CN102398936A - Composite preparation for inhibiting water blackening and smell and its preparation method and use method - Google Patents

Composite preparation for inhibiting water blackening and smell and its preparation method and use method Download PDF

Info

Publication number
CN102398936A
CN102398936A CN2010102816069A CN201010281606A CN102398936A CN 102398936 A CN102398936 A CN 102398936A CN 2010102816069 A CN2010102816069 A CN 2010102816069A CN 201010281606 A CN201010281606 A CN 201010281606A CN 102398936 A CN102398936 A CN 102398936A
Authority
CN
China
Prior art keywords
water
smell
preparation
blackening
compound
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
Application number
CN2010102816069A
Other languages
Chinese (zh)
Other versions
CN102398936B (en
Inventor
王慧
柏学凯
宁大亮
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.)
Tsinghua University
Original Assignee
Tsinghua University
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 Tsinghua University filed Critical Tsinghua University
Priority to CN201010281606.9A priority Critical patent/CN102398936B/en
Publication of CN102398936A publication Critical patent/CN102398936A/en
Application granted granted Critical
Publication of CN102398936B publication Critical patent/CN102398936B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A20/00Water conservation; Efficient water supply; Efficient water use
    • Y02A20/40Protecting water resources
    • Y02A20/402River restoration

Landscapes

  • Water Treatment By Sorption (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)
  • Silicates, Zeolites, And Molecular Sieves (AREA)

Abstract

The invention discloses a composite preparation for inhibiting water blackening and smell and its preparation method and use method. The composite preparation for inhibiting water blackening and smell comprises: by mass, 70 to 90% of zeolite powder and 10 to 30% of a substance A, wherein the substance A is selected from calcium peroxide, sodium peroxocarbonate or calcium nitrate. The preparation method comprises the following steps of uniformly mixing the zeolite powder and the substance A according to the mass percentage, and carrying out machinery molding to obtain particles having sizes of 3 to 10mm. The use method comprises that the composite preparation for inhibiting water blackening and smell is uniformly added into a water environment, wherein an addition amount of the composite preparation for inhibiting water blackening and smell is in a range of 0.5 to 2kg/m<2>. The composite preparation for inhibiting water blackening and smell has a low preparation cost, good use effects, and can be utilized for restoration of polluted rivers, polluted lakes and landscape water. When the composite preparation for inhibiting water blackening and smell is put into water, the composite preparation for inhibiting water blackening and smell is fast settled to a bottom and is dispersed uniformly, and thus a bottom dissolved oxygen amount is effectively increased and the contents of ammonia nitrogen, hydrogen sulfide, ferrous sulfide and organic matters in water are reduced, so that water blackening and smell is inhibited and a water bottom ecological environment is improved.

Description

A kind of black smelly compound and preparation and method of use of water body that suppress
Technical field
The invention belongs to water environment pollution control techniques field, be specifically related to a kind of black smelly compound and preparation and method of use of water body that suppress.
Background technology
A large amount of trade effluents, the unprocessed water body that just enters of sewage have caused water quality deterioration, and dissolved oxygen concentration reduces, even approach exhaustion.Under anaerobic; Organism in water body and the bed mud can be produced black deposits such as Iron sulfuret in the process of anaerobic digestion; Produce foul gass such as hydrogen sulfide, ammonia simultaneously; Black deposit can cause water body black smelly under the supporting of foul gas is stirred when serious, the self function is lost basically.In China, southern area especially, the black smelly phenomenon of water body is comparatively general.How suppressing black smelly, the recovery self function of water body effectively, is one of content that needs to be resolved hurrily in the water environment pollution control.
The black smelly technology of inhibition water body commonly used comprises bed mud dredging, biological prosthetic, artificial aeration etc.The bed mud dredging is controlled through the polluted bed mud of excavating the top layer and is reduced black smelly source, but bed mud dredging technology quantities is big, and cost is high, can cause certain destruction to water ecosystem, and the engineering Failure cases also has appears in the newspapers.Mikrobe preparation for repairing cost is high, and the quality guaranteed period is short, and effect slowly also receives the water surrounding condition restriction, is difficult to use on a large scale; The phytoremediation growth cycle is long, needs regularly harvesting, and actual effect is not obvious.The artificial aeration can increase oxygen in water content fast, and water body is black smellyly to have better effects to suppressing, but this technical costs is higher, and oxygen transfer efficiency is lower, also possibly cause on the bed mud when using in the shoaling water and turn over, and discharges certain pollutent.Therefore, development and operation convenient, with low cost, use widely the black smelly inhibition technology of water body to have the important engineering meaning.
Summary of the invention
The object of the invention is to overcome the prior art deficiency, and a kind of dissolved oxygen, the black smelly compound of inhibition water body and preparation method thereof and method of use of increasing is provided.
Inhibition water body provided by the present invention is deceived smelly compound, is that the zeolite powder of 70%-90% and the A material of 10%-30% are formed by the quality percentage composition; Wherein, said A material be selected from following any one: calcium superoxide, sodium carbonate peroxide and nitrocalcite.
Said compound exists with the particulate form, and said particle grain size is preferably 3-10mm.
The preparation method of compound provided by the present invention comprises the steps: zeolite powder and the said A material ratio mixing according to mass ratio 70-90: 10-30, processes the particle that particle diameter is 3-10mm through mechanical-moulded, promptly obtains said compound; Wherein, said A material be selected from following any one: calcium superoxide, sodium carbonate peroxide, nitrocalcite.
The method of use of compound provided by the present invention is that said compound is evenly thrown to the lake water environment of river, and dosage is 0.5-2kg/m 2
The characteristic of active principle among the present invention:
Zeolite powder: zeolite powder is to form by natural zeolite is levigate.Zeolite is the aluminium silicate mineral of a kind of shape structure forming of slag, is mostly pearl, and present known zeolite has kind more than 40, be used for natural zeolite that water surrounding handles main be clinoptilolite.Flourishing hole, duct are arranged in the zeolite framework, and the passage through opening between the hole is connected with each other, and links up with the external world.The volume of hole and passage generally accounts for more than 50% of its crystal volume in the zeolite; Therefore zeolite has bigger specific surface area; Has absorption property preferably; And be a kind of selection absorption of molecular sieve, strong and molecular diameter has very strong adsorptivity less than the ammonia nitrogen of zeolite cavities channel diameter to polarity.In addition, the molecular structure basis of zeolite is silicon (aluminium) oxygen tetrahedron, the silicon in the silicon-oxy tetrahedron; Can be constituted aluminum-oxygen tetrahedron by the aluminium atomic substitutions, because the aluminium atom is tervalent, so there is the electricity price of a Sauerstoffatom not obtain neutralization in the aluminum-oxygen tetrahedron; Make whole aluminum-oxygen tetrahedron electronegative, offset by positive charges such as potassium ion, sodium ion, calcium ion, mg ions, and these positively charged ions and tetrahedron bonded are more weak; Can carry out cationic exchange; But do not destroy zeolite crystal structure, therefore, zeolite has ion-exchange performance.Natural zeolite also has the molecular sieve effect to air, when dropping into zeolite in the water, also brings air in the water into, and they discharge with the form of microbubble, increased the dissolved oxygen in the water, and the increase of dissolved oxygen help the removal of ammonia nitrogen and sulfide.In addition, zeolite also has certain adsorption effect to organism and heavy metal.Zeolite also contains hydrocoles and grows required whole major elements with most of micro-, and these elements all exist with ionic condition, can be utilized by hydrocoles.Qualified zeolite powder ammonia absorption value is generally greater than 100mg/100g, and zeolite powder used in the present invention confirms that than the choosing back specific surface area is big through multiple zeolite powder being carried out performance, and silica alumina ratio is low, and ammonia absorption value is up to 700mg/100g.
Calcium superoxide: chemical formula is CaO 2, molecular weight is 72.08, white or micro-yellow powder.Be slightly soluble in water, react slowly release of oxygen, increase oxygen in water content, improve redox potential, accelerate organic decomposition with water.Mikrobe tends to select electron acceptor(EA) with the redox potential size in the process of biodegrade, and the redox potential size order of electron acceptor(EA) is O 2>NO 3 ->SO 4 2->CO 2, under aerobic conditions, mikrobe can preferentially utilize O 2As electron acceptor(EA), avoid utilizing SO 4 2-Produce hydrogen sulfide as electron acceptor(EA), simultaneously the S in the material such as Iron sulfuret in water body and the bed mud 2-, Fe 2+By O 2Be oxidized to SO 4 2-, Fe 3+, stoped Fe 3+And SO 4 2-Minimizing, reduced Iron sulfuret content, thereby further cut down black smelly source.Calcium superoxide can also reduce ammonia-nitrogen content in the water through promoting nitrification.
Sodium carbonate peroxide: popular name SPC-D, chemical formula are 2Na 2CO 33H 2O 2, molecular weight is 314.02, white crystals or crystalline powder.Similar with calcium superoxide character, slow release of oxygen in water increases dissolved oxygen content, improves redox potential, reduces the generation of sulfide, accelerates organic decomposition, promotes nitrification, reduces ammonia-nitrogen content in the water.
Nitrocalcite: be commonly called as calcinitre, chemical formula is Ca (NO3) 2, molecular weight is 164.09, water white transparency monoclinic crystal or powder.In water surrounding, add nitrocalcite and can remove partial organic substances in water body and the bed mud through denitrification.In addition, mikrobe can preferentially utilize nitrate salt as electron acceptor(EA), avoids utilizing SO 4 2-Produce hydrogen sulfide as electron acceptor(EA), simultaneously the S in the material such as Iron sulfuret in water body and the bed mud 2-, Fe 2+By O 2Be oxidized to SO 4 2-, Fe 3+, stoped Fe 3+And SO 4 2-Minimizing, reduced Iron sulfuret content, thereby further cut down black smelly source.
Compound product provided by the present invention is the fine particle shape, and is easy to use, can sink to the bottom fast after evenly throwing to the water surrounding, is uniformly dispersed; Cost is low, and is effective, and medicament adds can effectively increase the bottom dissolved oxygen in the water body, reduces the content of ammonia nitrogen, hydrogen sulfide, Iron sulfuret, organism etc. in the water body, suppresses the water body blackout and fouls, and improves water-bed ecotope.
Embodiment
The present invention will be described through specific embodiment below, but the present invention is not limited thereto.
Experimental technique described in the following embodiment like no specified otherwise, is ordinary method; Said reagent and material like no specified otherwise, all can obtain from commercial sources.
Embodiment 1, preparation suppress the black smelly compound of water body and the effect of processing water body thereof
Preparation suppresses the black smelly compound of water body:
Zeolite powder and nitrocalcite is even according to 70: 30 mixed of mass ratio, process the particle that particle diameter is 3-10mm through mechanical-moulded, promptly get said compound.
Utilize above-mentioned compound to handle water body:
Certain detention type river course, city, owing to trade effluent, sewage etc. enter for a long time in a large number, water quality deterioration, the black smelly phenomenon of water body is serious.Two zones selecting area adjacent in the river course to equate, surveying its dissolved oxygen concentration is 0.41mg/L, surrounds with iron sheet respectively, is numbered 1,2, and wherein No. 1 is control zone, and No. 2 is pilot region.In No. 2 zones with 0.8kg/m 2Consumption add this compound.No. 2 regional dissolved oxygen concentrations rise to 1.03mg/L after 20 days, and the black smelly phenomenon of water body disappears, and No. 1 regional dissolved oxygen concentration is 0.17mg/L, and the black smelly phenomenon of water body is obvious.
Table 1 control zone with add the area monitoring index relatively
Figure BSA00000269485200031
(measuring method of each index carries out with reference to the method in the following document in the table 1: water and effluent monitoring analytical procedure [M]. Beijing: and the China Environmental Science Press, 2002. times are together)
Embodiment 2, preparation suppress the black smelly compound of water body and the effect of processing water body thereof
Preparation suppresses the black smelly compound of water body:
Zeolite powder and calcium superoxide is even according to 80: 20 mixed of mass ratio, process the particle that particle diameter is 3-10mm through mechanical-moulded, promptly get said compound.
Utilize above-mentioned compound to handle water body:
The small-sized man-made lake in certain city adopts sewage disposal plant effluent to supply with water as part, and water body does not have mobile basically, and dissolved oxygen concentration is lower than 0.5mg/L for a long time, and water body has obviously black smelly phenomenon.With 1kg/m 2Consumption add this compound.After 10 days, dissolved oxygen concentration rises to 1.83mg/L, and black smelly phenomenon disappears.
Monitoring index relatively before and after table 2 added
Embodiment 3, preparation suppress the black smelly compound of water body and the effect of processing water body thereof
Preparation suppresses the black smelly compound of water body:
Zeolite powder and sodium carbonate peroxide is even according to 90: 10 mixed of mass ratio, process the particle that particle diameter is 3-10mm through mechanical-moulded, promptly get said compound.
Utilize above-mentioned compound to handle water body:
Small-sized natural landscape lake, certain city is received dirty river course with this city one and is communicated, and water quality inferiority, dissolved oxygen concentration are lower than 1mg/L for a long time, and water body has black smelly phenomenon.After cutting the river course water inlet, with 1.2kg/m 2Consumption add this compound.After 10 days, dissolved oxygen concentration rises to 1.67mg/L, and black smelly phenomenon disappears.
Monitoring index relatively before and after table 3 added
Figure BSA00000269485200042
Figure BSA00000269485200051

Claims (6)

1. one kind is suppressed the black smelly compound of water body, is that the zeolite powder of 70%-90% and the A material of 10%-30% are formed by the quality percentage composition; Wherein, said A material be selected from following any one: calcium superoxide, sodium carbonate peroxide and nitrocalcite.
2. compound according to claim 1 is characterized in that: said compound exists with particle form.
3. compound according to claim 2 is characterized in that: said particle grain size is 3-10mm.
4. the method for preparing the said compound of claim 1 comprises the steps: said zeolite powder and A material evenly according to the described mixed of claim 1, and the mechanical-moulded particle of processing promptly obtains said compound; Wherein, to be selected from following substances wherein a kind of for said A material: calcium superoxide, sodium carbonate peroxide, nitrocalcite.
5. method according to claim 4 is characterized in that: said particle grain size is 3-10mm.
6. the method for use of each said compound among the claim 1-3 is characterized in that: said compound is evenly thrown to the lake water environment of river, and dosage is 0.5-2kg/m 2
CN201010281606.9A 2010-09-13 2010-09-13 Composite preparation for inhibiting water blackening and smell and its preparation method and use method Expired - Fee Related CN102398936B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201010281606.9A CN102398936B (en) 2010-09-13 2010-09-13 Composite preparation for inhibiting water blackening and smell and its preparation method and use method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201010281606.9A CN102398936B (en) 2010-09-13 2010-09-13 Composite preparation for inhibiting water blackening and smell and its preparation method and use method

Publications (2)

Publication Number Publication Date
CN102398936A true CN102398936A (en) 2012-04-04
CN102398936B CN102398936B (en) 2014-11-26

Family

ID=45881650

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201010281606.9A Expired - Fee Related CN102398936B (en) 2010-09-13 2010-09-13 Composite preparation for inhibiting water blackening and smell and its preparation method and use method

Country Status (1)

Country Link
CN (1) CN102398936B (en)

Cited By (16)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104857930A (en) * 2015-05-14 2015-08-26 江苏玖力纳米材料科技有限公司 Method for producing special-purpose modified mineral materials for black-odor rivers
CN107051377A (en) * 2017-04-21 2017-08-18 同济大学 It is a kind of to be used for synchronous nano composite material for removing carbon nitrogen phosphorus and preparation method thereof
CN107285400A (en) * 2017-07-03 2017-10-24 安徽省黄淮兽药有限公司 A kind of improver of water quality and preparation method thereof
CN107445279A (en) * 2017-07-21 2017-12-08 西安建筑科技大学 Calper calcium peroxide is used to control the loss of landscape water body foul smell and the application of bed mud sediment upturning
CN107790099A (en) * 2017-11-08 2018-03-13 湖南新九方科技有限公司 A kind of sorbing material for being used for phosphorus and heavy metal-containing polluted water and preparation method thereof
CN108178276A (en) * 2016-12-08 2018-06-19 刘宫介 A kind of fishery substrate modifier and preparation method thereof
CN109534631A (en) * 2017-09-21 2019-03-29 天津大学 A kind of compound bed mud improver and preparation method thereof for administering black-odor riverway
CN109607664A (en) * 2018-12-20 2019-04-12 苏州科技大学 A kind of material and preparation method thereof of quick elimination black and odorous water
CN109607996A (en) * 2018-12-20 2019-04-12 苏州科技大学 Restorative zeolitic material of a kind of promotion bed mud and preparation method thereof
CN110104922A (en) * 2019-05-27 2019-08-09 北京恒通国盛环境管理有限公司 A kind of sediment in-situ biological curing repairs medicament and preparation method thereof
CN110589949A (en) * 2019-09-30 2019-12-20 扬州大学 Preparation method of slow-release oxygen agent for improving black and odorous water body
CN110981136A (en) * 2019-12-30 2020-04-10 江南大学 Method for in-situ remediation of river sediment by combination of powdered activated carbon and calcium peroxide
CN111892259A (en) * 2020-07-24 2020-11-06 中交第一公路勘察设计研究院有限公司 Method for inhibiting black and odorous bottom mud of river channel and composite medicament thereof
CN112592013A (en) * 2020-11-25 2021-04-02 武汉理工大学 Black odorous river sludge bottom modifying agent and preparation and use methods thereof
CN112939135A (en) * 2021-01-26 2021-06-11 南京乐透思环保科技有限公司 COD (chemical oxygen demand) and ammonia nitrogen remover for tail water treatment
CN114534686A (en) * 2022-03-01 2022-05-27 武汉理工大学 Black and odorous water body and bottom mud in-situ remediation agent as well as preparation method and application thereof

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1579150A (en) * 2004-04-26 2005-02-16 王同明 Preparation for aquatic product culturing industry and preparation method
CN1596631A (en) * 2004-07-21 2005-03-23 张南伟 Granular oxygenation agent for fish and shrimp and its preparation method
CN1850660A (en) * 2006-05-17 2006-10-25 天津生机集团有限公司 Improved composition of base of aquatic cultivation pool

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1579150A (en) * 2004-04-26 2005-02-16 王同明 Preparation for aquatic product culturing industry and preparation method
CN1596631A (en) * 2004-07-21 2005-03-23 张南伟 Granular oxygenation agent for fish and shrimp and its preparation method
CN1850660A (en) * 2006-05-17 2006-10-25 天津生机集团有限公司 Improved composition of base of aquatic cultivation pool

Cited By (18)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104857930A (en) * 2015-05-14 2015-08-26 江苏玖力纳米材料科技有限公司 Method for producing special-purpose modified mineral materials for black-odor rivers
CN108178276A (en) * 2016-12-08 2018-06-19 刘宫介 A kind of fishery substrate modifier and preparation method thereof
CN107051377B (en) * 2017-04-21 2019-09-27 同济大学 A kind of nanocomposite and preparation method thereof for synchronous removal carbon nitrogen phosphorus
CN107051377A (en) * 2017-04-21 2017-08-18 同济大学 It is a kind of to be used for synchronous nano composite material for removing carbon nitrogen phosphorus and preparation method thereof
CN107285400A (en) * 2017-07-03 2017-10-24 安徽省黄淮兽药有限公司 A kind of improver of water quality and preparation method thereof
CN107445279A (en) * 2017-07-21 2017-12-08 西安建筑科技大学 Calper calcium peroxide is used to control the loss of landscape water body foul smell and the application of bed mud sediment upturning
CN109534631A (en) * 2017-09-21 2019-03-29 天津大学 A kind of compound bed mud improver and preparation method thereof for administering black-odor riverway
CN107790099A (en) * 2017-11-08 2018-03-13 湖南新九方科技有限公司 A kind of sorbing material for being used for phosphorus and heavy metal-containing polluted water and preparation method thereof
CN107790099B (en) * 2017-11-08 2020-12-18 湖南新九方科技有限公司 Adsorbing material for phosphorus and heavy metal polluted water and preparation method thereof
CN109607996A (en) * 2018-12-20 2019-04-12 苏州科技大学 Restorative zeolitic material of a kind of promotion bed mud and preparation method thereof
CN109607664A (en) * 2018-12-20 2019-04-12 苏州科技大学 A kind of material and preparation method thereof of quick elimination black and odorous water
CN110104922A (en) * 2019-05-27 2019-08-09 北京恒通国盛环境管理有限公司 A kind of sediment in-situ biological curing repairs medicament and preparation method thereof
CN110589949A (en) * 2019-09-30 2019-12-20 扬州大学 Preparation method of slow-release oxygen agent for improving black and odorous water body
CN110981136A (en) * 2019-12-30 2020-04-10 江南大学 Method for in-situ remediation of river sediment by combination of powdered activated carbon and calcium peroxide
CN111892259A (en) * 2020-07-24 2020-11-06 中交第一公路勘察设计研究院有限公司 Method for inhibiting black and odorous bottom mud of river channel and composite medicament thereof
CN112592013A (en) * 2020-11-25 2021-04-02 武汉理工大学 Black odorous river sludge bottom modifying agent and preparation and use methods thereof
CN112939135A (en) * 2021-01-26 2021-06-11 南京乐透思环保科技有限公司 COD (chemical oxygen demand) and ammonia nitrogen remover for tail water treatment
CN114534686A (en) * 2022-03-01 2022-05-27 武汉理工大学 Black and odorous water body and bottom mud in-situ remediation agent as well as preparation method and application thereof

Also Published As

Publication number Publication date
CN102398936B (en) 2014-11-26

Similar Documents

Publication Publication Date Title
CN102398936B (en) Composite preparation for inhibiting water blackening and smell and its preparation method and use method
Deng et al. Application of biochar as an innovative substrate in constructed wetlands/biofilters for wastewater treatment: Performance and ecological benefits
Shu et al. An innovative method for synergistic stabilization/solidification of Mn2+, NH4+-N, PO43− and F− in electrolytic manganese residue and phosphogypsum
CN107176702B (en) Sewage treatment method for enhancing synchronous nitrogen and phosphorus removal in sulfur autotrophic denitrification process
CN103801254B (en) A kind of denitrogenation dephosphorizing material based on siderite and using method thereof
Huang et al. Ammonium removal from aqueous solutions by using natural Chinese (Chende) zeolite as adsorbent
Lin et al. Process optimization of anammox-driven hydroxyapatite crystallization for simultaneous nitrogen removal and phosphorus recovery
CN112592013B (en) Black odorous river sludge bottom modifying agent and preparation and use methods thereof
CN101412547B (en) Mineral composite material for removing lake endogenous pollution and use thereof
CN102219233B (en) Method for removing nitrogen and phosphorus in sewage by zeolite synthesized by coal ash
Zhang et al. Phosphorus recovery from wastewater and sewage sludge as vivianite
CN102285740A (en) Non-waste treatment method for garbage leachate
CN109574233B (en) Artificial wetland system added with zeolite loaded nano zero-valent iron
CN108298679A (en) A kind of low-density denitrogenation dephosphorizing filler and preparation method thereof
CN105948695B (en) A kind of purposes of sewage purification material
Zhong et al. How to select substrate for alleviating clogging in the subsurface flow constructed wetland?
Lin et al. Ammonium removal from digested effluent of swine wastewater by using solid residue from magnesium-hydroxide flue gas desulfurization process
CN102399045A (en) Composite medicament for fixing nitrogen and phosphorous in riverbed sludge, and preparation and application method thereof
CN101544456A (en) Composite material for reducing greenhouse gases discharge and application thereof
Si et al. Nitrate removal to its fate in wetland mesocosm filled with sponge iron: Impact of influent COD/N ratio
Kamarzamann et al. Hydroxyapatite/Dolomite alkaline activated material reaction in the formation of low temperature sintered ceramic as adsorbent materials
Ou et al. Removal of ammonia nitrogen and phosphorus by porous slow-release Ca2+ ceramsite prepared from industrial solid wastes
CN111203173A (en) Phosphorus removal material based on collophanite tailings and preparation and application methods thereof
Wang et al. Vivianite recovery from high concentration phosphorus wastewater with mine drainage as iron sources
Wang et al. The competitive and selective adsorption of heavy metals by struvite in the Pb (II)-Cd (II)-Zn (II) composite system and its environmental significance

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant
EE01 Entry into force of recordation of patent licensing contract
EE01 Entry into force of recordation of patent licensing contract

Application publication date: 20120404

Assignee: SHANTOU HONGDONG ENVIRONMENT TREATMENT CO.,LTD.

Assignor: Tsinghua University

Contract record no.: 2018990000322

Denomination of invention: Composite preparation for inhibiting water blackening and smell and its preparation method and use method

Granted publication date: 20141126

License type: Exclusive License

Record date: 20181130

CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20141126