CN104001479B - A kind of inorganic mineral water treatment agent and preparation method thereof - Google Patents

A kind of inorganic mineral water treatment agent and preparation method thereof Download PDF

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CN104001479B
CN104001479B CN201410229891.8A CN201410229891A CN104001479B CN 104001479 B CN104001479 B CN 104001479B CN 201410229891 A CN201410229891 A CN 201410229891A CN 104001479 B CN104001479 B CN 104001479B
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water treatment
treatment agent
zeolite
inorganic mineral
mineral water
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CN104001479A (en
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陈庆
李紫薇
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Shandan County Dongsheng water purifying agent factory
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Chengdu New Keli Chemical Science Co Ltd
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Abstract

The invention belongs to inorganic water treatment agent field, does is it 35% by 50-60 part natural zeolite, 25-30 part red pelelith, 8-15 part natural fiber, 3-4 part ferrous salt and 1-2 part mass concentration in particular to a kind of fiber multihole zeolite water inorganic agent and preparation method thereof? H 2o 2the aqueous solution forms; Its preparation method is: by natural zeolite and pelelith mixing, through process such as fragmentation, acid elution, Infrared irradiations, then natural fiber and zeolite are mixed under vacuum with pelelith mixture, add solubility ferrous iron solution, add H after a while 2o 2the aqueous solution, stir dry, high-temperature calcination, cooling is dried, and is inorganic mineral water treatment agent of the present invention.This water treatment agent has larger adsorption space and absorption affinity, can solve the problems such as the wastewater treatment efficiency of existing water treatment agent to complicated component is not obvious, environmental pollution.Water treatment agent of the present invention easily regenerates, and can not cause secondary pollution, can be widely used in the purified treatment of all kinds of sewage.

Description

A kind of inorganic mineral water treatment agent and preparation method thereof
Technical field
The present invention relates to water treatment agent field, be specifically related to a kind of with natural zeolite and natural fiber inorganic mineral water treatment agent that is primary raw material and preparation method thereof.
Background technology
The chemical agent that water treatment agent is water for industrial use, must use in domestic water, wastewater treatment process.The use of these chemical agents, makes the quality requirement that water reaches certain.Its Main Function is the formation controlling incrustation scale, mud, reduces foam, reduces the corrosion to material contact with water, and except the suspended solid in anhydrating and noxious material, deodorizing, decolouring, soften, stabilizing water quality and desalinization etc.The material base that the development of water treatment field itself relies on also is taken from environment, its many product also has many requirements not meeting environmental protection, as medicament or the formulation product of poisonous, high phosphorus, heavy metal, the current demand that technically can't meet water treatment, therefore, water treatment field itself is also faced with the problem such as demand of technological innovation, development, develop low toxicity, even nontoxic with eco-friendly Green Water treatment product and rationally, economic, safe Green Water treatment process, be the active demand of current water treatment field.And zeolite has the performances such as adsorptivity, ion exchangeable, catalysis and acidproof heat-proof, can be used as adsorbent, ion-exchanger and catalyst, for aspects such as sewage disposals, there is market application foreground widely.
Natural zeolite surface silicon oxide structure has extremely strong hydrophily, and the hydrolysis of structural outer cation easily, cause the performance extreme difference of natural zeolite adsorb organic compound, and silicon-aluminum structure itself is electronegative, therefore natural zeolite is difficult to remove the anionic pollutant in water.Therefore, modification is carried out to natural zeolite, improve its adsorption capacity to organic matter and anion, natural zeolite can be made more to be widely used in water treatment field natural zeolite through modification, its porosity and surface-active can be significantly improved, improve absorption property, ion-exchange performance and exchange capacity etc., thus improve its use value.Modified zeolite comprises wide range, from through simple ion-exchange treatment until the complete avalanche of structure and the product obtained all belongs to modified zeolite scope.
Porous zeolite material is the crystalline zeolite containing enriching porous, not only remain the excellent acidity of zeolitic material and hydrothermal stability, and improve it to macromolecular absorption and diffusion due to the introducing of new bore, particularly relating in macromolecular catalytic reaction at catalytic field is the material that there is application prospect pole.Early stage porous zeolite synthetic method mainly uses post processing, comprises hydrothermal treatment consists, acid treatment or alkali treatment.The use of template in recent years becomes the main method of synthesizing porous zeolite, mainly comprises mesoporous carbon template, high molecular polymer, organosilan and nano-inorganic substance etc.But the shortcomings such as existing template is big for environment pollution, cost is high, crystallization time is long, should not widely use.
Chinese Patent Application No. 201210382889.5,201210010532.4 and 201310414937.9, by zeolite and other blend Coagulation and Adsorption or metal-modified, improve absorption and sedimentation effect, adding of metallics can change water quality activity, but be sorbent usedly natural materials, absorption property is limited, and metal-modified rear absorption object is single, can only partial adsorbates to the pollutant such as organic matter, metal, and the adding of metal active material, can cause the secondary pollution to water body, the Treatment of Sludge trouble after absorption, easily causes secondary pollution to environment.
Chinese Patent Application No. 201310543704.9 and 200810143851.6, by zeolite through alkali treatment and surface modification, but the adsorptive selectivity had of modifier, can only adsorb certain or certain pollutant, so do not have a significant effect to this inorganic agent of process of complicated component sewage.
Chinese Patent Application No. 201210020674.9 and 201110321285.5, by zeolite through alkali treatment, microwave treatment, acid treatment etc., zeolite effective aperture is increased and promotes the generation of meso-hole structure, but inorganic agent used is the highly basic strong acid such as NaOH, lithium hydroxide, potassium hydroxide, sulfuric acid, nitric acid, have higher risk, and discharge of wastewater easily causes the secondary pollution of water quality, air etc. in large-scale production.
Chinese Patent Application No. 200810080287.8 and 200810080287.8, uses template modified zeolite, makes modified zeolite be highly ordered porous materials, but template is to mostly being non-green auxiliary agent, easily to environment, in manufacture process, crystallization time is long, makes production cost higher.
The application of zeolite in sewage disposal is comparatively extensive, but prior art exists poor to the wastewater treatment efficiency of complicated component, adjuvant usedly easily causes secondary pollution to water source, the problems such as cost of manufacture is high, technological process complexity.
Summary of the invention
The present invention is directed to that existing inorganic water treatment agent adsorbance is few, absorption affinity is little and environmental pollution, the problems such as cost of manufacture is high, complex process, provide a kind of main component to be the fiber multihole inorganic mineral water treatment agent that natural zeolite and natural fiber are made.
The present invention further provides a kind of preparation method of inorganic mineral water treatment agent, the method is by pulverizing natural zeolite, miniaturization natural fiber mass, and Homogeneous phase mixing two kinds of materials under vacuum, through high temperature sintering, natural fiber is stayed in zeolite pores, make zeolite form fiber multihole shape structure, thus improve zeolite to the purified treatment ability of sewage.
A kind of inorganic mineral water treatment agent of the present invention, is characterized in that weight portion consists of: 50-60 part natural zeolite, 25-30 part red pelelith, 8-15 part natural fiber, 3-4 part ferrous salt and 1-2 part mass concentration are the H of 35% 2o 2the aqueous solution forms, the at least one in analcime, phillipsite, sodalite, heulandite, clinoptilolite, chabasie, faujasite selected by wherein said natural zeolite, the at least one in husk, stalk, flax, kapok, sugarcane selected by described natural fiber, and described ferrous salt selects FeSO 4, FeCl 2in one.
Above-mentioned a kind of inorganic mineral water treatment agent, is characterized in that: described natural zeolite is preferably faujasite.
Above-mentioned a kind of inorganic mineral water treatment agent, is characterized in that: described ferrous salt and H 2o 2mass ratio is preferably m (Fe 2+)/m (H 2o 2)=8.
The preparation method of a kind of inorganic mineral water treatment agent of the present invention, is characterized in that: carry out as follows:
1) 50-60 part natural zeolite and the mixing of 25-30 part pelelith are crushed to particle diameter≤50 μm, 2-5h is soaked through ethylenediamine tetra-acetic acid, be the salt acid elution of 6M/L again by concentration, add hot reflux 8-10h, clean with distilled water, dry 24h at 60 ~ 200 DEG C, and the Infrared irradiation 3-6h with wavelength being 750nm, be conducive to the formation of porous;
2) by the abundant miniaturization of 8-15 part natural fiber mass, cross 2000 order molecular sieves, and ribbon length is less than 1) the middle particle diameter processing rear gained material;
3) by 1) with 2) material Homogeneous phase mixing under 1.5-2.5MPa vacuum condition of gained, natural fiber is made to enter into 1) the intragranular space of gained material, and 3h-8h is calcined at Muffle furnace 700-1000 DEG C, make 1) the fibrous porous structure of the interior formation of gained material, fiber multihole zeolite matrix is shaping;
4) by 3) gained material adds in deionized water, then adds the ferrous salt of 3-4 part, be uniformly mixed, and drips the H of 35% of 1-2 part in 0.5h-1.5h 2o 2the aqueous solution, at the uniform velocity stirs, at 40-100 DEG C, react 20h, and reaction terminates, centrifugal, filters, and using the precipitation that obtains as stock, by fluid bed, can obtain a kind of inorganic mineral water treatment agent.
The preparation method of above-mentioned a kind of inorganic mineral water treatment agent, is characterized in that: in manufacturing process step 3), and mixture is Homogeneous phase mixing in the de-airing mixer of 120r/min at rotating speed.
The preparation method of above-mentioned a kind of inorganic mineral water treatment agent, is characterized in that: the deionized water volume added in step 4) in manufacturing process is 0.8-1.5 times of step 3) gained mass volume.
The present invention's natural zeolite and natural fiber, via Infrared irradiation, vacuum mixes, the techniques such as high temperature sintering, obtained a kind of fiber multihole shape zeolite water inorganic agent; Component cost used is low, environmentally friendly, is easy to reclaim, and can be mass-produced.
Compared with prior art, usefulness is mainly reflected in the present invention:
(1) natural zeolite and natural fiber are through process such as modification, vacuum mixing, make that zeolite increases the adsorbance of each pollutant, absorption affinity strengthens;
(2) natural fiber of modified zeolite and miniaturization Homogeneous phase mixing under vacuum, fibrous matter is made to enter into zeolite pores, again via high temperature sintering, form the zeolite of fiber multihole shape structure, while effective increase specific area, change pore size, make molecular weight, not easily also can be removed by the material adsorbed, thus reach the effect to multiple pollutant high adsorption capacity;
(3) preparation technology of the present invention is simple, and cost is low, and is easy to reclaim, and can reuse, environmental friendliness, suitable for mass production.
Accompanying drawing explanation
Fig. 1 is the preparation flow figure of a kind of inorganic mineral water treatment agent of the present invention.
Detailed description of the invention
Below by way of detailed description of the invention, the present invention is described in further detail, but this should be interpreted as scope of the present invention is only limitted to following example.When not departing from said method thought of the present invention, the various replacement made according to ordinary skill knowledge and customary means or change, all should be within the scope of the present invention.
embodiment 1
1) 10KG faujasite and the red pelelith mixing of 5KG being crushed to particle diameter is 40 μm, 3h is soaked through ethylenediamine tetra-acetic acid, with the salt acid elution that concentration is 6M/L, add hot reflux 8h, clean with distilled water again, dry 24h at 150 DEG C, and the Infrared irradiation 6h with wavelength being 750nm, be conducive to the formation of porous;
2) by abundant for 2KG dry straw miniaturization, cross 2000 order molecular sieves, and ribbon length is 30 μm;
3) by 1) with 2) material Homogeneous phase mixing under 2.5MPa vacuum condition of gained, at Muffle furnace 800 DEG C, calcine 5h, make 1) form fibrous porous structure in gained material, fiber multihole zeolite matrix is shaping;
4) by 3) material add volume for 3) step material cumulative volume 1.5 times deionized water in, then the 0.75KGFeSO added 4, be uniformly mixed, in 1h, drip the H that 0.3KG mass concentration is 35% 2o 2the aqueous solution; At the uniform velocity stir, at 100 DEG C, react 20h; Reaction terminates, centrifugal, filters, and using the precipitation that obtains as stock, by fluid bed, can obtain a kind of inorganic mineral water treatment agent.
Embodiment 1 gained water treatment agent is added certain import department of water treatment plant sewage, water treatment agent of the present invention is joined in sewage by 0.30% of required water quality treatment amount.Before and after process, water quality index is as following table:
Before process (mg/L) After process (mg/L)
BOD (BOD 5 125 1.24
Chemical oxygen consumption (COC) (COD cr 157 0.21
Total nitrogen content (T-N) 25.4 0.62
Total phosphorus content (T-P) 3.1 Trace
embodiment 2
1) 5KG chabasie and the red pelelith mixing of 2.5KG being crushed to particle diameter is 40 μm, 3h is soaked through ethylenediamine tetra-acetic acid, with the salt acid elution that concentration is 6M/L, add hot reflux 8h, clean with distilled water again, dry 24h at 150 DEG C, and the Infrared irradiation 6h with wavelength being 750nm, be conducive to the formation of porous;
2) by the abundant miniaturization of dry for 2KG cane stalk, cross 2000 order molecular sieves, and ribbon length is 35 μm;
3) by 1) with 2) material Homogeneous phase mixing under 2.5MPa vacuum condition of gained, at Muffle furnace 800 DEG C, calcine 5h, make 1) form fibrous porous structure in gained material, fiber multihole zeolite matrix is shaping;
4) by 3) material add volume for 3) step material cumulative volume 0.9 times deionized water in, then the 0.45KGFeSO added 4, be uniformly mixed, in 1h, drip the H that 0.15KG mass concentration is 35% 2o 2the aqueous solution; At the uniform velocity stir, at 100 DEG C, react 20h; Reaction terminates, centrifugal, filters, and using the precipitation that obtains as stock, by fluid bed, can obtain a kind of inorganic mineral water treatment agent.
Embodiment 2 gained water treatment agent is added in certain papermaking sewage, water treatment agent of the present invention is joined in sewage by 0.95% of required water quality treatment amount.Before and after process, water quality index is as following table:
Before process (mg/L) After process (mg/L)
Suspension (SS) in water quality 1067 25.7
Chemical oxygen consumption (COC) (CODcr) 4800 34
Volatile phenol 1.7 Trace
Sulfide 15.1 Trace
Colourity 96 8
embodiment 3
1) 6KG sodalite and the red pelelith mixing of 3KG being crushed to particle diameter is 40 μm, 3h is soaked through ethylenediamine tetra-acetic acid, with the salt acid elution that concentration is 6M/L, add hot reflux 8h, clean with distilled water again, dry 24h at 150 DEG C, and the Infrared irradiation 6h with wavelength being 750nm, be conducive to the formation of porous;
2) by the abundant miniaturization of dry for 2KG cane stalk, cross 2000 order molecular sieves, and ribbon length is 35 μm;
3) by 1) with 2) material Homogeneous phase mixing under 2.5MPa vacuum condition of gained, at Muffle furnace 800 DEG C, calcine 5h, make 1) form fibrous porous structure in gained material, fiber multihole zeolite matrix is shaping;
4) by 3) material add volume for 3) step material cumulative volume 0.8 times deionized water in, then the 1.8KGFeSO added 4, be uniformly mixed, in 1h, drip the H that 0.2KG mass concentration is 35% 2o 2the aqueous solution; At the uniform velocity stir, at 100 DEG C, react 20h; Reaction terminates, centrifugal, filters, and using the precipitation that obtains as stock, by fluid bed, can obtain a kind of inorganic mineral water treatment agent.
Embodiment 3 gained water treatment agent is added in certain steel ore deposit mine system engineering, this water treatment agent is joined in sewage by 5% of required water quality treatment amount.Before and after process, water quality index is as following table:
Cu(mg/L) Fe(mg/L) Cd(mg/L) Pb(mg/L) Zn(mg/L) As(mg/L) pH
Content before process 6294 26858 7 0.97 133 33 <1.5
Content after process Trace 0.01 Trace Trace Trace Trace 6.5
embodiment 4
1) 3KG chabasie and 3KG heulandite are mixed with the red pelelith of 3KG to be crushed to particle diameter be 50 μm, 3h is soaked through ethylenediamine tetra-acetic acid, with the salt acid elution that concentration is 6M/L, add hot reflux 8h, clean with distilled water again, dry 24h at 200 DEG C, and the Infrared irradiation 6h with wavelength being 750nm, be conducive to the formation of porous;
2) by 1KG flax and the abundant miniaturization of 1KG kapok, cross 2000 order molecular sieves, and ribbon length is 40 μm;
3) by 1) with 2) material Homogeneous phase mixing under 2MPa vacuum condition of gained, at Muffle furnace 1000 DEG C, calcine 5h, make 1) form fibrous porous structure in gained material, fiber multihole zeolite matrix is shaping;
4) by 3) material add volume for 3) step material cumulative volume 0.8 times deionized water in, then the 0.5KGFeCl added 2, be uniformly mixed, dripping 0.25KG mass concentration at 0.5h is the H of 35% 2o 2the aqueous solution; At the uniform velocity stir, at 80 DEG C, react 20h; Reaction terminates, centrifugal, filters, and using the precipitation that obtains as stock, by fluid bed, can obtain a kind of inorganic mineral water treatment agent.
embodiment 5
1) 15KG phillipsite and 15KG clinoptilolite are mixed with the red pelelith of 20KG to be crushed to particle diameter be 50 μm, 3h is soaked through ethylenediamine tetra-acetic acid, with the salt acid elution that concentration is 6M/L, add hot reflux 8h, clean with distilled water again, dry 24h at 180 DEG C, and the Infrared irradiation 6h with wavelength being 750nm, be conducive to the formation of porous;
2) by 6KG husk and the abundant miniaturization of 5KG kapok, cross 2000 order molecular sieves, and ribbon length is 35 μm;
3) by 1) with 2) material Homogeneous phase mixing under 2MPa vacuum condition of gained, at Muffle furnace 850 DEG C, calcine 8h, make 1) form fibrous porous structure in gained material, fiber multihole zeolite matrix is shaping;
By 3) material add volume for 3) step material cumulative volume 0.8 times deionized water in, then to add by 1.0KGFeSO 4and 0.8KGFeCl 2, be uniformly mixed, in 1.5h, drip the H that 1.5KG mass concentration is 35% 2o 2the aqueous solution; At the uniform velocity stir, at 100 DEG C, react 20h; Reaction terminates, centrifugal, filters, and using the precipitation that obtains as stock, by fluid bed, can obtain a kind of inorganic mineral water treatment agent.

Claims (6)

1. an inorganic mineral water treatment agent, is characterized in that weight portion consists of: 50-60 part natural zeolite, 25-30 part red pelelith, 8-15 part natural fiber, 3-4 part ferrous salt and 1-2 part mass concentration are the H of 35% 2o 2the aqueous solution forms, the at least one in analcime, phillipsite, sodalite, heulandite, clinoptilolite, chabasie, faujasite selected by wherein said natural zeolite, the at least one in husk, stalk, flax, kapok, sugarcane selected by described natural fiber, and described ferrous salt selects FeSO 4, FeCl 2in one.
2. according to a kind of inorganic mineral water treatment agent described in claim 1, it is characterized in that: described natural zeolite is faujasite.
3., according to a kind of inorganic mineral water treatment agent described in claim 1, it is characterized in that: described ferrous salt and H 2o 2mass ratio is m (Fe 2+)/m (H 2o 2)=8.
4. a preparation method for inorganic mineral water treatment agent, is characterized in that: carry out as follows:
1) 50-60 part natural zeolite and the mixing of 25-30 part pelelith are crushed to particle diameter≤50 μm, 2-5h is soaked through ethylenediamine tetra-acetic acid, be the salt acid elution of 6mol/L again by concentration, add hot reflux 8-10h, clean with distilled water, dry 24h at 60 ~ 200 DEG C, and the red light irradiation 3-6h with wavelength being 750nm, be conducive to the formation of porous;
2) by the abundant miniaturization of 8-15 part natural fiber mass, cross 2000 order molecular sieves, and ribbon length is less than 1) the middle particle diameter processing rear gained material;
3) by 1) with 2) material Homogeneous phase mixing under 1.5-2.5MPa vacuum condition of gained, natural fiber is made to enter into 1) the intragranular space of gained material, and 3h-8h is calcined at Muffle furnace 700-1000 DEG C, make 1) the fibrous porous structure of the interior formation of gained material, fiber multihole zeolite matrix is shaping;
4) by 3) gained material adds in deionized water, then adds 3-4 part ferrous salt, be uniformly mixed, and in 0.5h-1.5h, drip 1-2 part mass concentration is the H of 35% 2o 2the aqueous solution, at the uniform velocity stirs, at 40-100 DEG C, react 20h, and reaction terminates, centrifugal, filters, and using the precipitation that obtains as stock, by fluid bed, can obtain a kind of inorganic mineral water treatment agent.
5. according to the preparation method of a kind of inorganic mineral water treatment agent described in claim 4, it is characterized in that: in manufacturing process step 3), mixture is Homogeneous phase mixing in the de-airing mixer of 120r/min at rotating speed.
6. according to the preparation method of a kind of inorganic mineral water treatment agent described in claim 4, it is characterized in that: the deionized water volume added in step 4) in manufacturing process is 0.8-1.5 times of step 3) gained mass volume.
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CN104383897A (en) * 2014-10-31 2015-03-04 田琳琳 Adsorbing material for treating wastewater
CN104383896A (en) * 2014-10-31 2015-03-04 田琳琳 Composite material for purifying industrial waste water
CN106268662A (en) * 2016-08-25 2017-01-04 贵州万山兴隆锰业有限公司 A kind of manganese ore waste water adsorbing material and preparation method thereof
CN106396920A (en) * 2016-08-31 2017-02-15 华艺生态园林股份有限公司 Manufacture method of organic ground surface mulch for garden trees
CN111087199A (en) * 2019-12-20 2020-05-01 南通斐腾新材料科技有限公司 Preparation method of porous hollow zeolite particles for adsorbing VOCs (volatile organic compounds)
CN114471452B (en) * 2022-03-04 2023-09-08 太原碧蓝水利工程设计股份有限公司 Method for rapidly treating acidic mine pit water and adsorbent prepared from acidic mine pit water

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103641197A (en) * 2013-11-25 2014-03-19 大连创达技术交易市场有限公司 Composite filtering agent for purifying water

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US7314569B2 (en) * 2003-04-04 2008-01-01 Arrowhead Center, Inc. Treatment of arsenic-contaminated water using akaganeite adsorption

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103641197A (en) * 2013-11-25 2014-03-19 大连创达技术交易市场有限公司 Composite filtering agent for purifying water

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
路建美,等.实验室激光的安全使用与防护.《高等学校实验室环境健康与安全》.南京大学出版社,2013,第173页. *

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Inventor after: Chen Guosheng

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