CN105985087A - Phosphorus removal filler and method for preparing same - Google Patents
Phosphorus removal filler and method for preparing same Download PDFInfo
- Publication number
- CN105985087A CN105985087A CN201510553655.6A CN201510553655A CN105985087A CN 105985087 A CN105985087 A CN 105985087A CN 201510553655 A CN201510553655 A CN 201510553655A CN 105985087 A CN105985087 A CN 105985087A
- Authority
- CN
- China
- Prior art keywords
- filler
- phosphorus removal
- sodium hydroxide
- hydroxide solution
- gypsum
- 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
Landscapes
- Curing Cements, Concrete, And Artificial Stone (AREA)
- Processing Of Solid Wastes (AREA)
Abstract
The invention discloses a phosphorus removal filler. The phosphorus removal filler comprises, by weight, 40%-60% of fly ash, 20%-40% of cement, 10%-20% of quicklime, 1%-3% of gypsum, 2%-8% of amino functional high-polymer composite materials and the balance 70%-90% sodium hydroxide solution. A method for preparing the phosphorus removal filler includes uniformly mixing the fly ash, the cement, the quicklime, the gypsum and the amino functional high-polymer composite materials with one another to obtain first mixtures; adding the 70%-90% sodium hydroxide solution into the first mixtures, stirring the first mixtures and the 70%-90% sodium hydroxide solution and uniformly mixing the first mixtures and the 70%-90% sodium hydroxide solution with one another to obtain second mixtures; artificially manufacturing small spheres with the diameters of 5-8 mm from the second mixtures or manufacturing small spheres with the diameters of 5-8 mm from the second mixtures by the aid of a pill manufacturing machine; naturally drying the small spheres by the aid of air for 24 hours; curing the small spheres by the aid of steam at the temperature of 40 DEG C for 2 hours; heating the small spheres until the temperatures of the small spheres are increased by 10 DEG C at intervals of 30 min; curing the small spheres for 12 hours after the temperatures of the small spheres are increased and reach 80 DEG C to obtain the phosphorus removal filler. The phosphorus removal filler and the method have the advantages that the phosphorus removal filler is low in production cost and high in pollutant removal capacity, and phosphorus removal effects of the phosphorus removal filler are superior to phosphorus removal effects of other common phosphorus removal fillers by 10%.
Description
Technical field
The present invention relates to a kind of dephosphorization filler and preparation method thereof, belong to technical field of sewage.
Background technology
China is shortage of water resources country, with the quickening of expanding economy, urbanization process, urban water shortage
Problem is day by day serious, and the discharge of the crossbeam of municipal sewage has more increased the weight of this trend.Sewage disposal is preventing and treating
One of important means of water environment pollution, the selection of sewage treatment process can directly affect a regional water ring
Border quality.Biofilter, artificial swamp and fluidization etc. are the conventional skills being suitable for middle-size and small-size sewage disposal
Art, they are many with granular filler as biofilm carrier, and meanwhile, filler has again filtration concurrently and retains and separation of solid and liquid
Function, carrier performance is relatively big on the treatment efficiency of above-mentioned technique, construction costs and operating cost impact, because of
This, characteristic and the rationally selection thereof of filler are the key problems of biofilter, artificial swamp and fluidization
One of.
The key property of current water environment pollution is Organic Pollution and the eutrophication of water body, particularly with nitrogen,
The nutriments such as the phosphorus body eutrophication phenomenon causing that exceeds standard is day by day serious." urban wastewater treatment firm pollutant
Discharge standard " the content of nitrogen and phosphorous in institute of sewage treatment plant sewage effluent i.e. all made by (GB18918-2002)
Clear and definite regulation, this means that most cities sewage and Industrial Wastewater Treatment facility will fill from now on
Divide the denitrogenation dephosphorizing problem considering sewage.
As the core of the water processing establishments such as biofilter, artificial swamp and fluid bed, the selection of filler can be straight
Connect and affect its sewage disposal, especially the effect of denitrogenation dephosphorizing.
Content of the invention
For above-mentioned weak point of the prior art, it is desirable to provide a kind of dephosphorization filler and preparation thereof
Method, this filler combines with organic material with inorganic material, prepares and is applicable to artificial swamp, biological filter
The ecological water treatment facilities such as pond, production cost is low, contaminant removal capacity is strong, phosphor-removing effect is more common than other
Dephosphorization filler is high by more than 10%.
One aspect of the present invention, provides a kind of dephosphorization filler, and this filler is made up of following component, and this component is powder
Coal ash, cement, quick lime, gypsum, amino functional polymer composite, 70%~90% NaOH
Solution.
Further, the percetage by weight composition of this dephosphorization filler is: flyash 40%~60%, cement
20%~40%, quick lime 10%~20%, gypsum 1%~3%, amino functional polymer composite 2%~8%,
Remaining is 70%~90% sodium hydroxide solution.
Further, the percetage by weight composition of this dephosphorization filler is: flyash 45%~60%, cement
25%~40%, quick lime 12%~20%, gypsum 1.6%~3%, amino functional polymer composite 3.5%~
8%th, remaining is 70%~90% sodium hydroxide solution.
Further, the percetage by weight composition of this dephosphorization filler is: flyash 50%~60%, cement
30%~40%, quick lime 15%~20%, gypsum 2%~3%, amino functional polymer composite 5.2%~
8%th, remaining is 70%~90% sodium hydroxide solution.
Further, the percetage by weight composition of this dephosphorization filler is: flyash 55%~60%, cement
35%~40%, quick lime 18%~20%, gypsum 2.5%~3%, amino functional polymer composite 6.4%~
8%th, remaining is 70%~90% sodium hydroxide solution.
Another aspect of the present invention is to provide the preparation method of above-mentioned dephosphorization filler, and technical scheme is, by fine coal
Ash, cement, quick lime, gypsum, amino functional polymer composite uniformly mix, and add 70%~90%
After sodium hydroxide solution stirring is mixed, artificial or pelletization machine makes a diameter of 5~8mm bead, natural air drying 24
Hour, steam curing 2 hours at a temperature of 40 DEG C, heat up 10 DEG C at interval of 30min afterwards, until heating up
Thermostatic curing 12 hours again after 80 DEG C, obtain dephosphorization filler.
Beneficial effects of the present invention: combine with organic material with inorganic material, prepares and is applicable to Manual moist
The ecological water treatment facilities such as ground, biofilter, production cost is low, contaminant removal capacity is strong, phosphor-removing effect
Higher by more than 10% than other common dephosphorization filler.
Detailed description of the invention
Further describe the present invention below in conjunction with specific embodiment.
A kind of dephosphorization filler, described filler is by component flyash, cement, quick lime, gypsum, amino functional
Change polymer composite, 70%~90% sodium hydroxide solution composition.
Specifically, described dephosphorization filler percetage by weight composition is: flyash 40%~60%, cement 20%~
40%th, quick lime 10%~20%, gypsum 1%~3%, amino functional polymer composite 2%~8%, its
More than be 70%~90% sodium hydroxide solution.
Or further, described filler weight percentage composition is: flyash 45%~60%, cement
25%~40%, quick lime 12%~20%, gypsum 1.6%~3%, amino functional polymer composite 3.5%~
8%th, remaining is 70%~90% sodium hydroxide solution.
Or further, described filler weight percentage composition is: flyash 50%~60%, cement
30%~40%, quick lime 15%~20%, gypsum 2%~3%, amino functional polymer composite 5.2%~
8%th, remaining is 70%~90% sodium hydroxide solution.
Or further, described filler weight percentage composition is: flyash 55%~60%, cement
35%~40%, quick lime 18%~20%, gypsum 2.5%~3%, amino functional polymer composite 6.4%~
8%th, remaining is 70%~90% sodium hydroxide solution.
The preparation method of above-mentioned dephosphorization filler is as follows, by flyash, cement, quick lime, gypsum, amino work(
Polymer composite weight percent proportioning can be changed uniformly mix, add 70%~90% sodium hydroxide solution
After stirring is mixed, a diameter of 5~8mm bead made by artificial or pelletization machine, and natural air drying 24 hours, 40
Steam curing 2 hours at a temperature of DEG C, heat up 10 DEG C at interval of 30min afterwards, until after being warming up to 80 DEG C again
Thermostatic curing 12 hours, obtains dephosphorization filler.
The dephosphorization material of the present invention is made with tradition inorganic material such as flyash, cement, quick lime, gypsum
Become common dephosphorization filler Experimental Comparison, respectively with distilled water configuration concentration be 0.5mg/L, 1mg/L, 3mg/L,
The phosphate solution of 5mg/L, 8mg/L, 10mg/L, weighs common dephosphorization filler and dephosphorization filler of the present invention is each
5g, is respectively placed in the phosphate solution that 100mL configures, and after concussion is reacted 1 hour, takes supernatant and measures
Residue phosphate concn, calculates clearance, and experimental result is as shown in the table.
Can be apparent from by upper table Data Comparison, the phosphor-removing effect of the dephosphorization filler of the present invention is significantly better than tradition
The phosphor-removing effect of common dephosphorization filler.
Outfit for dephosphorization filler:
Embodiment 1: by 60g flyash, 34g cement, 16g quick lime, 1.9g gypsum, 2.7g amino work(
Can change after polymer composite uniformly mixes, add 70%~90% sodium hydroxide solution 28mL stirring and be mixed,
Making a diameter of 5~8mm bead by artificial or pelletization machine, natural air drying 24 hours, at a temperature of 40 DEG C
Steam curing 2 hours, heats up 10 DEG C at interval of 30min afterwards, until thermostatic curing again after being warming up to 80 DEG C
12 hours, obtain dephosphorization filler.
Embodiment 2: by 45g flyash, 28g cement, 13g quick lime, 2.7g gypsum, 5.4g amino work(
Can change after polymer composite uniformly mixes, add 70%~90% sodium hydroxide solution 25mL stirring and be mixed,
Making a diameter of 5~8mm bead by artificial or pelletization machine, natural air drying 24 hours, at a temperature of 40 DEG C
Steam curing 2 hours, heats up 10 DEG C at interval of 30min afterwards, until thermostatic curing again after being warming up to 80 DEG C
12 hours, obtain dephosphorization filler.
Embodiment 3: by 35g flyash, 23g cement, 9g quick lime, 1.4g gypsum, 2.6g amino work(
Can change after polymer composite uniformly mixes, add 70%~90% sodium hydroxide solution 25mL stirring and be mixed,
Making a diameter of 5~8mm bead by artificial or pelletization machine, natural air drying 24 hours, at a temperature of 40 DEG C
Steam curing 2 hours, heats up 10 DEG C at interval of 30min afterwards, until thermostatic curing again after being warming up to 80 DEG C
12 hours, obtain dephosphorization filler.
Embodiment 4: by 78g flyash, 44g cement, 26g quick lime, 3.9g gypsum, 7.6g amino work(
Can change after polymer composite uniformly mixes, add 70%~90% sodium hydroxide solution 25mL stirring and be mixed,
Making a diameter of 5~8mm bead by artificial or pelletization machine, natural air drying 24 hours, at a temperature of 40 DEG C
Steam curing 2 hours, heats up 10 DEG C at interval of 30min afterwards, until thermostatic curing again after being warming up to 80 DEG C
12 hours, obtain dephosphorization filler.
The technical scheme being provided the embodiment of the present invention above is described in detail, tool used herein
Principle and embodiment to the embodiment of the present invention for body the example is set forth, and the explanation of above example is only
It is adapted to assist in understanding the principle of the embodiment of the present invention;Simultaneously for one of ordinary skill in the art, depend on
According to the embodiment of the present invention, detailed description of the invention and range of application all will change, in sum,
This specification content should not be construed as limitation of the present invention.
Claims (6)
1. a dephosphorization filler, it is characterised in that described filler is made up of following component, this component is fine coal
Ash, cement, quick lime, gypsum, amino functional polymer composite, 70%~90% NaOH are molten
Liquid.
2. a kind of dephosphorization filler according to claim 1, it is characterised in that described filler weight percentage
Number compositions are: flyash 40%~60%, cement 20%~40%, quick lime 10%~20%, gypsum 1%~
3%th, amino functional polymer composite 2%~8%, remaining be 70%~90% sodium hydroxide solution.
3. a kind of dephosphorization filler according to claim 2, it is characterised in that: described filler weight percentage
Number compositions are: flyash 45%~60%, cement 25%~40%, quick lime 12%~20%, gypsum 1.6%~
3%th, amino functional polymer composite 3.5%~8%, remaining be 70%~90% sodium hydroxide solution.
4. a kind of dephosphorization filler according to claim 2, it is characterised in that: described filler weight percentage
Number compositions are: flyash 50%~60%, cement 30%~40%, quick lime 15%~20%, gypsum 2%~
3%th, amino functional polymer composite 5.2%~8%, remaining be 70%~90% sodium hydroxide solution.
5. a kind of dephosphorization filler according to claim 2, it is characterised in that: described filler weight percentage
Number compositions are: flyash 55%~60%, cement 35%~40%, quick lime 18%~20%, gypsum 2.5%~
3%th, amino functional polymer composite 6.4%~8%, remaining be 70%~90% sodium hydroxide solution.
6. the preparation method according to the arbitrary described dephosphorization filler of claim 1-5, it is characterised in that will
Flyash, cement, quick lime, gypsum, amino functional polymer composite uniformly mix, add 70%~
After 90% sodium hydroxide solution stirring is mixed, artificial or pelletization machine makes a diameter of 5~8mm bead, natural wind
Dry 24 hours, steam curing 2 hours at a temperature of 40 DEG C, heat up 10 DEG C at interval of 30min afterwards, directly
To thermostatic curing 12 hours again after being warming up to 80 DEG C, obtain dephosphorization filler.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201510553655.6A CN105985087B (en) | 2015-09-02 | 2015-09-02 | A kind of dephosphorization filler and preparation method thereof |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201510553655.6A CN105985087B (en) | 2015-09-02 | 2015-09-02 | A kind of dephosphorization filler and preparation method thereof |
Publications (2)
Publication Number | Publication Date |
---|---|
CN105985087A true CN105985087A (en) | 2016-10-05 |
CN105985087B CN105985087B (en) | 2018-06-29 |
Family
ID=57040653
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201510553655.6A Active CN105985087B (en) | 2015-09-02 | 2015-09-02 | A kind of dephosphorization filler and preparation method thereof |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN105985087B (en) |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN108298679A (en) * | 2018-03-31 | 2018-07-20 | 信阳华电环保工程技术有限公司 | A kind of low-density denitrogenation dephosphorizing filler and preparation method thereof |
CN110498659A (en) * | 2019-08-30 | 2019-11-26 | 杭州沁霖生态科技有限公司 | A kind of lightweight dephosphorization granule filter material and preparation method thereof |
CN110548477A (en) * | 2018-05-30 | 2019-12-10 | 中国科学院过程工程研究所 | Adsorbing material and preparation method and application thereof |
Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101367573A (en) * | 2008-09-08 | 2009-02-18 | 贾祥波 | Compound for wastewater treatment |
CN202099163U (en) * | 2011-05-26 | 2012-01-04 | 上海交通大学 | Combined layering biological filter for sewage treatment |
CN103739058A (en) * | 2014-01-06 | 2014-04-23 | 上海交通大学 | Sewage reinforced phosphorous removal packing and preparation method thereof |
-
2015
- 2015-09-02 CN CN201510553655.6A patent/CN105985087B/en active Active
Patent Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101367573A (en) * | 2008-09-08 | 2009-02-18 | 贾祥波 | Compound for wastewater treatment |
CN202099163U (en) * | 2011-05-26 | 2012-01-04 | 上海交通大学 | Combined layering biological filter for sewage treatment |
CN103739058A (en) * | 2014-01-06 | 2014-04-23 | 上海交通大学 | Sewage reinforced phosphorous removal packing and preparation method thereof |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN108298679A (en) * | 2018-03-31 | 2018-07-20 | 信阳华电环保工程技术有限公司 | A kind of low-density denitrogenation dephosphorizing filler and preparation method thereof |
CN110548477A (en) * | 2018-05-30 | 2019-12-10 | 中国科学院过程工程研究所 | Adsorbing material and preparation method and application thereof |
CN110548477B (en) * | 2018-05-30 | 2020-11-10 | 中国科学院过程工程研究所 | Adsorbing material and preparation method and application thereof |
CN110498659A (en) * | 2019-08-30 | 2019-11-26 | 杭州沁霖生态科技有限公司 | A kind of lightweight dephosphorization granule filter material and preparation method thereof |
Also Published As
Publication number | Publication date |
---|---|
CN105985087B (en) | 2018-06-29 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN1150975C (en) | Spherical porous light haydite for treating waste water and its production method | |
CN101935195B (en) | Porous phosphorus removing ceramic granules with function of slowly releasing alkali and preparation method thereof | |
Xu et al. | The utilization of lime-dried sludge as resource for producing cement | |
CN102765914B (en) | Building garbage baking-free brick or building block and preparation method thereof | |
CN102746023B (en) | Constructed wetland matrix filling material for simultaneous nitrogen and phosphorus removal and its preparation method | |
CN105692823A (en) | Environment-friendly efficient biological flocculant and preparing method thereof | |
CN105753279B (en) | A kind of silt/sludge solidifying agent and its application method | |
CN101560110B (en) | Spherical light porous material for wastewater treatment | |
CN101791534A (en) | Phosphorus-removing adsorbent and preparation method thereof | |
CN101891362A (en) | Process for curing and drying sludge | |
CN107902964A (en) | A kind of modification method for strengthening pervious concrete purifying property | |
CN101693185B (en) | Industrial salty slurry base composite dephosphorization material and preparation method thereof | |
CN105985087A (en) | Phosphorus removal filler and method for preparing same | |
CN101759245A (en) | Water purifying agent | |
CN102180607A (en) | Ultralight ceramsites and preparation method thereof | |
CN102351565A (en) | Method for preparing water treatment phosphorus accumulation filler by sintering with household garbage incineration residues | |
CN108865152A (en) | A kind of preparation method of contaminated soil remediation material | |
CN100500279C (en) | Denitrifying phosphorus-removing carrier and use | |
CN108996691A (en) | A kind of aluminium sludge compounded mix and preparation method thereof for artificial swamp | |
CN105126740B (en) | A kind of BIOLOGICAL CALCIUM type Phosphateadsorption porous material and preparation method thereof | |
KR100337084B1 (en) | method for manufacturing compost by using sewage sluge | |
CN105236707A (en) | Sewage treatment plant waste mud immobilization agent, and preparation method and application thereof | |
CN101670264A (en) | Desulfurized ash slag waste water dephosphorization materials prepared by baking-free method and preparation method | |
CN108414389A (en) | Ecological permeable concrete detergent power analysis method | |
CN105523641B (en) | The preparation method of microorganism compatibility water process light carrier |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
C06 | Publication | ||
PB01 | Publication | ||
C10 | Entry into substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
GR01 | Patent grant | ||
GR01 | Patent grant |