A (en) * 2020-01-15 2020-05-29 国网山东省电力公司电力科学研究院 Desulfurization wastewater pretreatment process based on flocculation-Fenton-like coupling method and activating agent
CN111233225A (en) * 2020-01-16 2020-06-05 深圳市蓝清环境科技工程有限公司 UV-FENTON wastewater treatment process
CN111233225B (en) * 2020-01-16 2022-03-08 深圳市蓝清环境科技工程有限公司 UV-FENTON wastewater treatment process

Also Published As

Publication number Publication date
CN107321384B (en) 2019-10-01

Similar Documents

Publication Publication Date Title
CN107233916B (en) Carry the preparation method and applications of the cellulose ester-based spheric catalyst of hophornbeam matter
Asgher Biosorption of reactive dyes: a review
CN107213916B (en) The preparation method and applications of modified wood fibre element ester group class fenton catalyst
Peighambardoust et al. Decoration of Citrus limon wood carbon with Fe3O4 to enhanced Cd2+ removal: a reclaimable and magnetic nanocomposite
Kwak et al. Surface-modified spherical lignin particles with superior Cr (VI) removal efficiency
Asgher et al. Evaluation of thermodynamics and effect of chemical treatments on sorption potential of Citrus waste biomass for removal of anionic dyes from aqueous solutions
Othmani et al. Biochar and activated carbon derivatives of lignocellulosic fibers towards adsorptive removal of pollutants from aqueous systems: Critical study and future insight
Nayagam et al. Utilization of shell-based agricultural waste adsorbents for removing dyes: A review
Ladnorg et al. Alginate-like exopolysaccharide extracted from aerobic granular sludge as biosorbent for methylene blue: Thermodynamic, kinetic and isotherm studies
El-Sayed et al. Assessment of food processing and pharmaceutical industrial wastes as potential biosorbents: a review
CN101298038B (en) Gel adsorbing agent for wastewater treatment
CN107321384B (en) Lignocellulosic ester/sodium alginate complex spherical class fenton catalyst preparation method and applications
Gokulan et al. Experimental and chemometric analysis of bioremediation of remazol dyes using biochar derived from green seaweeds
CN102531237B (en) Method for treating money-printing wastewater with combination of modified bentonite and photo-Fenton method
Al-Ajji et al. Novel insights into the nanoadsorption mechanisms of crystal violet using nano-hazelnut shell from aqueous solution
CN105399963B (en) A kind of mechanical activation method for preparing solid phase of lignocellulosic ester group oxidation catalyst
Ahmad et al. Microwave-assisted hydrothermal treatment of soybean residue and chitosan: Characterization of hydrochars and role of N and P transformation for Pb (II) removal
Prasanna A novel adsorption process for the removal of salt and dye from saline textile industrial wastewater using a three-stage reactor with surface modified adsorbents
Türk et al. Removal of basic yellow 51 dye by using ion exchange resin obtained by modification of byproduct sugar beet pulp
Luan et al. Facile and sustainable modification for improving the adsorption ability of sugarcane bagasse towards cationic organic pollutants
Bavi et al. Batch and continuous mode adsorption of methylene blue cationic dye onto synthesized titanium dioxide/polyurethane nanocomposite modified by sodium dodecyl sulfate
Oliveira et al. Chitosan-based magnetic bioadsorbent beads from eucalyptus sawdust waste for the Direct Violet-51 dye remediation: Eco-friendly strategy and statistical optimization
CN105692845B (en) A kind of preparation method of the natural coagulant of pomelo peel
Jia et al. Multidimensional decipherment of interactions in invert sugar–amino acid co-degradation colorants (IACDCs) capture by polyamine co-modified shaddock peel cellulose/graphene oxide aerogel
CN111996008B (en) Method for immobilizing humic acid on surface of shell natural material

Legal Events

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