CN101508511A - Confervoid-biomembrane ecological treating system - Google Patents

Confervoid-biomembrane ecological treating system Download PDF

Info

Publication number
CN101508511A
CN101508511A CNA200910071593XA CN200910071593A CN101508511A CN 101508511 A CN101508511 A CN 101508511A CN A200910071593X A CNA200910071593X A CN A200910071593XA CN 200910071593 A CN200910071593 A CN 200910071593A CN 101508511 A CN101508511 A CN 101508511A
Authority
CN
China
Prior art keywords
oxidation pond
biomembrane
pool
confervoid
silk floss
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
CNA200910071593XA
Other languages
Chinese (zh)
Inventor
马军
雷国元
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.)
Harbin Institute of Technology
Original Assignee
Harbin Institute 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 Harbin Institute of Technology filed Critical Harbin Institute of Technology
Priority to CNA200910071593XA priority Critical patent/CN101508511A/en
Publication of CN101508511A publication Critical patent/CN101508511A/en
Pending legal-status Critical Current

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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

Landscapes

  • Biological Treatment Of Waste Water (AREA)

Abstract

The invention discloses a spirogyra-biomembrane ecological treatment system, and relates to a sewage treatment system. The invention solves the problems of high construction and operation cost and a low sewage advanced purification rate lying in the prior sewage treatment system. The spirogyra-biomembrane ecological treatment system consists of an oxidation pond and a culture pond, wherein the spirogyras and biomembranes are arranged in the oxidation pond; and the spirogyras are cultured in the culture pond. The method has high capability of removing nitrogen and phosphorus in the sewage, facilitates the advanced treatment of the sewage, has simple operation, and reduces the sewage treatment cost by 60 to 70 percent. Simultaneously the nitrogen and phosphorus enriched spirogyras can be used as fertilizers; therefore the system produces high economic efficiency.

Description

Confervoid-biomembrane ecological treating system
Technical field:
The present invention relates to a kind of Sewage treatment systems.
Background technology:
Along with the rapid raising of people's living standard and the acceleration of urbanization process, produced a large amount of sewage in the city and entered in the rivers, wherein nitrogen and phosphorus are seriously polluted, cause body eutrophication, water environment pollution serious day by day.At sewage treatment area, exist Sewage treatment systems at present and build and running cost high the problem that the advanced treatment of wastewater rate is low.
Summary of the invention:
The present invention builds and the running cost height in order to solve present Sewage treatment systems, and the problem that the advanced treatment of wastewater rate is low provides Confervoid-biomembrane ecological treating system.
Confervoid-biomembrane ecological treating system of the present invention is made up of the oxidation pond and the cultivation pool, be connected by pipeline between the oxidation pond and the cultivation pool, be furnished with the tender microbial film of water in the oxidation pond, the tender microbial film employing of water " on-down " combination, the water silk floss is arranged in waterborne of oxidation pond, and the water silk floss is fixed with the plastic grid support down, under plastic grid, vertically arrange microbial film, the water flow mode of oxidation pond goes out on advancing under being, cultivates to arrange in the pool and cultivate the water silk floss, and the water flow mode of cultivating the pool goes out on advancing under being.
The function of oxidation pond be purify waste water, enriched in nitrogen and phosphorus, the function of cultivating the pool is to cultivate the continuous and advanced treatment water body once more of the required water of oxidation pond.
Spirogyra can be fixed by the plastic grid support in large-scale thread living algae, is difficult for running off.
The water silk floss has good stain resistance and environmental compatibility.
Because the water silk floss consumes carbonic acid gas and discharges oxygen in process of growth, can provide oxygen for microbial film, strengthen the biological degradation of aerobic microbiological on the microbial film, reach sewage is carried out the advanced treatment purpose.The microbial film degradation of contaminant does not need aeration in the Confervoid-biomembrane ecological treating system of the present invention, reduces cost of sewage disposal 60%~70%, compares with conventional oxidation pond technology, does not need that secondary is carried out in water outlet and removes the algae processing, is beneficial to the advanced treatment of sewage.
Confervoid-biomembrane ecological treating system only is made up of the oxidation pond and the cultivation pool, and laid down cost is low.
In addition, the water silk floss also has the growth of the microalgae cell of inhibition, reduces the physiologically active of microalgae cell, can suppress the growth of miniature algae in the water body when disposing of sewage.
Description of drawings
Fig. 1 is the Confervoid-biomembrane ecological treating system structure iron.
Embodiment:
Embodiment one: describe in conjunction with Fig. 1, the present embodiment Confervoid-biomembrane ecological treating system is made up of the oxidation pond 5 and the cultivation pool 1, be connected by pipeline 6 between the oxidation pond 5 and the cultivation pool 1, be furnished with water continuous 2 and microbial film 4 in the oxidation pond 5, water continuous 2 and microbial film 4 employings " on-down " combination, water silk floss 2 is arranged in waterborne of oxidation pond 5, water is fixed with plastic grid 3 supports for continuous 2 times, vertically arrange microbial film 43 times at plastic grid, the water flow mode of oxidation pond 5 goes out on advancing under being, cultivate and to arrange in the pool 1 and cultivate water silk floss 2, the water flow mode of cultivating the pool 1 goes out on advancing under being.
Embodiment two: what present embodiment and embodiment one were different is: oxidation pond 5 degree of depth are 0.5~1.2 meter, the density of water silk floss 2 is 0.5~5g/L in the oxidation pond 5, plastic grid 3 bottoms are apart from 20~30 centimetres of the waters surface, microbial film 4 is a carrier with the inert fiber, and the volume of carrier is oxidation pond 5 volumetrical 1%~20%.It is identical with embodiment one that other forms structure.
Inert fiber quality softness in the present embodiment.
Embodiment three: what present embodiment was different with embodiment one or two is: the density of water silk floss 2 is 0.8~4.5g/L in the oxidation pond 5.It is identical with embodiment one or two that other forms structure.
Embodiment four: what present embodiment was different with embodiment one or two is: the concentration of water silk floss 2 is 0.5g/L in the oxidation pond 5.It is identical with embodiment one or two that other forms structure.
Embodiment five: what present embodiment was different with embodiment one or two is: the concentration of water silk floss 2 is 5g/L in the oxidation pond 5.It is identical with embodiment one or two that other forms structure.
Embodiment six: what present embodiment was different with embodiment one or two is: the concentration of water silk floss 2 is 4g/L in the oxidation pond 5.It is identical with embodiment one or two that other forms structure.
Embodiment seven: what present embodiment was different with embodiment one or two is: the volume of carrier is oxidation pond 5 volumetrical 15%.It is identical with embodiment one or two that other forms structure.
Embodiment eight: what this embodiment was different with embodiment one or two is: oxidation pond 5 degree of depth of Confervoid-biomembrane ecological treating system are 0.8 meter, the concentration of water silk floss 2 is 4g/L in the oxidation pond 5, water silk floss-biomembranous array mode can adopt " on-down " combination, water silk floss 2 is covered with oxidation pond 5 waters surface, it is fixed with plastic grid 3 supports down, vertically arrange fixed biofilms 4 plastic grid 3 times, microbial film 4 is that the soft inert fiber of oxidation pond 5 volumes 15% is a carrier with the volume.It is identical with embodiment one or two that other forms structure.
Embodiment nine: what present embodiment and embodiment one were different is: cultivating the pool 1 degree of depth is 0.3~0.7 meter, the concentration of cultivating total phosphorus in the pool 1 is 1.0~1.5mg/L, the pH value is 6~8, the volume of cultivating the pool 1 is oxidation pond 5 volumetrical 20%~50%, hydraulic detention time 2~7 days.It is identical with embodiment one that other forms structure.
Present embodiment can enter by adjustment and cultivate in the pool ratio of sewage and oxidation pond water outlet and control and cultivate that total phosphorus concentration is 1.0~1.5mg/L in the pool.
Embodiment ten: what present embodiment was different with embodiment one or nine is: the volume of cultivating the pool 1 is oxidation pond 5 volumetrical 25%~45%.It is identical with embodiment one or nine that other forms structure.
Embodiment 11: what present embodiment was different with embodiment one or nine is: the volume of cultivating the pool 1 is oxidation pond 5 volumetrical 20%.It is identical with embodiment one or nine that other forms structure.
Embodiment 12: what present embodiment was different with embodiment one or nine is: the volume of cultivating the pool 1 is oxidation pond 5 volumetrical 50%.It is identical with embodiment one or nine that other forms structure.
Embodiment 14: what present embodiment was different with embodiment one or nine is: the volume of cultivating the pool 1 is oxidation pond 5 volumetrical 30%.It is identical with embodiment one or nine that other forms structure.
Embodiment 15: what this concrete mode was different with embodiment one or nine is: the cultivation pool 1 degree of depth of water silk floss-microbial film 4 ecological treatment systems is 0.5 meter, the pH value of cultivating water in the pool 1 is 6~8, the volume size of cultivating the pool 1 is oxidation pond 5 volumetrical 30%, hydraulic detention time 2~7 days.It is identical with embodiment one or nine that other forms structure.

Claims (8)

1, Confervoid-biomembrane ecological treating system, it is characterized in that Confervoid-biomembrane ecological treating system is by oxidation pond (5) with cultivate the pool (1) and form, be connected by pipeline (6) between the oxidation pond (5) and the cultivation pool (1), be furnished with water silk floss (2) and microbial film (4) in the oxidation pond (5), water silk floss (2) and microbial film (4) employing " on-down " combination, water silk floss (2) is arranged in waterborne of oxidation pond (5), water silk floss (2) is fixed with plastic grid (3) support down, vertically arrange microbial film (4) down at plastic grid (3), the water flow mode of oxidation pond (5) goes out on advancing under being, cultivate and to arrange in the pool (1) and cultivate the water silk floss, the water flow mode of cultivating the pool (1) goes out on advancing under being.
2, Confervoid-biomembrane ecological treating system according to claim 1, it is characterized in that oxidation pond (5) degree of depth is 0.5~1.2 meter, the density of the interior water silk floss of oxidation pond (5) (2) is 0.5~5g/L, plastic grid (3) bottom is apart from 20~30 centimetres of the waters surface, microbial film (4) is carrier with the inert fiber, and the volume of carrier is oxidation pond (a 5) volumetrical 1%~20%.
3, Confervoid-biomembrane ecological treating system according to claim 1 and 2, the density that it is characterized in that the interior water silk floss of oxidation pond (5) (2) is 0.8~4.5g/L.
4, Confervoid-biomembrane ecological treating system according to claim 1 and 2, the concentration that it is characterized in that the interior water silk floss of oxidation pond (5) (2) is 4g/L.
5, Confervoid-biomembrane ecological treating system according to claim 1 and 2, the volume that it is characterized in that carrier are oxidation pond (5) volumetrical 15%.
6, Confervoid-biomembrane ecological treating system according to claim 1, it is characterized in that cultivating the pool (1) degree of depth is 0.3~0.7 meter, the concentration of cultivating total phosphorus in the pool (1) is 1.0~1.5mg/L, the pH value is 6~8, the volume of cultivating the pool (1) is oxidation pond (a 5) volumetrical 20%~50%, hydraulic detention time 2~7 days.
7, according to claim 1 or 6 described Confervoid-biomembrane ecological treating systems, the volume that it is characterized in that cultivating the pool (1) is oxidation pond (a 5) volumetrical 25%~45%.
8, according to claim 1 or 6 described Confervoid-biomembrane ecological treating systems, the volume that it is characterized in that cultivating the pool (1) is oxidation pond (a 5) volumetrical 30%.
CNA200910071593XA 2009-03-20 2009-03-20 Confervoid-biomembrane ecological treating system Pending CN101508511A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CNA200910071593XA CN101508511A (en) 2009-03-20 2009-03-20 Confervoid-biomembrane ecological treating system

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CNA200910071593XA CN101508511A (en) 2009-03-20 2009-03-20 Confervoid-biomembrane ecological treating system

Publications (1)

Publication Number Publication Date
CN101508511A true CN101508511A (en) 2009-08-19

Family

ID=41001070

Family Applications (1)

Application Number Title Priority Date Filing Date
CNA200910071593XA Pending CN101508511A (en) 2009-03-20 2009-03-20 Confervoid-biomembrane ecological treating system

Country Status (1)

Country Link
CN (1) CN101508511A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104591506A (en) * 2015-02-01 2015-05-06 武汉中科水生环境工程股份有限公司 Black and odorous plain river network overall ecological restoration system

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104591506A (en) * 2015-02-01 2015-05-06 武汉中科水生环境工程股份有限公司 Black and odorous plain river network overall ecological restoration system
CN104591506B (en) * 2015-02-01 2016-05-04 武汉中科水生环境工程股份有限公司 Black smelly type plain river network entirety Ecosystem restoration system

Similar Documents

Publication Publication Date Title
CN102276068B (en) River channel ecological construction and water body restoring system
CN204324990U (en) Be applicable to the multi-stage biological filter tank-ecological pond purification system into lake landscape water body
CN108217957B (en) Comprehensive treatment device and method for black and odorous water body in river channel
CN102219339A (en) Modular system for purification of polluted river water body and application of the same
CN204310864U (en) The circulation pulling flow type immobilization bioreactor that the pool, a kind of lake water body in-situ is repaired
CN104528921B (en) A kind of biological purification plant of high ammonia nitrogen cultivation biogas slurry
CN103833138B (en) View tower type device for water aeration and biological purification, and purification method
CN110143737A (en) A kind of river Ecology original position dredging restorative procedure
CN203768124U (en) Ecological filter for micro-polluted water treatment
CN104828951B (en) A kind of artificial wet land reinforced carbon nitrogen of ecological regulation and control type synchronously removes system
CN111777182A (en) Oxygen-enriched bioreactor suitable for in-situ remediation of micro-polluted water
CN203256023U (en) Tail water deep processing aeration-type ecological floating island with bamboo filament filler substrate
CN105417699A (en) Vertical flow artificial wetland ecological degradation method for tail water of urban sewage treatment plant
CN104386825A (en) Method for remediating pond water in situ
CN201506744U (en) Livestock breeding wastewater purification and treatment bio-film belt sectioned aeration oxidation pond
CN219239455U (en) Enhanced three-pond two-dam aquaculture tail water treatment system
CN202038919U (en) Riverway ecology construction and water restoration system
CN201458913U (en) Integrated biological ecological coordinated sewage treatment reactor
CN111499003A (en) Multistage coupling water quality ecological restoration system and restoration method
CN101381166A (en) Pollutant in water body of river, lake and landscape water strengthening reduction method using biological mode
CN201040726Y (en) Drift type multifunctional water purifying apparatus
CN110463647A (en) Based on microalgae-strain bio reactor circulating seawer cultivating system
CN101508511A (en) Confervoid-biomembrane ecological treating system
CN212833050U (en) Oxygen-enriched bioreactor suitable for in-situ remediation of micro-polluted water
CN204434348U (en) The biological purification plant of a kind of high ammonia nitrogen cultivation natural pond liquid

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C02 Deemed withdrawal of patent application after publication (patent law 2001)
WD01 Invention patent application deemed withdrawn after publication

Open date: 20090819