CN106986396A - A kind of modification of chitosan and preparation method thereof - Google Patents

A kind of modification of chitosan and preparation method thereof Download PDF

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Publication number
CN106986396A
CN106986396A CN201710308412.5A CN201710308412A CN106986396A CN 106986396 A CN106986396 A CN 106986396A CN 201710308412 A CN201710308412 A CN 201710308412A CN 106986396 A CN106986396 A CN 106986396A
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chitosan
modification
water
polyacrylamide
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陈宽
何明军
袁云杰
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Zhejiang World Clean Environment Engineering Co Ltd
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Zhejiang World Clean Environment Engineering Co Ltd
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    • 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
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/281Treatment of water, waste water, or sewage by sorption using inorganic sorbents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/286Treatment of water, waste water, or sewage by sorption using natural organic sorbents or derivatives thereof
    • 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
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • C02F1/5236Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents
    • C02F1/5245Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents using basic salts, e.g. of aluminium and iron
    • 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
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • C02F1/54Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using organic material
    • C02F1/56Macromolecular compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/105Phosphorus compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/16Nitrogen compounds, e.g. ammonia
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/20Heavy metals or heavy metal compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/08Chemical Oxygen Demand [COD]; Biological Oxygen Demand [BOD]
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/14NH3-N
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/16Total nitrogen (tkN-N)
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2303/00Specific treatment goals
    • C02F2303/02Odour removal or prevention of malodour

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  • Chemical & Material Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Organic Chemistry (AREA)
  • Inorganic Chemistry (AREA)
  • Water Treatment By Sorption (AREA)
  • Separation Of Suspended Particles By Flocculating Agents (AREA)

Abstract

The invention discloses a kind of modification of chitosan, the weight proportion of wherein each component is:10 15 parts of chitosan, 10 15 parts of aluminium polychloride, 35 parts of ethylenediamine, 35 parts of silane coupler, 15 parts of sodium hydroxide, 15 parts of polyacrylamide, 15 parts of aluminum sulfate, 15 parts of modification infusorial earth, the wherein ratio of polyacrylamide and modification infusorial earth are 1:1.A kind of modification of chitosan that the present invention is obtained, can effectively reduce the content of COD in water, total nitrogen, total phosphorus and ammonia nitrogen, effect is notable in terms of denitrogenation dephosphorizing.

Description

A kind of modification of chitosan and preparation method thereof
Technical field
The present invention relates to a kind of water treatment agent, particularly a kind of modification of chitosan and preparation method thereof.
Background technology
The bait added during fish culture all can not utilize effectively by cultivation object, have 70% ~ 80% to feed Material is to dissolve or particulate form is discharged into water body, wherein there are about 51% nitrogen and 64% phosphorus is discharged into ring in the form of pollutant In border.The eutrophication process of water proximate will be further exacerbated by, and wherein the higher of phosphorus concentration is to cause algae bio crazy Long principal element, therefore the concentration of reduction water body nitrogen phosphorus especially phosphorus is the primary approach for solving the problems, such as body eutrophication.With Industrial wastewater is compared with sanitary sewage, and aquiculture waste water has that pollutant load is low, the big and pollutant that need to handle water The characteristics of main component, structure are different from common Lu Yuan sewage.Main processing method has physics, chemistry and biological treatment, Wherein, the engineering measure investment of physical method is huge, often cures the symptoms, not the disease;Chemical method easily causes secondary pollution;Biology side The method cycle of operation is long, and single treatment does not reach discharge standard.In view of the defect of above-mentioned conventional method, adsorption treatment method can yet be regarded as one Important physico-chemical process is planted, is played an important role all the time in cultivating wastewater purification.
Chitosan (CTS) is the deacetylated products of chitin N-, is the nitrogen-containing basic polysaccharide that nature is uniquely largely present.From Since 1970s, chitosan, chitin are utilized and studied with its unique physicochemical properties and bioactivity, are enjoyed The favor of researcher, it is considered to be " green water treatment agent ", currently turns into the study hotspot in environment-friendly material field.Cause Contain substantial amounts of hydroxyl and amino in chitosan and its modifier molecule, there is very strong chelation to metal ion, can be with For reclaiming the industrial wastewater of heavy metal and processing containing heavy metal ion.But currently without modified chitosan in sewage disposal The effect of middle denitrogenation dephosphorizing is also less desirable.
The content of the invention
A kind of one kind of high-efficient denitrification and dephosphorization is provided the invention aims to solve above-mentioned the deficiencies in the prior art Modification of chitosan and preparation method thereof.
To achieve these goals, a kind of modification of chitosan designed by the present invention, the weight proportion of wherein each component is: It is 10-15 parts of chitosan, 10-15 parts of aluminium polychloride, 3-5 parts of ethylenediamine, 3-5 parts of silane coupler, 1-5 parts of sodium hydroxide, poly- 1-5 parts of acrylamide, 1-5 parts of aluminum sulfate, 1-5 parts of modification infusorial earth, the ratio of wherein polyacrylamide and modification infusorial earth is 1:1。
Each component weight proportion in the modification infusorial earth is 60 parts of diatomite, 15 parts of pomelo peel, 5 parts of activated carbon, stone Black 10 parts of alkene, 2 parts of poly-ferric chloride, 3 parts of cerous nitrate, 5 parts of oxalic acid.
The polyacrylamide is PAMC, and its molecular weight is 10,000,000.
The chitosan is water soluble chitosan.
A kind of preparation method of modification of chitosan, comprises the following steps:
Step 1, pomelo peel is cleaned with distilled water, dries 2h after chopping at 105 DEG C, ground after taking-up, taken after crossing 100 mesh sieves 15 parts are put into beaker, add 5 parts of activated carbon, it is well mixed after be put into the 2- well prepared in advance being made up of 5 parts of oxalic acid In 3mol/L oxalic acid solution, 60 parts of diatomite, 10 parts of graphene, 2 parts of poly-ferric chloride, 3 parts of cerous nitrate are then sequentially placed into, By stirring mixing, after the normal-temperature reaction of 24 hours, deliver in baking oven, take out cooling after being dried in 105 DEG C, be ground to 100 mesh, it is standby to make to obtain modification infusorial earth;
Step 2, it is 10-15 parts of 10-15 parts of chitosan and aluminium polychloride is soluble in water, it is then slow while stirring at 80 DEG C 1-5 parts of sodium hydroxide is added, 3-5 parts of ethylenediamine, 3-5 parts of silane coupler is subsequently added into, after being uniformly mixed, stood 24 hours, then air-dry at normal temperatures, obtain mixture A standby to make;
Step 3, it is 1-5 parts of aluminum sulfate, 1-5 parts of polyacrylamide is soluble in water, mixed by mixing apparatus, at normal temperatures and pressures By 100 turns per minute, through 10 ~ 20 minutes be thoroughly mixed, mixture B is obtained standby to make;
Step 4, it is soluble in water after mixture A is mixed with mixture B, then 1-5 parts of modification infusorial earth is put into, in normal temperature and pressure Under, after the mixing that 30 ~ 60 minutes are carried out by 100 turns per minute of speed, natural air drying is the modification shell for obtaining the present invention Glycan.
Wherein chitosan (CTS) is white plates or pulverulent solids with pearly luster, with biodegradability, Various bacteria, the growth of fungi can also be suppressed.Chitosan causes the concern of people as material for water treatment, living on its strand Property amino and hydroxyl have very strong suction-operated to pollutant, its absorption to pollutant mainly has physical absorption, chemistry to inhale Echo ion exchange absorption.Chitosan contains substantial amounts of hydroxyl and amino, can generate chelate with metal formation coordinate bond.Change It is monolayer adsorption to learn absorption, selective.Physical absorption is the suction by electrostatic attraction, hydrophobic reciprocation, Van der Waals force etc. It is attached, it is multilayer absorption.Many hydroxyls, amino and some N- acetylaminos are dispersed with the macromolecular chain of chitosan, can be in acidity The cationic polyelectrolyte of high charge density is formed in solution, similar network structure can be also formed by hydrogen bond or ionic bond Cage molecule, is settled so as to condense the suspension in water.
There is aluminium polychloride (PAC) color to be in yellow, there is the performances such as absorption, cohesion, precipitation, aluminium polychloride stability Difference.Toxicity and protection are corrosive, and with powder is thin, particle is uniform, soluble in water, flocculating effect is good, purification efficient stable, throw Dosage is few, the low feature of cost.It is suitable in terms of drink water purifying, city water purification and industrial water supply purification;It is applied to The source water of various turbidity, pH is applied widely, and it is fast that alumen ustum forms big, fast, sinking speed.Due to spray dried products stability Good, adaptation waters is wide, and hydrolysis rate is fast, high adsorption capacity, forms alumen ustum greatly, and soon, delivery turbidity is low, dewatering for the close precipitation of matter Good the advantages of, in the case of same water quality, spray drying aluminium polychloride throwing amount is reduced.
By the way that chitosan and aluminium polychloride are mixed, then cause on chitosan on hydroxyl radical free radical with the aluminium in aluminium chloride Ion coordination, aluminium ion covers chitosan surface increase surface area and space, increases adsorbance.Increase ethylenediamine simultaneously, draw More NH are entered2, obtained compound adsorbent is increased than the adsorption activity point of chitosan, so as to improve adsorbance. Increase silane coupler, then introduce SiO2The density of chitosan is increased, makes made compound adsorbent more heavy than chitosan Reduction of speed rate is accelerated.
Simultaneously polyacrylamide also have good flocculability, the frictional resistance between liquid can be reduced, with aluminium from During son mixing, its flocculation ability can be strengthened, increase the cohesiveness of adsorbed material to a certain extent.Chitosan-aluminium-polypropylene Acid amides three can promote mutually, improve flocculation ability.
Other diatomite is a kind of siliceous organism sedimentary rock, and main chemical is SiO2, and contain a small amount of Al2O3, P2O5, CaO, MgO etc., it is made up of the wall shell of diatom, has multistage, a large amount of, micropore of ordered arrangement on wall shell, surface has largely Carboxyl is covered, thus aobvious faintly acid, is referred to as solid acid in catalytic field.Diatomite light weight, porous, relative density are small, aperture Distribution is big, and porosity is high, and high adsorption capacity can adsorb 1.5~4 times of impurity of own wt.Therefore, by diatomite Unique microcellular structure, waste water is handled using its absorption property can not only reduce cost, but also can more effective land productivity With the mineral resources of China's abundant.And in this patent, diatomite is modified using graphene and poly-ferric chloride so that change Diatomite after property is greatly improved for the clearance of organic matter.When graphene and poly-ferric chloride are distributed in diatomaceous surface When, there is stronger cohesiveness to the organic matter in sewage so that more organic matters are attracted in microcellular structure.While nitre The addition of sour cerium then improves facilitation, improves the activity of graphene and poly-ferric chloride.The shaddock peel powder that it is possible to additionally incorporate End, is also the material with stronger adsorption capacity, and both diatomite and pomelo peel powder cooperate, had to organic removal rate Bigger enhancement effect, and the toxic heavy metal ion that pomelo peel powder can be in absorption effluent.Wherein activated carbon has There are certain deodorizing capability and adsorption capacity, to having certain improvement result on sanitary sewage smell.
A kind of modification of chitosan that the present invention is obtained, organic matter that can effectively in absorption effluent, so as to reduce in water COD, total nitrogen, the content of total phosphorus and ammonia nitrogen, effect is notable in terms of denitrogenation dephosphorizing.
Embodiment
With reference to embodiment, the present invention is further described.
Embodiment 1:
A kind of modification of chitosan that the present embodiment is provided, the weight proportion of each component is:10 parts of chitosan, aluminium polychloride 10 Part, 3 parts of ethylenediamine, 3 parts of silane coupler, 2 parts of sodium hydroxide, 3 parts of polyacrylamide, 3 parts of aluminum sulfate, 3 parts of modification infusorial earth.
Each component weight proportion in the modification infusorial earth is 60 parts of diatomite, 15 parts of pomelo peel, 5 parts of activated carbon, stone Black 10 parts of alkene, 2 parts of poly-ferric chloride, 3 parts of cerous nitrate, 5 parts of oxalic acid.
A kind of preparation method of modification of chitosan, comprises the following steps:
Step 1, pomelo peel is cleaned with distilled water, dries 2h after chopping at 105 DEG C, ground after taking-up, taken after crossing 100 mesh sieves 15 parts are put into beaker, add 5 parts of activated carbon, it is well mixed after be put into the 2- well prepared in advance being made up of 5 parts of oxalic acid In 3mol/L oxalic acid solution, 60 parts of diatomite, 10 parts of graphene, 2 parts of poly-ferric chloride, 3 parts of cerous nitrate are then sequentially placed into, By stirring mixing, after the normal-temperature reaction of 24 hours, deliver in baking oven, take out cooling after being dried in 105 DEG C, be ground to 100 mesh, it is standby to make to obtain modification infusorial earth;
Step 2, it is 10 parts of 10 parts of chitosan and aluminium polychloride is soluble in water, then hydrogen is slowly added to while stirring at 80 DEG C 2 parts of sodium oxide molybdena, is subsequently added into 32 parts of ethylenediamine, 32 parts of silane coupler, after being uniformly mixed, and stands 24 hours, so Air-dry at normal temperatures afterwards, obtain mixture A standby to make;
Step 3, it is 3 parts of aluminum sulfate, 3 parts of polyacrylamide is soluble in water, mixed by mixing apparatus, at normal temperatures and pressures by every 100 turns of minute, through 10 ~ 20 minutes be thoroughly mixed, obtain mixture B standby to make;
Step 4, it is soluble in water after mixture A is mixed with mixture B, then 1-5 parts of modification infusorial earth is put into, in normal temperature and pressure Under, after the mixing that 30 ~ 60 minutes are carried out by 100 turns per minute of speed, natural air drying is the modification shell for obtaining the present invention Glycan.
Modification of chitosan made from the present embodiment is used to handle breeding wastewater, its result is as follows:COD, total nitrogen, total phosphorus and The clearance of ammonia nitrogen is respectively:93.4%、87.1%、87.3%、92.5%.
Embodiment 2:
A kind of modification of chitosan that the present embodiment is provided and preparation method thereof is substantially same as Example 1, and its main distinction point exists In the weight proportion of each component is in the present embodiment:It is 15 parts of chitosan, 15 parts of aluminium polychloride, 3 parts of ethylenediamine, silane coupled 33 parts of agent, 2 parts of sodium hydroxide, 5 parts of polyacrylamide, 5 parts of aluminum sulfate, 5 parts of modification infusorial earth.
Modification of chitosan made from the present embodiment is used to handle breeding wastewater, its result is as follows:COD, total nitrogen, total phosphorus and The clearance of ammonia nitrogen is respectively:92.5%、88.3%、86.9%、93.1%.
Embodiment 3:
A kind of modification of chitosan that the present embodiment is provided and preparation method thereof is substantially same as Example 1, and its main distinction point exists In the weight proportion of each component is in the present embodiment:It is 12 parts of chitosan, 12 parts of aluminium polychloride, 5 parts of ethylenediamine, silane coupled 5 parts of agent, 5 parts of sodium hydroxide, 4 parts of polyacrylamide, 4 parts of aluminum sulfate, 4 parts of modification infusorial earth.
Modification of chitosan made from the present embodiment is used to handle breeding wastewater, its result is as follows:COD, total nitrogen, total phosphorus and The clearance of ammonia nitrogen is respectively:93.6%、88.3%、87.9%、92.8%.

Claims (5)

1. a kind of modification of chitosan, it is characterized in that the weight proportion of each component is:10-15 parts of chitosan, aluminium polychloride 10-15 Part, 3-5 parts of ethylenediamine, 3-5 parts of silane coupler, 1-5 parts of sodium hydroxide, 1-5 parts of polyacrylamide, 1-5 parts of aluminum sulfate, modification 1-5 parts of diatomite, the wherein ratio of polyacrylamide and modification infusorial earth are 1:1.
2. a kind of modification of chitosan according to claim 1, it is characterized in that each component weight in the modification infusorial earth Match as 60 parts of diatomite, 15 parts of pomelo peel, 5 parts of activated carbon, 10 parts of graphene, 2 parts of poly-ferric chloride, 3 parts of cerous nitrate, oxalic acid 5 parts.
3. a kind of modification of chitosan according to claim 1, it is characterized in that the polyacrylamide is cation polypropylene Acid amides, its molecular weight is 10,000,000.
4. a kind of modification of chitosan according to claim 1, it is characterized in that the chitosan is water soluble chitosan.
5. a kind of preparation method of modification of chitosan as claimed in claim 1, it is characterized in that comprising the following steps:
Step 1, pomelo peel is cleaned with distilled water, dries 2h after chopping at 105 DEG C, ground after taking-up, taken after crossing 100 mesh sieves 15 parts are put into beaker, add 5 parts of activated carbon, it is well mixed after be put into the 2- well prepared in advance being made up of 5 parts of oxalic acid In 3mol/L oxalic acid solution, 60 parts of diatomite, 10 parts of graphene, 2 parts of poly-ferric chloride, 3 parts of cerous nitrate are then sequentially placed into, By stirring mixing, after the normal-temperature reaction of 24 hours, deliver in baking oven, take out cooling after being dried in 105 DEG C, be ground to 100 mesh, it is standby to make to obtain modification infusorial earth;
Step 2, it is 10-15 parts of 10-15 parts of chitosan and aluminium polychloride is soluble in water, it is then slow while stirring at 80 DEG C 1-5 parts of sodium hydroxide is added, 3-5 parts of ethylenediamine, 3-5 parts of silane coupler is subsequently added into, after being uniformly mixed, stood 24 hours, then air-dry at normal temperatures, obtain mixture A standby to make;
Step 3, it is 1-5 parts of aluminum sulfate, 1-5 parts of polyacrylamide is soluble in water, mixed by mixing apparatus, at normal temperatures and pressures By 100 turns per minute, through 10 ~ 20 minutes be thoroughly mixed, mixture B is obtained standby to make;
Step 4, it is soluble in water after mixture A is mixed with mixture B, then 1-5 parts of modification infusorial earth is put into, in normal temperature and pressure Under, after the mixing that 30 ~ 60 minutes are carried out by 100 turns per minute of speed, natural air drying is the modification shell for obtaining the present invention Glycan.
CN201710308412.5A 2017-05-04 2017-05-04 A kind of modification of chitosan and preparation method thereof Pending CN106986396A (en)

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Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109319895A (en) * 2018-10-23 2019-02-12 四川意德康环保科技有限公司 A kind of aluminium polychloride and preparation method thereof that Nano chitosan is modified
CN112127049A (en) * 2020-09-30 2020-12-25 安徽灵春医用耗材有限公司 Preparation method of polypropylene melt-blown non-woven fabric material for mask
CN112320914A (en) * 2020-10-13 2021-02-05 神美科技有限公司 Phosphorus removal agent with composite function and phosphorus removal method
CN114105245A (en) * 2021-12-09 2022-03-01 宝钢湛江钢铁有限公司 Treatment process for removing soluble organic matters in reverse osmosis concentrated water
CN114275832A (en) * 2021-12-22 2022-04-05 江苏宿迁润泰环保科技有限公司 Biological polysaccharide-based sewage treatment agent and application thereof in sewage treatment process
CN116789331A (en) * 2023-08-22 2023-09-22 青岛中润设备仪表有限公司 Sea water desalination process
CN117142548A (en) * 2023-10-30 2023-12-01 中国科学院东北地理与农业生态研究所 Wastewater treatment material based on graphene composite modification and preparation method thereof

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102671633A (en) * 2012-05-07 2012-09-19 浙江大学 Preparation method, product and application of chitosan aluminum-iron composite adsorbent
CN103121742A (en) * 2012-11-12 2013-05-29 武汉斯隆电气有限公司 Inorganic-modified chitosan composite type polymeric flocculant
CN104071881A (en) * 2014-07-18 2014-10-01 廉勇 Flocculating agent for waste water treatment, and preparation method thereof
CN107265931A (en) * 2017-05-04 2017-10-20 浙江清天地环境工程有限公司 A kind of eco-concrete and preparation method thereof

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102671633A (en) * 2012-05-07 2012-09-19 浙江大学 Preparation method, product and application of chitosan aluminum-iron composite adsorbent
CN103121742A (en) * 2012-11-12 2013-05-29 武汉斯隆电气有限公司 Inorganic-modified chitosan composite type polymeric flocculant
CN104071881A (en) * 2014-07-18 2014-10-01 廉勇 Flocculating agent for waste water treatment, and preparation method thereof
CN107265931A (en) * 2017-05-04 2017-10-20 浙江清天地环境工程有限公司 A kind of eco-concrete and preparation method thereof

Cited By (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109319895A (en) * 2018-10-23 2019-02-12 四川意德康环保科技有限公司 A kind of aluminium polychloride and preparation method thereof that Nano chitosan is modified
CN109319895B (en) * 2018-10-23 2021-10-08 四川意德康环保科技有限公司 Nano chitosan modified polyaluminum chloride and preparation method thereof
CN112127049A (en) * 2020-09-30 2020-12-25 安徽灵春医用耗材有限公司 Preparation method of polypropylene melt-blown non-woven fabric material for mask
CN112320914A (en) * 2020-10-13 2021-02-05 神美科技有限公司 Phosphorus removal agent with composite function and phosphorus removal method
CN112320914B (en) * 2020-10-13 2022-09-27 神美科技有限公司 Phosphorus removal agent with composite function and phosphorus removal method
CN114105245A (en) * 2021-12-09 2022-03-01 宝钢湛江钢铁有限公司 Treatment process for removing soluble organic matters in reverse osmosis concentrated water
CN114275832A (en) * 2021-12-22 2022-04-05 江苏宿迁润泰环保科技有限公司 Biological polysaccharide-based sewage treatment agent and application thereof in sewage treatment process
CN114275832B (en) * 2021-12-22 2022-10-18 江苏宿迁润泰环保科技有限公司 Biological polysaccharide-based sewage treatment agent and application thereof in sewage treatment process
CN116789331A (en) * 2023-08-22 2023-09-22 青岛中润设备仪表有限公司 Sea water desalination process
CN116789331B (en) * 2023-08-22 2023-11-10 青岛中润设备仪表有限公司 Sea water desalination process
CN117142548A (en) * 2023-10-30 2023-12-01 中国科学院东北地理与农业生态研究所 Wastewater treatment material based on graphene composite modification and preparation method thereof
CN117142548B (en) * 2023-10-30 2024-01-09 中国科学院东北地理与农业生态研究所 Wastewater treatment material based on graphene composite modification and preparation method thereof

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Application publication date: 20170728