CN109354180A - Can biofilm anaerobic organism flora porous mineral particle and its preparation method and application - Google Patents

Can biofilm anaerobic organism flora porous mineral particle and its preparation method and application Download PDF

Info

Publication number
CN109354180A
CN109354180A CN201811346727.XA CN201811346727A CN109354180A CN 109354180 A CN109354180 A CN 109354180A CN 201811346727 A CN201811346727 A CN 201811346727A CN 109354180 A CN109354180 A CN 109354180A
Authority
CN
China
Prior art keywords
parts
porous mineral
weight
raw material
mineral particle
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.)
Pending
Application number
CN201811346727.XA
Other languages
Chinese (zh)
Inventor
杜玉成
靳翠鑫
王义成
李杨
牛炎
李生辉
谷恒学
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Jilin Jiapeng Diatomite Research And Development Co Ltd
Beijing University of Technology
Original Assignee
Jilin Jiapeng Diatomite Research And Development Co Ltd
Beijing University of Technology
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Jilin Jiapeng Diatomite Research And Development Co Ltd, Beijing University of Technology filed Critical Jilin Jiapeng Diatomite Research And Development Co Ltd
Priority to CN201811346727.XA priority Critical patent/CN109354180A/en
Publication of CN109354180A publication Critical patent/CN109354180A/en
Pending legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/28Anaerobic digestion processes
    • C02F3/2806Anaerobic processes using solid supports for microorganisms
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/32Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Microbiology (AREA)
  • Engineering & Computer Science (AREA)
  • Biodiversity & Conservation Biology (AREA)
  • Hydrology & Water Resources (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Biotechnology (AREA)
  • Botany (AREA)
  • Fertilizers (AREA)

Abstract

The present invention provides it is a kind of can biofilm anaerobic organism flora porous mineral particle and its preparation method and application.The porous mineral particle is by including that the raw material of following parts by weight is made: 30~70 parts of natural porous mineral, 1~15 part of sepiolite, 5~25 parts of bentonite and 5~20 parts of calcium hydroxide.The present invention is granulated by organically combining natural porous mineral and sepiolite, bentonite and calcium hydroxide, while making full use of natural porous mineral adsorpting characteristic, it can build the platform for being conducive to anaerobic organism bacterium and plant growth, to form the ecosystem of imitation the Nature water body purification.

Description

Can biofilm anaerobic organism flora porous mineral particle and its preparation method and application
Technical field
The present invention relates to water remediation agent field, more particularly, to it is a kind of can biofilm anaerobic organism flora porous mine Composition granule and its preparation method and application.
Background technique
The water-based pollution of the flowing such as river, lake, irrigation canals and ditches, fish pond (mostly with micro- pollution presentation) difficulty of governance is big, and main cause exists Wide in its drainage area, unpowered power supply is supported, some traditional waste water control methods is caused to be difficult to carry out.Such as aerobic biochemical process Aeration, physically or chemically the stirring in method and water body conveying, thickening filtration etc. need the process of power support;Even Conventional chemical method, since such water body is related to ecological, environmental protective problem, being also very limited, (some chemical agents are banned It only uses).Such water pollution improvement meets real needs, but lacks conventional effective method again at present.
Using simulation nature water natural purification process, as water by the filtering of soil Minerals, absorption, ion exchange, Bioconversion, root system of plant absorption etc., are a good directions.Because it does not need power consumption and the pollution of non-generation environment, It is very suitable to such water pollution improvement, in recent years by the concern of environmental protection industry (epi) and researcher, especially anaerobic organism bacterium Biological einforcement method cooperates adsorption filtration method again, has small-scale application, and have better effects.But there is also some problems, one It is that current water is very easy to lead to the loss of anaerobic organism bacterium, can not ensure anaerobic organism bacteria concentration or quantity, thus seriously Influence regulation effect;The second is anaerobic organism bacterium after pollutant, can generate sludge simultaneously, can not remove in time in consumption water body Processing, equally will cause secondary pollution.It can be floated in water body using natural porous clay minerals particle modularization assembling Carrier nest come cultivate anaerobic organism bacterium flora, it can be achieved that energy free consumption biological reinforced system for handling, while in clay class Mineral surfaces cultivate water plant, and (pollutant is also plant to the subsequent pollutant dissolved for organism-absorbing bacterium simultaneously Nutrients), and above-mentioned ask can be effectively solved using the characterization of adsorption of porous mineral come suspended contaminant in purifying water body (SS) Topic.But key problem in technology is natural porous clay minerals particle preparation, because of adobe mineral (such as diatomite, bentonite, boiling Stone etc.), mostly ultra-fine powder (fineness be 1~30 micron, μm), the poly- accumulation body of formation, seepage of water is poor;Also it is unfavorable for simultaneously The attachment of biological bacteria.
Summary of the invention
The first object of the present invention be to provide it is a kind of can biofilm anaerobic organism flora porous mineral particle, the porous mine Composition granule is by including that the raw material of following parts by weight is made: 30~70 parts of natural porous mineral, 1~15 part of sepiolite, bentonite 5~ 25 parts and 5~20 parts of calcium hydroxide.
The present invention is granulated by organically combining natural porous mineral and sepiolite, bentonite and calcium hydroxide, abundant While using natural porous mineral adsorpting characteristic, the platform for being conducive to anaerobic organism bacterium and plant growth can build, To form the ecosystem of imitation the Nature water body purification.Wherein, other air hardening cementitious materials such as gypsum, cement are not Can be used for this invention, it is not suitable for requirement of the invention.
In a preferred embodiment of the invention, the porous mineral particle is by including that the raw material of following parts by weight is made: 30~65 parts of natural porous mineral, 5~15 parts of sepiolite, 10~25 parts of bentonite and 8~15 parts of calcium hydroxide.
In a preferred embodiment of the invention, natural porous mineral are diatomite and/or zeolite.I.e. in the present invention In, natural porous mineral can be diatomite, zeolite or the mixing of both diatomite and zeolite.Diatomite can be with bentonite and hydrogen Calcium oxide reacts the lasting stability to be formed with certain intensity and support particle in water body.
It further include the composite chemical fertilizer that can promote plant growth in the raw material in a preferred embodiment of the invention. In order to preferably be conducive to the growth of anaerobic organism bacterium and plant, more preferably, which is 1~5 parts by weight of calcium and magnesium potassium mineral fertilizer, preferably 1~3 parts by weight.
It further include 3~20 parts by weight of waterglass in a preferred embodiment of the invention, in the raw material, preferably 5 ~15 parts by weight.Wherein, more preferably, when natural porous mineral contains zeolite, it is preferably added to above-mentioned quality in the feed The waterglass of part, can provide intensity more preferably strength support.
In a preferred embodiment of the invention, in order to improve adsorption filtration function and water repelling property, porous mineral The diameter of particle is 5~20mm, preferably 10~15mm.
In a preferred embodiment of the invention, in order to make porous mineral particle better adapt to the life of pressure oxygen biological bacteria Long, the porous mineral particle is by including that the raw material of following parts by weight is made: 50~65 parts of diatomite, 5~15 parts of sepiolite, swelling 1~5 part of 10~20 parts of soil, 8~20 parts of calcium hydroxide and calcium and magnesium potassium mineral fertilizer.It is further preferably the porous mineral Grain is by including that the raw material of following parts by weight is made: 55~65 parts of diatomite, 5~10 parts of sepiolite, 15~20 parts of bentonite, hydrogen-oxygen Change 1~3 part of 10~15 parts of calcium and calcium and magnesium potassium mineral fertilizer.It is still more preferably that the porous mineral particle is by including as follows The raw material of parts by weight is made: 60~65 parts of diatomite, 5~8 parts of sepiolite, 15~18 parts of bentonite, 12~15 parts of calcium hydroxide With 1~3 part of calcium and magnesium potassium mineral fertilizer.
In a preferred embodiment of the invention, the porous mineral particle is by including that the raw material of following parts by weight is made: 40~50 parts of zeolite, 5~10 parts of sepiolite, 15~20 parts of bentonite, 10~15 parts of calcium hydroxide, calcium and magnesium potassium mineral fertilizer 1~3 Part and 10~15 parts of waterglass.
In a preferred embodiment of the invention, the porous mineral particle is by including that the raw material of following parts by weight is made: 40~50 parts of diatomite, 10~20 parts of zeolite, 5~10 parts of sepiolite, 10~20 parts of bentonite, 8~15 parts of calcium hydroxide, calcium and magnesium 1~3 part and 8~15 parts of waterglass of potassium mineral fertilizer.
In the present invention in a preferred embodiment, porous mineral particle is made by the raw material of above-mentioned parts by weight.
In the present invention, parts by weight can be the unit of weight well known in the art such as μ g, mg, g, kg, be also possible to it again Number, such as 1/10,1/100,10 times, 100 times.
Another object of the present invention is to provide the preparation method of above-mentioned porous mineral particle, which includes as follows Step:
Raw material is mixed evenly according to the ratio, adds water that slurry is made, is granulated, it is dry to get.
Wherein, when containing waterglass in raw material, drying temperature is until waterglass can harden.
A further object of the present invention is to provide above-mentioned porous mineral particles or above-mentioned preparation method in water body purification Using.
Natural porous mineral and sepiolite, bentonite and calcium hydroxide are innovatively organically combined and are granulated by the present invention, are obtained Porous ore particles surface have adsorption filtration function, water-resistance is good, can keep not dissipating for 4~6 months in water body;After drying There is certain air capacity in atmospheric environment;Surface energy band has positive charge in water body, i.e. surface shows electropositive;With can promote Plant root system development nutritional ingredient.Porous ore particles provided by the invention are making full use of natural porous mineral adsorpting characteristic While, it can build the platform for being conducive to anaerobic organism bacterium and plant growth, to form imitation the Nature water The ecosystem of body purification.
Detailed description of the invention
Fig. 1 is the material object tested using the porous mineral particle of the embodiment of the present invention 1 in anaerobic organism bacterium growth adaptability Figure.
Specific embodiment
With reference to embodiment, the embodiment of the present invention is furthur described in detail.Following embodiment is used for Illustrate the present invention, but is used to limit the scope of the invention incessantly.
The commercially available acquisition of raw material components used in the present invention, agents useful for same of the embodiment of the present invention are that chemistry is pure.
Embodiment 1
The present embodiment provides a kind of porous mineral particle, preparation method includes the following steps:
By diatomite 65%, sepiolite 5%, calcium and magnesium potassium mineral fertilizer 3%, bentonite 15%, calcium hydroxide 12% weight Percentage is measured, 500g powder material is prepared, and be mixed and causes uniformly, to add the stirring of 220g water that thick slurry is made, adopt It is granulated with screw extruder, and is cut into the small 30mm particle of length, be dried granulated under the conditions of 120 DEG C, done Sample carries out growing anaerobic organism flora porous mineral particle as culture of the invention after dry, as shown in Figure 1.
Material properties test and the test of anaerobic organism bacterium growth adaptability.
The specific test method is as follows for it:
Hold gas: being carried out by nitrogen adsorption desorption tester, in terms of every gram of material air capacity (micro- ml);Water-resistance: in water Accelerate stirring 48 hours in body, measures the degree of crushing of material and to turbidity caused by clear water;Surface electrical behavior: pass through ζ electricity Position instrument (electro kinetic potential instrument) tests current potential positive and negative values in its water.
Particulate samples are put into the glucose solution equipped with anaerobic organism bacterium by the test of anaerobic organism bacterium growth adaptability In, it places 14 days, stirring twice, tests its surface biological film growing state (how many or fine or not degree) daily.
Test result is as follows:
Hold gas: 8 micro- ml/g;Water-resistance: particle is without damaged, 48 hours water quality of stirring is limpid;Surface electrical behavior be+ 0.08mv;Anaerobic organism bacterium well-grown, as shown in Figure 1.
Embodiment 2
The present embodiment provides a kind of porous mineral particle, preparation method includes the following steps:
By diatomite 55%, sepiolite 9%, calcium and magnesium potassium mineral fertilizer 1%, bentonite 20%, calcium hydroxide 15% weight Percentage is measured, 500g powder material is prepared, and be mixed and causes uniformly, to add the stirring of 180g water that thick slurry is made, adopt It is granulated with screw extruder, and is cut into the small 30mm particle of length, be dried granulated under the conditions of 120 DEG C, done Sample carries out growing anaerobic organism flora porous mineral particle as culture of the invention after dry.
Material properties test and the test of anaerobic organism bacterium growth adaptability.
Test result is as follows:
Hold gas: 10 micro- ml/g;Water-resistance: particle is without damaged, 48 hours water quality of stirring is limpid;Surface electrical behavior be+ 0.12mv;Anaerobic organism bacterium well-grown.
Embodiment 3
The present embodiment provides a kind of porous mineral particle, preparation method includes the following steps:
By zeolite 50%, sepiolite 5%, calcium and magnesium potassium mineral fertilizer 3%, bentonite 15%, waterglass 12%, hydroxide The weight percent of calcium 15% prepares 500g powder material, and be mixed and cause uniformly, to add the stirring of 150g water to be made sticky Shape slurry, is granulated using screw extruder, and is cut into the small 30mm particle of length, by it is granulated under the conditions of 150 DEG C into Row drying, sample carries out growing anaerobic organism flora porous mineral particle as culture of the invention after drying.
Material properties test and the test of anaerobic organism bacterium growth adaptability.
Test result is as follows:
Hold gas: 5 micro- ml/g;Water-resistance: particle has a small amount of damaged but 48 hours water quality of stirring limpid;Surface electrical behavior be+ 0.01mv;The growth of anaerobic organism bacterium is poor.
Embodiment 4
The present embodiment provides a kind of porous mineral particle, preparation method includes the following steps:
By zeolite 40%, sepiolite 8%, calcium and magnesium potassium mineral fertilizer 2%, bentonite 20%, waterglass 15%, hydroxide The weight percent of calcium 15% prepares 500g powder material, and be mixed and cause uniformly, to add the stirring of 150g water to be made sticky Shape slurry, is granulated using screw extruder, and is cut into the small 30mm particle of length, by it is granulated under the conditions of 150 DEG C into Row drying, sample carries out growing anaerobic organism flora porous mineral particle as culture of the invention after drying.
Material properties test and the test of anaerobic organism bacterium growth adaptability.
Test result is as follows:
Hold gas: 5 micro- ml/g;Water-resistance: particle is without damaged, 48 hours water quality of stirring is limpid;Surface electrical behavior be+ 0.01mv;The growth of anaerobic organism bacterium is poor.
Embodiment 5
The present embodiment provides a kind of porous mineral particle, preparation method includes the following steps:
It is by diatomite 40%, zeolite 20%, sepiolite 8%, calcium and magnesium potassium mineral fertilizer 2%, bentonite 10%, waterglass 5%, the weight percent of calcium hydroxide 15% prepares 500g powder material, and be mixed and cause uniformly, 180g water to be added to stir Mixing is granulated at thick slurry using screw extruder, and is cut into the small 30mm particle of length, by granulated 150 It is dried under the conditions of DEG C, sample carries out growing anaerobic organism flora porous mineral particle as culture of the invention after drying.
Material properties test and the test of anaerobic organism bacterium growth adaptability.
Test result is as follows:
Hold gas: 8 micro- ml/g;Water-resistance: particle is without damaged, 48 hours water quality of stirring is limpid;Surface electrical behavior be+ 0.02mv;The growth of anaerobic organism bacterium is general.
Embodiment 6
The present embodiment provides a kind of porous mineral particle, preparation method includes the following steps:
It is by diatomite 50%, zeolite 10%, sepiolite 5%, calcium and magnesium potassium mineral fertilizer 1%, bentonite 14%, waterglass 8%, the weight percent of calcium hydroxide 12% prepares 500g powder material, and be mixed and cause uniformly, 200g water to be added to stir Mixing is granulated at thick slurry using screw extruder, and is cut into the small 30mm particle of length, by granulated 150 It is dried under the conditions of DEG C, sample carries out growing anaerobic organism flora porous mineral particle as culture of the invention after drying.
Material properties test and the test of anaerobic organism bacterium growth adaptability.
Test result is as follows:
Hold gas: 8 micro- ml/g;Water-resistance: particle is without damaged, 48 hours water quality of stirring is limpid;Surface electrical behavior be+ 0.02mv;The growth of anaerobic organism bacterium is preferable.
Finally, method of the invention is only preferable embodiment, it is not intended to limit the scope of the present invention.It is all Within the spirit and principles in the present invention, any modification, equivalent replacement, improvement and so on should be included in protection of the invention Within the scope of.

Claims (10)

1. one kind can biofilm anaerobic organism flora porous mineral particle, which is characterized in that by the raw material including following parts by weight It is made: 30~70 parts of natural porous mineral, 1~15 part of sepiolite, 5~25 parts of bentonite and 5~20 parts of calcium hydroxide.
2. porous mineral particle according to claim 1, which is characterized in that be made by the raw material for including following parts by weight: 30~65 parts of natural porous mineral, 5~15 parts of sepiolite, 10~25 parts of bentonite and 8~15 parts of calcium hydroxide.
3. porous mineral particle according to claim 1 or 2, which is characterized in that the natural porous mineral are diatomite And/or zeolite.
4. porous mineral particle according to any one of claim 1 to 3, which is characterized in that further include in the raw material 1~5 parts by weight of calcium and magnesium potassium mineral fertilizer, preferably 1~3 parts by weight.
5. porous mineral particle according to any one of claim 1 to 4, which is characterized in that further include in the raw material 3~20 parts by weight of waterglass, preferably 5~15 parts by weight.
6. porous mineral particle according to any one of claim 1 to 5, which is characterized in that the porous mineral particle Diameter be 5~20mm, preferably 10~15mm.
7. porous mineral particle according to any one of claim 1 to 6, which is characterized in that by including following parts by weight Raw material be made: 50~65 parts of diatomite, 5~15 parts of sepiolite, 10~20 parts of bentonite, 8~20 parts of calcium hydroxide and calcium and magnesium 1~5 part of potassium mineral fertilizer;It is further preferably to be made by the raw material for including following parts by weight: 55~65 parts of diatomite, sea 1~3 part of 5~10 parts of afrodite, 15~20 parts of bentonite, 10~15 parts of calcium hydroxide and calcium and magnesium potassium mineral fertilizer.
8. porous mineral particle according to any one of claim 1 to 7, which is characterized in that by including following parts by weight Raw material be made: 40~50 parts of zeolite, 5~10 parts of sepiolite, 15~20 parts of bentonite, 10~15 parts of calcium hydroxide, calcium and magnesium potassium 1~3 part and 10~15 parts of waterglass of mineral fertilizer;
And/or the raw material by including following parts by weight is made: 40~50 parts of diatomite, 10~20 parts of zeolite, sepiolite 5~10 Part, 10~20 parts of bentonite, 8~15 parts of calcium hydroxide, 1~3 part of calcium and magnesium potassium mineral fertilizer and 8~15 parts of waterglass.
9. the preparation method of porous mineral particle described in any item of the claim 1 to 8, which is characterized in that including walking as follows It is rapid:
Raw material is mixed evenly according to the ratio, adds water that slurry is made, is granulated, it is dry to get.
10. application of the porous mineral particle described in any item of the claim 1 to 8 in water body purification.
CN201811346727.XA 2018-11-13 2018-11-13 Can biofilm anaerobic organism flora porous mineral particle and its preparation method and application Pending CN109354180A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201811346727.XA CN109354180A (en) 2018-11-13 2018-11-13 Can biofilm anaerobic organism flora porous mineral particle and its preparation method and application

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201811346727.XA CN109354180A (en) 2018-11-13 2018-11-13 Can biofilm anaerobic organism flora porous mineral particle and its preparation method and application

Publications (1)

Publication Number Publication Date
CN109354180A true CN109354180A (en) 2019-02-19

Family

ID=65344808

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201811346727.XA Pending CN109354180A (en) 2018-11-13 2018-11-13 Can biofilm anaerobic organism flora porous mineral particle and its preparation method and application

Country Status (1)

Country Link
CN (1) CN109354180A (en)

Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1051384A (en) * 1990-12-10 1991-05-15 湖北省化学研究所 The sorbent material and the method for making thereof of protection speed change catalyzer
CN1587082A (en) * 2004-09-30 2005-03-02 北京工业大学 Composite natural micro porous material sewage treating agent
CN1883745A (en) * 2006-05-30 2006-12-27 许盛英 Natural mineral adsorption filtering agent
CN104176815A (en) * 2013-05-27 2014-12-03 青岛国强环保科技有限公司 High-efficiency industrial wastewater treating biological carrier
CN104176831A (en) * 2013-05-26 2014-12-03 青岛国强环保科技有限公司 Industrial-wastewater biological treatment adsorption filling material
CN104276806A (en) * 2013-07-08 2015-01-14 金松 Spherical calcium hydroxide and preparation method thereof
CN104692763A (en) * 2015-02-09 2015-06-10 中山大学 Cheap nutritional biological deodorization packing and preparation method thereof
CN106745690A (en) * 2016-12-15 2017-05-31 江门市海达水净化工程有限公司 A kind of biological carrier sewage treatment device
CN107841037A (en) * 2016-09-20 2018-03-27 河南智联寰宇知识产权运营有限公司 High adsorption polylactic acid composite biological membrane carrier materials and preparation method thereof

Patent Citations (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1051384A (en) * 1990-12-10 1991-05-15 湖北省化学研究所 The sorbent material and the method for making thereof of protection speed change catalyzer
CN1033430C (en) * 1990-12-10 1996-12-04 湖北省化学研究所 Absorbent for protection of catalyst and the prepn. method
CN1587082A (en) * 2004-09-30 2005-03-02 北京工业大学 Composite natural micro porous material sewage treating agent
CN1883745A (en) * 2006-05-30 2006-12-27 许盛英 Natural mineral adsorption filtering agent
CN100502999C (en) * 2006-05-30 2009-06-24 许盛英 Natural mineral adsorption filtering agent
CN104176831A (en) * 2013-05-26 2014-12-03 青岛国强环保科技有限公司 Industrial-wastewater biological treatment adsorption filling material
CN104176815A (en) * 2013-05-27 2014-12-03 青岛国强环保科技有限公司 High-efficiency industrial wastewater treating biological carrier
CN104276806A (en) * 2013-07-08 2015-01-14 金松 Spherical calcium hydroxide and preparation method thereof
CN104692763A (en) * 2015-02-09 2015-06-10 中山大学 Cheap nutritional biological deodorization packing and preparation method thereof
CN107841037A (en) * 2016-09-20 2018-03-27 河南智联寰宇知识产权运营有限公司 High adsorption polylactic acid composite biological membrane carrier materials and preparation method thereof
CN106745690A (en) * 2016-12-15 2017-05-31 江门市海达水净化工程有限公司 A kind of biological carrier sewage treatment device

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
王立久等: "《新型屋面材料》", 31 October 2012, 北京:中国建材工业出版社 *
郑水林等: "《非金属矿加工技术与应用手册》", 31 May 2005, 北京:冶金工业出版社 *

Similar Documents

Publication Publication Date Title
CN103820427B (en) The preparation method of microorganism purification of water quality microbial inoculum
CN102923927B (en) Contaminated water body bottom mud reoxygenation type repairing agent, preparation method and applications thereof
CN101880147B (en) Steel slag eco-concrete, steel slag eco-concrete product and preparation method thereof
CN103436519B (en) Composite microbial preparation for watershed bioremediation as well as preparation method and application thereof
CN106399176B (en) One Bacillus species and its application in terms of purifying water body
CN105238728B (en) It is a kind of for river black and odorous water administer complex microorganism preparations and preparation method, using and methods for using them
KR101438380B1 (en) Concrete block for purifying water
CN104478090A (en) Multi-channel efficient biological filler and preparation method and application thereof
CN102603359B (en) Coal ash biological filter material and preparation method thereof
CN107673558B (en) Black and odorous water body purification method
CN103951044A (en) Novel non-sintered biological stuffing rapid in biofilm formation and preparation method thereof
Doniyarov et al. Obtaining a new kind of organic fertilizer on the basis of low-grade phosphorite of Central Kyzylkum
CN102311935B (en) Controlled release microecological preparation for water quality improvement and preparation method thereof
JP4945742B2 (en) Bottom quality improving material and bottom quality improving method using the same
JP3175964B2 (en) Water environment improvement method and water environment improvement paint
CN109354180A (en) Can biofilm anaerobic organism flora porous mineral particle and its preparation method and application
CN107572658B (en) Synchronous algae-dissolving denitrification biological floating bed in-situ remediation method for landscape water body
KR101661133B1 (en) Bacteria for biomineralization and method for biomineralising using the same
CN105294051B (en) The preparation method and its device of microorganism coral sanded brick
JP2008049265A (en) Microorganism-carrying sintered compact for water purification and its manufacturing method, and method for water purification of water area using this sintered compact
CN114262128A (en) Black and odorous inland river treatment by combination of encapsulated microorganisms and composite functional minerals
Li et al. Activated sludge and other aerobic suspended culture processes
CN108101227B (en) Sewage treatment agent for solidifying carrier microorganism and preparation method thereof
Lanjewar et al. A Critical Review on Prospects and Challenges in “Conceptualization to Technology Transfer” for Nutrient Recovery from Municipal Wastewater
CN208454624U (en) A kind of river comprehensive treatment device

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
RJ01 Rejection of invention patent application after publication

Application publication date: 20190219

RJ01 Rejection of invention patent application after publication