CN106179196A - A kind of petrochemical wastewater process adsorbent and preparation method thereof - Google Patents
A kind of petrochemical wastewater process adsorbent and preparation method thereof Download PDFInfo
- Publication number
- CN106179196A CN106179196A CN201610555322.1A CN201610555322A CN106179196A CN 106179196 A CN106179196 A CN 106179196A CN 201610555322 A CN201610555322 A CN 201610555322A CN 106179196 A CN106179196 A CN 106179196A
- Authority
- CN
- China
- Prior art keywords
- preparation
- adsorbent
- modified
- rectorite
- meerschaum
- 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
Links
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/22—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
- B01J20/26—Synthetic macromolecular compounds
- B01J20/265—Synthetic macromolecular compounds modified or post-treated polymers
- B01J20/267—Cross-linked polymers
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/28—Treatment of water, waste water, or sewage by sorption
- C02F1/281—Treatment of water, waste water, or sewage by sorption using inorganic sorbents
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/02—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
- B01J20/10—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising silica or silicate
- B01J20/16—Alumino-silicates
- B01J20/165—Natural alumino-silicates, e.g. zeolites
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/02—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
- B01J20/0203—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising compounds of metals not provided for in B01J20/04
- B01J20/0225—Compounds of Fe, Ru, Os, Co, Rh, Ir, Ni, Pd, Pt
- B01J20/0229—Compounds of Fe
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/02—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
- B01J20/10—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising silica or silicate
- B01J20/12—Naturally occurring clays or bleaching earth
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/22—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/22—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
- B01J20/24—Naturally occurring macromolecular compounds, e.g. humic acids or their derivatives
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/22—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
- B01J20/26—Synthetic macromolecular compounds
- B01J20/264—Synthetic macromolecular compounds derived from different types of monomers, e.g. linear or branched copolymers, block copolymers, graft copolymers
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/28—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties
- B01J20/28002—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties characterised by their physical properties
- B01J20/28009—Magnetic properties
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/28—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties
- B01J20/28014—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties characterised by their form
- B01J20/28016—Particle form
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/28—Treatment of water, waste water, or sewage by sorption
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/28—Treatment of water, waste water, or sewage by sorption
- C02F1/285—Treatment of water, waste water, or sewage by sorption using synthetic organic sorbents
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/28—Treatment of water, waste water, or sewage by sorption
- C02F1/286—Treatment of water, waste water, or sewage by sorption using natural organic sorbents or derivatives thereof
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J2220/00—Aspects relating to sorbent materials
- B01J2220/40—Aspects relating to the composition of sorbent or filter aid materials
- B01J2220/48—Sorbents characterised by the starting material used for their preparation
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/34—Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32
- C02F2103/36—Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32 from the manufacture of organic compounds
- C02F2103/365—Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32 from the manufacture of organic compounds from petrochemical industry (e.g. refineries)
Landscapes
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Analytical Chemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Life Sciences & Earth Sciences (AREA)
- Engineering & Computer Science (AREA)
- Hydrology & Water Resources (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Inorganic Chemistry (AREA)
- Dispersion Chemistry (AREA)
- Geochemistry & Mineralogy (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
- Water Treatment By Sorption (AREA)
Abstract
The invention provides the preparation method of a kind of petrochemical wastewater process adsorbent, concrete steps include: the preparation of (1) composite granule gel;(2) preparation of modified compound adsorbent;(3) preparation of magnetic coupling crosslinking adsorbent;Adsorbent of the present invention be by property of modified rectorite and modified meerschaum carry out compound based on adsorbent material, wherein, rectorite and meerschaum introduce organic group on its surface after being modified, its surface nature of extreme enrichment, improve its absorption property;And rectorite and meerschaum are used in combination, playing respective strong point, synergism, the alternative organic and inorganic pollution adsorbing variety classes different with molecular size also substantially increases its absorption property, is greatly expanded its range of application;It addition, adsorbent of the present invention is owing to having magnetic, after absorption, described adsorbent thoroughly can reclaim under interior magnetic field at 20 minutes, it is not necessary to filters, settle, the extra process such as be centrifuged.
Description
Technical field
The invention belongs to technical field of waste water processing, be specifically related to a kind of petrochemical wastewater process adsorbent and system thereof
Preparation Method.
Background technology
Along with expanding economy, the chemical plant of various places gets more and more, the focus being treated as all circles' concern of trade effluent,
Traditional plating, process hides, Treatment of Metal Surface, printing and dyeing, petrochemical industry and the wastewater discharge containing other organic pollutions increase day by day
Add.
Petrochemical industry is the important component part of chemical industry, plays an important role in the development of national economy, is China
One of pillar industry department.Petrochemical industry refers to oil and natural gas as raw material, produces oil product and petrochemicals
Processing industry.Oil product also known as oil product, mainly include various fuel oil (gasoline, kerosene, diesel oil etc.) and lubricating oil and
Liquefied petroleum gas, oil coke, paraffin, Colophonium etc..The course of processing producing these products is commonly referred to as petroleum refining, is called for short refining
Oil.The further chemical process of raw oil that petrochemicals provide with oil refining process obtains.Produce the of petrochemicals
One step is that gentle to raw oil (such as propane, gasoline, diesel oil etc.) crack, and generates with ethylene, propylene, butadiene, benzene, first
Benzene, dimethylbenzene are the basic chemical raw materials of representative.Second step is to produce multiple Organic Chemicals (about with basic chemical raw materials
200 kinds) and synthetic material (plastics, synthetic fibers, synthetic rubber).The production of this two steps product belongs to the scope of petrochemical industry.
Organic Chemicals continues processing can prepare the chemical products of more multi items, is not belonging to the scope of petrochemical industry traditionally.Having
In a little data, with natural gas, light gasoline, heavy oil for Material synthesis ammonia, carbamide, even produce nitric acid and also list petrochemical industry in.Existing
Its thorough process can not just be discharged it by some petrochemical wastewaters when processing, and causes the pollution of environment, waste resource
Pollute environment simultaneously.
Adsorption treatment technology is the technology of a kind of simple and effective process waste water, containing heavy metal ion industrial wastewater, dye
The process of material waste water, petrochemical wastewater etc. is widely used.At present, the active charcoal of Industrial Wastewater Treatment common technology adsorbs, boiling
Stone exchange etc..Activated carbon is because of features such as it are expensive, regeneration is complicated, it is difficult to large-scale use.
Rectorite Mineral Material is natural product, has the good compatibility with environment, is a kind of ring quite having application prospect
Border material, can use as adsorbent.Compared with activated carbon, rectorite has inexpensive, high adsorption capacity, abundance and can be again
The advantages such as natural disposition.Containing bigger water-wetted surface in the crystal structure of rectorite, demonstrate good hydrophilic in aqueous
And high dispersion.In waste water processes and former water burst Pollution reparation is put into practice, organic in order to improve rectorite absorption
Ability, people often use quaternary ammonium salt etc. that it is carried out organic modification, are prepared as organic rectorite.And meerschaum is a kind of rich
Fibrous magnesium silicate clay mineral, has the advantages that bigger specific surface area, adsorptivity are good, and its price is less than conventional work
Property charcoal commercially available price, meerschaum become waste water process study hotspot.But owing to meerschaum adsorption treatment waste water is difficult to back
Receiving, regenerate difficulty, be unfavorable for carrying out industrialization, hinder meerschaum promotes the use of scope.Therefore, meerschaum is used to develop honest and clean
Valency, efficient novel absorption material also are used it for processing industrial wastewater, have important practical significance.
Summary of the invention
It is extensive that the technical problem to be solved is to provide a kind of raw material sources, and preparation technology is simple, adsorption capacity
Height, processing cost is low, it is easy to adsorbent of recovery and preparation method thereof,.
For solving the problems referred to above, the technical solution used in the present invention is:
The preparation method of a kind of petrochemical wastewater process adsorbent, comprises the steps:
(1) preparation of composite granule gel: the modified meerschaum powder body taking 15-30 part property of modified rectorite powder body and 20-40 part divides
Dissipate in the solvent of 100-180 part, and ultrasonic vibration 1-2h at room temperature, then heat to 65-75 DEG C, be slowly added dropwise 20-30
The tetraethyl orthosilicate of part, continues stirring to solution and becomes solid phase;It is solid to mass conservation, at 100-110 DEG C with distilled water wash
It is dried 3-6 hour, obtains composite granule gel;
(2) preparation of modified compound adsorbent: modified composite granule gel step (1) obtained joins the season of 10-15 part
Mixing and stirring in ammonium salt four cohesive surface activating agent, the chitosan of 6-12 part and 50-80 part toluene solvant, then will mixing
Thing transfers in politef hydrothermal reaction kettle hydro-thermal reaction 6-10h at 80-120 DEG C, and reaction end is centrifuged, washes
Wash, dry, i.e. obtain modified compound adsorbent;
(3) preparation of magnetic coupling crosslinking adsorbent: the modified compound adsorbent that step (2) obtains is joined 30-40 part
In mixed molysite solution, at N2Under protection, under the conditions of 40 DEG C, stirring reaction 20-30 min i.e. obtains described petrochemical wastewater
Process adsorbent.
Wherein, in described (2), the preparation method of quaternary ammonium salt four cohesive surface activating agent is: at the 250mL tri-equipped with condensing tube
In mouth flask, adding dehydrated alcohol 40mL, ethylenediamine 4.5g, room temperature carries out magnetic agitation, adds epoxy chloropropionate with 10/min
Alkane 34.7g, 50 DEG C of back flow reaction 4h after dropping, obtain four cohesive surface surfactant intermediate, for faint yellow after decompression distillation
Translucent thick liquid, takes this intermediate 20g, adds dehydrated alcohol and deionized water mixed solution 40mL that volume ratio is 1:l
For solvent, then drip 7.9gN, N-dimethyl dodecyl base tertiary amine, it is warming up to 80 DEG C, reacts 1h, decompression distillation, recrystallization, very
The empty acquisition white powdery solids that is dried is quaternary ammonium salt four cohesive surface activating agent.
The modifying agent that described property of modified rectorite powder body is used is for selected from ten alkyl trimethyl phosphonium bromides, ten alkyl trimethyls
One in phosphorus chloride and cetyl triphenylphosphonium chloride.
The modifying agent that described modified meerschaum powder body is used is for from TEPA, triethylene tetramine, ethylenediamine or second
One in ethylenediamine tetraacetic acid (EDTA).
After adding mixed molysite solution in described step (3), being slowly added dropwise 1-2 part concentration during stirring is 28%
Ammonia, ammonia finishes and is warming up to 40 DEG C again.
Described mixed molysite be mol ratio be the FeSO of 1:1.5-2.54·7H2O and FeC13·6H2The mixture of O.
In described step (1), solvent is in toluene, N,N-dimethylformamide, DMAC N,N' dimethyl acetamide, oxolane
One or more.
The technique effect of the present invention is: (1) adsorbent of the present invention is to be combined with property of modified rectorite and modified meerschaum
Based on adsorbent material, wherein, rectorite and meerschaum be modified after its surface introduce organic group, extreme enrichment
Its surface nature, improves its absorption property;And rectorite and meerschaum are used in combination, play respective strong point, collaborative
Effect, the alternative organic and inorganic pollution adsorbing variety classes different with molecular size also substantially increases its adsorptivity
Can, it is greatly expanded its range of application;It addition, the present invention uses quaternary ammonium salt four cohesive surface activating agent and chitosan torr tired to modification
It is modified that stone and modified meerschaum complex carry out secondary cross-linking so that composite surface inlays the biggest organic of molecular weight further
Group, improves it and replaces performance and absorption property, improve its stability and intensity, enables gained adsorbent to stablize and efficient
Adsorption removal petrochemical wastewater.
(2) method that adsorbent of the present invention uses hydro-thermal reaction when carrying out twice-modified, use the method can be fabulous
The active group of modifying agent is anchored on property of modified rectorite and modified meerschaum complex, and sufficiently stable.
(3) adsorbent of the present invention is owing to having magnetic, and after absorption, described adsorbent can be under 20 minutes interior magnetic fields
Thoroughly reclaim, it is not necessary to filter, settle, the extra process such as be centrifuged.
Detailed description of the invention
Below in conjunction with embodiment, technical scheme is further elaborated:
Embodiment 1
The preparation method of a kind of petrochemical wastewater process adsorbent, comprises the steps:
(1) preparation of composite granule gel: take 15 part of ten alkyl trimethyl phosphonium bromide property of modified rectorite powder body and 20 part of four ethylene
Five amine modified meerschaum powder body are scattered in the toluene of 100 parts, and ultrasonic vibration 1h at room temperature, then heat to 65 DEG C, slow
The tetraethyl orthosilicate of slow dropping 20 parts, continues stirring to solution and becomes solid phase;It is solid to mass conservation with distilled water wash,
100 DEG C are dried 3 hours, obtain composite granule gel;
(2) preparation of modified compound adsorbent: modified composite granule gel step (1) obtained joins the quaternary ammonium salt of 10 parts
Mixing and stirring in four cohesive surface activating agents, the chitosan of 6 parts and 50 parts of toluene solvants, then transfers to gather by mixture
In tetrafluoroethene hydrothermal reaction kettle at 80 DEG C hydro-thermal reaction 6h, reaction end be centrifuged, wash, dry, i.e. obtain modification
Compound adsorbent;
(3) preparation of magnetic coupling crosslinking adsorbent: the modified compound adsorbent that step (2) obtains is joined the mixing of 30 parts
In iron salt solutions, at N2Under protection, being slowly added dropwise 1 part of concentration during stirring is the ammonia of 28%, stirs under the conditions of 40 DEG C
Mix reaction 20 min and i.e. obtain described petrochemical wastewater process adsorbent.
Embodiment 2
The preparation method of a kind of petrochemical wastewater process adsorbent, comprises the steps:
(1) preparation of composite granule gel: take 30 part of ten alkyl trimethyl phosphorus chloride property of modified rectorite powder body and 20-40 part three second
Alkene tetramine modified meerschaum powder body is scattered in the DMF of 180 parts, and ultrasonic vibration 2h at room temperature, then
It is warming up to 75 DEG C, is slowly added dropwise the tetraethyl orthosilicate of 30 parts, continue stirring to solution and become solid phase;It is solid to distilled water wash
Mass conservation, is dried 3 hours at 110 DEG C, obtains composite granule gel;
(2) preparation of modified compound adsorbent: modified composite granule gel step (1) obtained joins the quaternary ammonium salt of 15 parts
Mixing and stirring in four cohesive surface activating agents, the chitosan of 12 parts and 80 parts of toluene solvants, then transfers to mixture
In politef hydrothermal reaction kettle at 120 DEG C hydro-thermal reaction 10h, reaction end be centrifuged, wash, dry, i.e. obtain
Modified compound adsorbent;
(3) preparation of magnetic coupling crosslinking adsorbent: the modified compound adsorbent that step (2) obtains is joined the mixing of 40 parts
In iron salt solutions, at N2Under protection, being slowly added dropwise 2 parts of concentration during stirring is the ammonia of 28%, stirs under the conditions of 40 DEG C
Mix reaction 27 min and i.e. obtain described petrochemical wastewater process adsorbent.
Embodiment 3
The preparation method of a kind of petrochemical wastewater process adsorbent, comprises the steps:
(1) preparation of composite granule gel: take 20 parts of cetyl triphenylphosphonium chloride property of modified rectorite powder body and 30 parts of second two
Amine modified meerschaum powder body is scattered in the N,N-dimethylacetamide of 140 parts, and ultrasonic vibration 1.5h at room temperature, then rises
Temperature, to 70 DEG C, is slowly added dropwise the tetraethyl orthosilicate of 25 parts, continues stirring to solution and becomes solid phase;It is solid to matter with distilled water wash
Measure constant, be dried 5 hours at 105 DEG C, obtain composite granule gel;
(2) preparation of modified compound adsorbent: modified composite granule gel step (1) obtained joins the quaternary ammonium salt of 12 parts
Mixing and stirring in four cohesive surface activating agents, the chitosan of 9 parts and 70 parts of toluene solvants, then transfers to gather by mixture
In tetrafluoroethene hydrothermal reaction kettle at 100 DEG C hydro-thermal reaction 8h, reaction end be centrifuged, wash, dry, i.e. obtain modification
Compound adsorbent;
(3) preparation of magnetic coupling crosslinking adsorbent: the modified compound adsorbent that step (2) obtains is joined the mixing of 35 parts
In iron salt solutions, at N2Under protection, being slowly added dropwise 1.5 parts of concentration during stirring is the ammonia of 28%, under the conditions of 40 DEG C
Stirring reaction 25 min i.e. obtain described petrochemical wastewater process adsorbent.
Embodiment 4
The preparation method of a kind of petrochemical wastewater process adsorbent, comprises the steps:
(1) preparation of composite granule gel: take 25 part of ten alkyl trimethyl phosphonium bromide property of modified rectorite powder body and 35 parts of ethylenediamines
Tetraacetic acid modified meerschaum powder body is scattered in the oxolane of 160 parts, and ultrasonic vibration 1.8h at room temperature, then heats to
70 DEG C, it is slowly added dropwise the tetraethyl orthosilicate of 28 parts, continues stirring to solution and become solid phase;It is solid to quality not with distilled water wash
Become, be dried 5 hours at 110 DEG C, obtain composite granule gel;
(2) preparation of modified compound adsorbent: modified composite granule gel step (1) obtained joins the quaternary ammonium salt of 14 parts
Mixing and stirring in four cohesive surface activating agents, the chitosan of 10 parts and 70 parts of toluene solvants, then transfers to mixture
In politef hydrothermal reaction kettle at 110 DEG C hydro-thermal reaction 9h, reaction end be centrifuged, wash, dry, i.e. changed
Property compound adsorbent;
(3) preparation of magnetic coupling crosslinking adsorbent: the modified compound adsorbent that step (2) obtains is joined the mixing of 38 parts
In iron salt solutions, at N2Under protection, being slowly added dropwise 1.5 parts of concentration during stirring is the ammonia of 28%, under the conditions of 40 DEG C
Stirring reaction 25 min i.e. obtain described petrochemical wastewater process adsorbent.
Embodiment 5
The preparation method of a kind of petrochemical wastewater process adsorbent, comprises the steps:
(1) preparation of composite granule gel: take 18 part of ten alkyl trimethyl phosphorus chloride property of modified rectorite powder body and 25 parts of ethylenediamines
Tetraacetic acid modified meerschaum powder body is scattered in the N,N-dimethylacetamide of 130 parts, and ultrasonic vibration 1h at room temperature, then
It is warming up to 75 DEG C, is slowly added dropwise the tetraethyl orthosilicate of 25 parts, continue stirring to solution and become solid phase;It is solid to distilled water wash
Mass conservation, is dried 4 hours at 105 DEG C, obtains composite granule gel;
(2) preparation of modified compound adsorbent: modified composite granule gel step (1) obtained joins the quaternary ammonium salt of 12 parts
Mixing and stirring in four cohesive surface activating agents, the chitosan of 9 parts and 60 parts of toluene solvants, then transfers to gather by mixture
In tetrafluoroethene hydrothermal reaction kettle at 90 DEG C hydro-thermal reaction 10h, reaction end be centrifuged, wash, dry, i.e. obtain modification
Compound adsorbent;
(3) preparation of magnetic coupling crosslinking adsorbent: the modified compound adsorbent that step (2) obtains is joined the mixing of 33 parts
In iron salt solutions, at N2Under protection, being slowly added dropwise 1.5 parts of concentration during stirring is the ammonia of 28%, under the conditions of 40 DEG C
Stirring reaction 22 min i.e. obtain described petrochemical wastewater process adsorbent.
Comparative example 1
Preparation method is same as in Example 1, and unique difference is that raw material uses single meerschaum.
Comparative example 2
Preparation method is same as in Example 1, and unique difference is in step (2) that modified feedstock is lived only with quaternary ammonium salt four cohesive surface
Property agent.
Comparative example 3
Preparation method is same as in Example 1, and unique difference is that the hydro-thermal reaction of step (2) changes normal pressure water-bath into.
Adsorption experiment I: embodiment 1-5 and comparative example 1-3 contain the absorption of waste water to simulation.
Using the absorbent particles after activation to process simulated oily wastewater, simulation oil-containing water sample major parameter is as follows: COD is dense
Degree is 1500.Omg L-1, oil concentration be 982.0mg L-1, water sampling 40mL.
Consumption and the adsorption conditions of adsorbent include: the consumption of absorbent particles is 25g/L, through meter 1g adsorbent, absorption
Temperature is 40 DEG C, and adsorption time is 120min, and experimental result see table 1.
Can be drawn by table 1, the adsorbent of embodiment 1-5 all demonstrates good suction to COD in petrochemical wastewater and oil
Attached performance, and it is better than the adsorbent of comparative example 1-3.
Finally it is noted that the foregoing is only the preferred embodiments of the present invention, it is not limited to the present invention,
Although being described in detail the present invention with reference to previous embodiment, for a person skilled in the art, it still may be used
So that the technical scheme described in foregoing embodiments to be modified, or wherein portion of techniques feature is carried out equivalent.
All within the spirit and principles in the present invention, any modification, equivalent substitution and improvement etc. made, should be included in the present invention's
Within protection domain.
Claims (8)
1. the preparation method of a petrochemical wastewater process adsorbent, it is characterised in that comprise the steps:
(1) preparation of composite granule gel: the modified meerschaum powder body taking 15-30 part property of modified rectorite powder body and 20-40 part divides
Dissipate in the solvent of 100-180 part, and ultrasonic vibration 1-2h at room temperature, then heat to 65-75 DEG C, be slowly added dropwise 20-30
The tetraethyl orthosilicate of part, continues stirring to solution and becomes solid phase;It is solid to mass conservation, at 100-110 DEG C with distilled water wash
It is dried 3-6 hour, obtains composite granule gel;
(2) preparation of modified compound adsorbent: modified composite granule gel step (1) obtained joins the season of 10-15 part
Mixing and stirring in ammonium salt four cohesive surface activating agent, the chitosan of 6-12 part and 50-80 part toluene solvant, then will mixing
Thing transfers in politef hydrothermal reaction kettle hydro-thermal reaction 6-10h at 80-120 DEG C, and reaction end is centrifuged, washes
Wash, dry, i.e. obtain modified compound adsorbent;
(3) preparation of magnetic composite adsorbent: the modified compound adsorbent that step (2) obtains is joined the mixing of 30-40 part
In iron salt solutions, at N2Under protection, under the conditions of 40 DEG C, stirring reaction 20-30 min i.e. obtains the process of described petrochemical wastewater
Use adsorbent.
Preparation method the most according to claim 1, it is characterised in that quaternary ammonium salt four cohesive surface activating agent in described (2)
Preparation method is: equipped with in the 250mL there-necked flask of condensing tube, adding dehydrated alcohol 40mL, ethylenediamine 4.5g, room temperature is carried out
Magnetic agitation, adds epoxychloropropane 34.7g, 50 DEG C of back flow reaction 4h after dropping with 10/min, obtains after decompression distillation
To four cohesive surface surfactant intermediate, for faint yellow translucent thick liquid, taking this intermediate 20g, adding volume ratio is 1:l's
Dehydrated alcohol and deionized water mixed solution 40mL are solvent, then drip 7.9gN, N-dimethyl dodecyl base tertiary amine, are warming up to
80 DEG C, reacting 1h, decompression distillation, recrystallization, vacuum drying obtains white powdery solids and is quaternary ammonium salt four cohesive surface activity
Agent.
Preparation method the most according to claim 1, it is characterised in that the modifying agent that described property of modified rectorite powder body is used
For the one in ten alkyl trimethyl phosphonium bromides, ten alkyl trimethyl phosphorus chloride and cetyl triphenylphosphonium chloride.
Preparation method the most according to claim 1, it is characterised in that the modifying agent that described modified meerschaum powder body is used
For the one in TEPA, triethylene tetramine, ethylenediamine or ethylenediaminetetraacetic acid.
Preparation method the most according to claim 1, it is characterised in that after adding mixed molysite solution in described step (3),
Being slowly added dropwise 1-2 part concentration during stirring is the ammonia of 28%, and ammonia finishes and is warming up to 40 DEG C again.
Preparation method the most according to claim 1, it is characterised in that described mixed molysite be mol ratio be 1:1.5-
The FeSO of 2.54·7H2O and FeC13·6H2The mixture of O.
Preparation method the most according to claim 1, it is characterised in that in described step (1), solvent is toluene, N, N-diformazan
One or more in base Methanamide, DMAC N,N' dimethyl acetamide, oxolane.
8. the adsorbent that method described in an any one of claim 1-7 prepares.
Priority Applications (3)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201610555322.1A CN106179196B (en) | 2016-07-15 | 2016-07-15 | A kind of petrochemical wastewater processing adsorbent and preparation method thereof |
CN201810281434.1A CN108439523B (en) | 2016-07-15 | 2016-07-15 | Application of composite adsorbent in treatment of oily wastewater |
CN201810281432.2A CN108421537B (en) | 2016-07-15 | 2016-07-15 | A kind of compound adsorbent and its preparation method and application |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201610555322.1A CN106179196B (en) | 2016-07-15 | 2016-07-15 | A kind of petrochemical wastewater processing adsorbent and preparation method thereof |
Related Child Applications (2)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201810281432.2A Division CN108421537B (en) | 2016-07-15 | 2016-07-15 | A kind of compound adsorbent and its preparation method and application |
CN201810281434.1A Division CN108439523B (en) | 2016-07-15 | 2016-07-15 | Application of composite adsorbent in treatment of oily wastewater |
Publications (2)
Publication Number | Publication Date |
---|---|
CN106179196A true CN106179196A (en) | 2016-12-07 |
CN106179196B CN106179196B (en) | 2018-06-19 |
Family
ID=57474886
Family Applications (3)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201810281434.1A Active CN108439523B (en) | 2016-07-15 | 2016-07-15 | Application of composite adsorbent in treatment of oily wastewater |
CN201810281432.2A Active CN108421537B (en) | 2016-07-15 | 2016-07-15 | A kind of compound adsorbent and its preparation method and application |
CN201610555322.1A Active CN106179196B (en) | 2016-07-15 | 2016-07-15 | A kind of petrochemical wastewater processing adsorbent and preparation method thereof |
Family Applications Before (2)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201810281434.1A Active CN108439523B (en) | 2016-07-15 | 2016-07-15 | Application of composite adsorbent in treatment of oily wastewater |
CN201810281432.2A Active CN108421537B (en) | 2016-07-15 | 2016-07-15 | A kind of compound adsorbent and its preparation method and application |
Country Status (1)
Country | Link |
---|---|
CN (3) | CN108439523B (en) |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN108854840A (en) * | 2018-05-03 | 2018-11-23 | 沈阳化工大学 | A kind of poly quaternary surfactant preparation method of amide containing coupling link |
CN108993395A (en) * | 2018-08-22 | 2018-12-14 | 嘉兴迪迈科技有限公司 | A kind of chemical waste liquid desulfuration adsorbent and preparation method thereof |
CN112715574A (en) * | 2021-01-20 | 2021-04-30 | 张乘邦 | Environment-friendly composite antibacterial agent and preparation method thereof |
Families Citing this family (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN109179573A (en) * | 2018-11-15 | 2019-01-11 | 刘益波 | A kind of inorganic agent and preparation method thereof can be used for handling sanitary sewage |
CN110585006A (en) * | 2019-08-30 | 2019-12-20 | 苏州市天灵中药饮片有限公司 | Traditional Chinese medicine decoction processing technology for reducing heavy metal residues |
CN113277783A (en) * | 2021-05-21 | 2021-08-20 | 陈锡均 | Epoxy asphalt concrete for roads and bridges and preparation method thereof |
CN115672257A (en) * | 2022-11-08 | 2023-02-03 | 江西省润穹环保科技有限公司 | Preparation method of adsorbent for oil-water separation |
CN117244535B (en) * | 2023-11-17 | 2024-02-20 | 中国科学院南京土壤研究所 | Preparation of floatable hollow microsphere material and application of floatable hollow microsphere material in soil cadmium reduction |
Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US20100087689A1 (en) * | 2008-10-02 | 2010-04-08 | Basf Se | Method for depletion of sulfur and/or compounds containing sulfur from a biochemically produced organic compound |
CN102580682A (en) * | 2012-01-17 | 2012-07-18 | 湘潭大学 | Adsorbent for simultaneously removing heavy metals and phenol organics in mineral processing wastewater and preparation method thereof |
CN103949203A (en) * | 2014-04-30 | 2014-07-30 | 明光市恒大棒粉厂 | Preparation method of novel compound wastewater treatment adsorbing agent |
CN104138740A (en) * | 2014-04-30 | 2014-11-12 | 明光市恒大棒粉厂 | Compound sewage treatment adsorbent |
CN105152296A (en) * | 2015-09-16 | 2015-12-16 | 杨洋 | Dyeing wastewater treating agent and manufacturing method thereof |
Family Cites Families (11)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN100491450C (en) * | 2006-12-22 | 2009-05-27 | 武汉大学 | Chitosan quaternary ammonium salt/organic rectorite composite material and its preparing method |
CN101502785B (en) * | 2008-11-25 | 2011-01-05 | 中国科学院合肥物质科学研究院 | Method for preparing nano titanates for removing surface modification of heavy metal ion |
CN101537341B (en) * | 2009-03-18 | 2011-03-23 | 济南大学 | Modified fly ash loading chitosan compounding sorption agent and preparation method thereof |
US9770514B2 (en) * | 2013-09-03 | 2017-09-26 | ExxPharma Therapeutics LLC | Tamper-resistant pharmaceutical dosage forms |
JP6383636B2 (en) * | 2013-10-22 | 2018-08-29 | 中国石油化工股▲ふん▼有限公司 | Metal-modified Y-type zeolite, its production and use |
ES2558472B1 (en) * | 2014-07-03 | 2016-11-16 | Consejo Superior De Investigaciones Científicas (Csic) | COMPOSITE MATERIAL OF NANOCELLULOSE AND FIBER CLAYS, MANUFACTURING AND USE PROCEDURE |
CN104475065B (en) * | 2014-12-16 | 2017-01-18 | 湖南科技大学 | Efficient heavy-metal-ion absorbent material and preparation method thereof |
CN104971694B (en) * | 2015-07-15 | 2017-06-27 | 中国石油天然气股份有限公司 | A kind of Inorganic whisker bentonite clay material and its preparation method and application |
CN105000621A (en) * | 2015-08-14 | 2015-10-28 | 宁波保税区维迪克环保科技有限公司 | Heavy metal sewage treatment agent and preparation method thereof |
CN105504760B (en) * | 2015-12-28 | 2017-12-08 | 山东蓝泓环境科技有限公司 | It is a kind of to be used to handle hydrogel material containing heavy metal containing sewage and preparation method thereof |
CN105709698B (en) * | 2016-04-07 | 2018-09-28 | 浙江科技学院 | A kind of N- carboxyetbyl chitosans nanometer magnetic bead and its preparation method and application |
-
2016
- 2016-07-15 CN CN201810281434.1A patent/CN108439523B/en active Active
- 2016-07-15 CN CN201810281432.2A patent/CN108421537B/en active Active
- 2016-07-15 CN CN201610555322.1A patent/CN106179196B/en active Active
Patent Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US20100087689A1 (en) * | 2008-10-02 | 2010-04-08 | Basf Se | Method for depletion of sulfur and/or compounds containing sulfur from a biochemically produced organic compound |
CN102580682A (en) * | 2012-01-17 | 2012-07-18 | 湘潭大学 | Adsorbent for simultaneously removing heavy metals and phenol organics in mineral processing wastewater and preparation method thereof |
CN103949203A (en) * | 2014-04-30 | 2014-07-30 | 明光市恒大棒粉厂 | Preparation method of novel compound wastewater treatment adsorbing agent |
CN104138740A (en) * | 2014-04-30 | 2014-11-12 | 明光市恒大棒粉厂 | Compound sewage treatment adsorbent |
CN105152296A (en) * | 2015-09-16 | 2015-12-16 | 杨洋 | Dyeing wastewater treating agent and manufacturing method thereof |
Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN108854840A (en) * | 2018-05-03 | 2018-11-23 | 沈阳化工大学 | A kind of poly quaternary surfactant preparation method of amide containing coupling link |
CN108854840B (en) * | 2018-05-03 | 2020-07-21 | 沈阳化工大学 | Preparation method of polyquaternium surfactant containing amide connecting chain |
CN108993395A (en) * | 2018-08-22 | 2018-12-14 | 嘉兴迪迈科技有限公司 | A kind of chemical waste liquid desulfuration adsorbent and preparation method thereof |
CN112715574A (en) * | 2021-01-20 | 2021-04-30 | 张乘邦 | Environment-friendly composite antibacterial agent and preparation method thereof |
CN112715574B (en) * | 2021-01-20 | 2023-09-26 | 张乘邦 | Environment-friendly composite antibacterial agent and preparation method thereof |
Also Published As
Publication number | Publication date |
---|---|
CN108439523B (en) | 2021-01-29 |
CN108421537A (en) | 2018-08-21 |
CN108439523A (en) | 2018-08-24 |
CN108421537B (en) | 2019-12-03 |
CN106179196B (en) | 2018-06-19 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN106179196A (en) | A kind of petrochemical wastewater process adsorbent and preparation method thereof | |
CN106000359B (en) | A kind of petrochemical wastewater processing adsorbent and preparation method thereof | |
Noreen et al. | Batch and fixed bed adsorption study for the removal of Drimarine Black CL-B dye from aqueous solution using a lignocellulosic waste: a cost affective adsorbent | |
CN104971699B (en) | A kind of modified zeolite organic matter complexing agent of sewage synchronous denitrification dephosphorizing and preparation method thereof, using and methods for using them | |
CN106076276B (en) | A kind of Industrial Wastewater Treatment adsorbent and preparation method thereof | |
CN102188957B (en) | Polyethyleneimine modified magnetic porous adsorbent and preparation method and application thereof | |
CN106179249B (en) | A kind of preparation method of concave convex rod cellulose composite adsorption microballoon | |
Ren et al. | Defective SO3H-MIL-101 (Cr) for capturing different cationic metal ions: Performances and mechanisms | |
CN105561933A (en) | Preparation method of modified magnetic hydrogel heavy metal ion adsorbent | |
CN106145132A (en) | A kind of method utilizing attapulgite to prepare ordered mesoporous material Al MCM 41 | |
CN105195110A (en) | Amine modified fibrous membrane adsorption material and preparation method thereof | |
CN110523395A (en) | A kind of load MOF resin compounded adsorbent and its preparation method and application | |
Han et al. | Preparation and uranium (VI) biosorption for tri-amidoxime modified marine fungus material | |
CN104785217B (en) | A kind of preparation method of flyash/graphene oxide composite adsorption material | |
CN105944698A (en) | Adsorbent for heavy metal ions in industrial wastewater and preparation method of adsorbent | |
CN103908955A (en) | Method for preparing acetamido-modified ultra-high crosslinking type adsorption resin and application of resin | |
CN112755983B (en) | Three-dimensional porous oil-water separation foam | |
CN106622177B (en) | A kind of spherical porous adsorbent and the preparation method and application thereof based on carbon nanotube | |
CN104128165A (en) | Preparation method and application of polysiloxane modified natural zeolite | |
CN105111413B (en) | A kind of preparation method and applications for having magnetic conjugatd polymerses microballoon | |
CN109851839A (en) | A kind of aerogel material and the preparation method and application thereof | |
CN110342604A (en) | Graphene-montmorillonite material absorption rhodamine B method | |
CN109589913A (en) | A kind of magnetic bio charcoal and the preparation method and application thereof of quick removal methylene blue | |
Liang et al. | Volatile Organic Compounds Adsorption Capacities of Zeolite/Activated Carbon Composites Formed by Electrostatic Self-Assembly | |
CN108744600A (en) | A kind of preparation method of water-oil separationg film |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
C06 | Publication | ||
PB01 | Publication | ||
C10 | Entry into substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
CB03 | Change of inventor or designer information |
Inventor after: Hou Fushun Inventor before: Ye Cheng |
|
CB03 | Change of inventor or designer information | ||
TA01 | Transfer of patent application right |
Effective date of registration: 20180515 Address after: 274500 Dongming Chemical Industrial Park, Chengguan Town, Dongming, Heze, Shandong Applicant after: CITIC Guoan Chemical Co Ltd Address before: 325024 second second, Sha Qian street, seaside street, Longwan District, Wenzhou, Zhejiang. Applicant before: WENZHOU HONGCHENGXIANG TECHNOLOGY CO., LTD. |
|
TA01 | Transfer of patent application right | ||
GR01 | Patent grant | ||
GR01 | Patent grant |