CN108249708B - Efficient livestock-raising water treatment system - Google Patents
Efficient livestock-raising water treatment system Download PDFInfo
- Publication number
- CN108249708B CN108249708B CN201810169882.2A CN201810169882A CN108249708B CN 108249708 B CN108249708 B CN 108249708B CN 201810169882 A CN201810169882 A CN 201810169882A CN 108249708 B CN108249708 B CN 108249708B
- Authority
- CN
- China
- Prior art keywords
- water
- chamber
- pipe
- reaction chamber
- communicated
- 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.)
- Expired - Fee Related
Links
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims abstract description 129
- 238000011282 treatment Methods 0.000 title claims abstract description 40
- 238000000746 purification Methods 0.000 claims abstract description 25
- 239000010802 sludge Substances 0.000 claims abstract description 25
- 239000010865 sewage Substances 0.000 claims abstract description 22
- 238000009395 breeding Methods 0.000 claims abstract description 14
- 230000001488 breeding effect Effects 0.000 claims abstract description 14
- 244000144972 livestock Species 0.000 claims abstract description 13
- 238000001179 sorption measurement Methods 0.000 claims description 9
- 241000894006 Bacteria Species 0.000 claims description 7
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims description 6
- 238000005273 aeration Methods 0.000 claims description 6
- 239000012528 membrane Substances 0.000 claims description 5
- 241001148470 aerobic bacillus Species 0.000 claims description 3
- 241001148471 unidentified anaerobic bacterium Species 0.000 claims description 3
- 238000004659 sterilization and disinfection Methods 0.000 abstract description 9
- 238000004062 sedimentation Methods 0.000 abstract description 4
- 238000012986 modification Methods 0.000 description 5
- 230000004048 modification Effects 0.000 description 5
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 4
- 210000002700 urine Anatomy 0.000 description 4
- 239000012535 impurity Substances 0.000 description 3
- 239000007787 solid Substances 0.000 description 3
- 239000007921 spray Substances 0.000 description 3
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 2
- 230000009286 beneficial effect Effects 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 210000003608 fece Anatomy 0.000 description 2
- 238000001914 filtration Methods 0.000 description 2
- 239000007788 liquid Substances 0.000 description 2
- 238000007726 management method Methods 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 2
- 238000000034 method Methods 0.000 description 2
- 229910052757 nitrogen Inorganic materials 0.000 description 2
- 229910052698 phosphorus Inorganic materials 0.000 description 2
- 239000011574 phosphorus Substances 0.000 description 2
- 239000000843 powder Substances 0.000 description 2
- 238000000926 separation method Methods 0.000 description 2
- 230000001954 sterilising effect Effects 0.000 description 2
- 239000002352 surface water Substances 0.000 description 2
- 239000002351 wastewater Substances 0.000 description 2
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical compound S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 description 1
- 238000010564 aerobic fermentation Methods 0.000 description 1
- 230000004075 alteration Effects 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 238000004061 bleaching Methods 0.000 description 1
- 230000006866 deterioration Effects 0.000 description 1
- 201000010099 disease Diseases 0.000 description 1
- 208000037265 diseases, disorders, signs and symptoms Diseases 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 238000000855 fermentation Methods 0.000 description 1
- 238000011010 flushing procedure Methods 0.000 description 1
- 229910000037 hydrogen sulfide Inorganic materials 0.000 description 1
- 208000015181 infectious disease Diseases 0.000 description 1
- 230000002458 infectious effect Effects 0.000 description 1
- 238000002955 isolation Methods 0.000 description 1
- 238000002386 leaching Methods 0.000 description 1
- 238000012544 monitoring process Methods 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 244000052769 pathogen Species 0.000 description 1
- 238000005325 percolation Methods 0.000 description 1
- 244000144977 poultry Species 0.000 description 1
- 239000013049 sediment Substances 0.000 description 1
- 230000035943 smell Effects 0.000 description 1
- 238000003860 storage Methods 0.000 description 1
- 239000002341 toxic gas Substances 0.000 description 1
Images
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F9/00—Multistage treatment of water, waste water or sewage
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/28—Treatment of water, waste water, or sewage by sorption
- C02F1/283—Treatment of water, waste water, or sewage by sorption using coal, charred products, or inorganic mixtures containing them
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/30—Treatment of water, waste water, or sewage by irradiation
- C02F1/32—Treatment of water, waste water, or sewage by irradiation with ultraviolet light
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/50—Treatment of water, waste water, or sewage by addition or application of a germicide or by oligodynamic treatment
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/02—Aerobic processes
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/28—Anaerobic digestion processes
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Biological Treatment Of Waste Water (AREA)
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
- Water Treatment By Sorption (AREA)
Abstract
The invention belongs to the technical field of sewage treatment, and particularly relates to a high-efficiency livestock-raising water treatment system which comprises a settling chamber, an anaerobic reaction chamber, an aerobic reaction chamber and a purification chamber which are sequentially communicated, wherein the top of the settling chamber is provided with a first operation opening, the upper end of the side wall of the settling chamber is communicated with a water inlet pipe, the upper end of the inner part of the settling chamber is provided with a filter screen, the outer side of the settling chamber is provided with a sludge chamber, the settling chamber and the anaerobic reaction chamber are communicated through a first water pipe, a second water pipe and a third water pipe are communicated between the anaerobic reaction chamber and the aerobic reaction chamber, and the aerobic reaction chamber and the purification chamber are communicated through a. The treatment system of the invention respectively carries out multi-stage treatment such as sedimentation, anaerobic treatment, aerobic treatment, disinfection and purification on the livestock breeding sewage, ensures the breeding sewage to be purified completely, and each stage can be circularly refluxed and repeatedly treated, thereby effectively improving the treatment quality of the water treatment system.
Description
Technical Field
The invention belongs to the technical field of sewage treatment, and particularly relates to a high-efficiency livestock breeding water treatment system.
Background
The industrialized and large-scale operation of the livestock breeding industry becomes a necessary trend of domestic and foreign production modes, and large-scale livestock farms develop rapidly and are increasingly large in scale in China this year. Meanwhile, with the enhancement of the environmental awareness of people, on one hand, the excrement generated in the production process of the industrialized livestock industry brings huge management pressure to enterprises and also brings serious threat and damage to the environment. The livestock breeding industry wastewater belongs to high-concentration organic wastewater rich in a large number of pathogens, is directly discharged into a water body or is not suitable for storage, is washed by rainwater and enters the water body, and can cause serious deterioration of surface water or underground water quality; because the leaching solubility of the livestock and poultry excrement and urine is very strong, if the nitrogen, phosphorus and water-soluble organic matters in the excrement and urine are not properly treated, the excrement and urine enters an underground water layer through surface runoff and percolation to pollute underground water; the influence on surface water is shown in that a large amount of dissolved oxygen in water is consumed, so that water body smells, and toxic gases such as methane, hydrogen sulfide and the like are generated, so that aquatic organisms die, and even certain epidemic diseases are spread. Therefore, how to solve the problem of the pollution of the excrement in the animal husbandry becomes a bottleneck technical problem to be solved urgently.
For the reasons, some sewage treatment methods and devices are available in the market, but the sewage treatment devices usually only carry out simple solid-liquid separation and then manually remove sediments, so that the labor intensity is high, the use effect and other surface feedback results are not ideal, the discharged livestock sewage still contains more impurities and has higher content of infectious microbes, and the requirements of sewage purification treatment cannot be completely met. For this reason, this application has developed an efficient livestock-raising water treatment system.
Disclosure of Invention
The treatment system of the invention respectively carries out multi-stage treatment such as sedimentation, anaerobic treatment, aerobic treatment, disinfection and purification on the livestock breeding sewage, ensures the breeding sewage to be purified completely, and each stage can be circularly refluxed and repeatedly treated, thereby effectively improving the treatment quality of the water treatment system.
The invention provides a high-efficiency livestock-raising water treatment system which comprises a settling chamber, an anaerobic reaction chamber, an aerobic reaction chamber and a purification chamber which are communicated in sequence, the inner bottom surfaces of the settling chamber, the anaerobic reaction chamber and the aerobic reaction chamber are all slopes, the top of the settling chamber is provided with a first operation opening, and the upper end of the side wall is communicated with a water inlet pipe, the upper end of the inner part of the settling chamber is provided with a filter screen, the outer side of the settling chamber is also provided with a sludge chamber, and the lower end of the side wall of the settling chamber and the lowest point of the slope close to the settling chamber are communicated with the top of the sludge chamber through a sludge discharge pipe, a first flow control valve is arranged on the sludge discharge pipe, the bottom of the sludge chamber is communicated with a sewage discharge pipe, the sewage discharge pipe is provided with a second flow control valve, a biological membrane filter layer is vertically arranged in the sludge chamber, and the sludge discharge pipe and the sewage discharge pipe are positioned on the same side of the biological membrane filter layer;
the highest point of the side wall of the settling chamber, which is close to the slope, is communicated with the side wall of the anaerobic reaction chamber and the highest point of the side wall of the anaerobic reaction chamber, which is close to the slope, through a first water passing pipe, a first water valve is installed on the first water passing pipe, the first water passing pipe is communicated with the sludge chamber through a first water return pipe, the first water return pipe and the sludge discharge pipe are respectively distributed on two sides of the biomembrane filter layer, a second water valve and a first water pump are respectively installed on the first water return pipe, attachment plates which are distributed in a left-right staggered manner are arranged in the anaerobic reaction chamber, and anaerobic bacteria are distributed on the attachment plates;
the anaerobic reaction chamber is communicated with the upper end of the side wall of the aerobic reaction chamber through a second water pipe, the lower end of the side wall of the aerobic reaction chamber is communicated with the upper end of the side wall of the anaerobic reaction chamber through a third water pipe, a connector of the third water pipe is positioned above the lowest point of a slope of the anaerobic reaction chamber and the aerobic reaction chamber, the third water pipe is communicated with the sludge discharge pipe through a second water return pipe, a third water valve and a second water pump are respectively installed on the second water return pipe, a support frame is arranged in the aerobic reaction chamber, a plurality of bacteria rooms are bound on the support frame, aerobic bacteria are distributed on the bacteria rooms, an air blower is arranged at the top of the aerobic reaction chamber, an aeration pipe is installed on the air blower, and the aeration pipe penetrates through the top of the aerobic reaction chamber and;
the aerobic reaction room with through the fourth water pipe intercommunication between the clean room, just the interface of fourth water pipe is located the slope peak top department of aerobic reaction room, inside, being located of clean room the fourth water pipe interface top department is equipped with the adsorbed layer, on the clean room lateral wall, be located the intercommunication of adsorbed layer top department has the drain pipe, the drain pipe with through third wet return intercommunication between the first water pipe, just install fourth water valve and third water pump on the third wet return respectively, the clean room top the water quality monitoring appearance is installed to the drain pipe kneck, the ultraviolet lamp is installed at the top in the clean room, just the clean room is provided with operation mouthful two.
Preferably, a spray header is installed on the inner top surface of the settling chamber, and the filter screen is V-shaped.
Preferably, a fifth water valve is installed on the second water passing pipe, and a sixth water valve is installed on the fourth water passing pipe.
Preferably, the adsorption layer comprises a cobblestone layer and an activated carbon layer laid on the cobblestone layer.
Compared with the prior art, the invention has the beneficial effects that:
the method comprises the steps of respectively carrying out multi-stage treatment such as sedimentation, anaerobic treatment, aerobic treatment, disinfection and purification and the like on livestock breeding sewage to ensure that the breeding sewage is purified, namely removing solid impurities such as hair and the like in the breeding sewage by using a filter screen, carrying out biofilm filtration and concentration on feces and urine after primary sedimentation to achieve a solid-liquid separation effect, decomposing organic dissolved matters and high-content nitrogen and phosphorus in the sewage through anaerobic fermentation and aerobic fermentation in sequence, and finally combining multiple modes such as filtration and adsorption, ultraviolet sterilization, delivery of disinfection powder and the like in a purification chamber to complete disinfection and purification. The device has reasonable design, the multiple return pipes can lead the sewage to be repeatedly treated by circulating and returning, the treatment quality of the water treatment system is effectively improved, and in addition, the valve is arranged between each treatment chamber, which is also beneficial to the isolation treatment according to the requirement, thereby saving resources.
Drawings
Fig. 1 is a schematic view of the efficient livestock breeding water treatment system of the invention.
Description of reference numerals:
1-a settling chamber, 11-an operation port I, 12-a filter screen, 13-a sludge discharge pipe, 14-a spray header, 2-an anaerobic reaction chamber, 21-an attachment plate, 3-an aerobic reaction chamber, 31-a second water passing pipe, 32-a third water passing pipe, 33-a second water return pipe, 34-a second water pump, 4-a purification chamber, 41-a third water return pipe, 42-a third water pump, 43-an ultraviolet lamp, 44-an operation port II, 5-a sludge chamber, 51-a biomembrane filter layer, 52-a first water return pipe, 53-a first water pump, 6-a support frame, 61-a bacteria room, 7-a blower, 71-an aeration pipe, 8-an adsorption layer and 9-a water quality monitor.
Detailed Description
One embodiment of the present invention is described in detail below with reference to fig. 1, but it should be understood that the scope of the present invention is not limited to the embodiment.
As shown in figure 1, a high-efficiency livestock-raising water treatment system comprises a settling chamber 1, an anaerobic reaction chamber 2, an aerobic reaction chamber 3 and a purification chamber 4 which are sequentially communicated, wherein livestock-raising sewage is respectively subjected to multi-stage treatment such as settling, anaerobic treatment, aerobic treatment, disinfection and purification to ensure that the breeding sewage is purified, the inner bottom surfaces of the settling chamber 1, the anaerobic reaction chamber 2 and the aerobic reaction chamber 3 are slopes to facilitate the concentration of sludge and feces in a water body at a low position for convenient discharge, an operation opening I11 is arranged at the top of the settling chamber 1, a water inlet pipe is communicated with the upper end of the side wall, a filter screen 12 is arranged at the upper end inside the settling chamber 1 to remove solid impurities, a sludge chamber 5 is also arranged outside the settling chamber 1, the lowest point of the side wall of the settling chamber 1, which is close to the slope of the settling chamber 1, is communicated with the top of the sludge chamber 5 through a sludge discharge pipe, 5 bottoms of mud room intercommunication has the blow off pipe, and installs the second flow control valve on the blow off pipe, and the vertical biomembrane filter layer 51 that is provided with in the mud room 5 is further concentrated the mud excrement that just deposits, and the follow-up usefulness such as landfill, retting of being convenient for mud excrement is located the homonymy of biomembrane filter layer 51 with the blow off pipe.
The side wall of the settling chamber 1 is communicated with the side wall of the anaerobic reaction chamber 2 at the highest point close to the slope and is communicated with the highest point close to the slope through a first water passing pipe, a first water valve is arranged on the first water passing pipe, the first water passing pipe is communicated with the sludge chamber 5 through a first water return pipe 52, the first water return pipe 52 and the sludge discharge pipe 13 are respectively distributed at two sides of the biomembrane filter layer 51, a second water valve and a first water pump 53 are respectively arranged on the first water return pipe 52, the anaerobic reaction chamber 2 is internally provided with attachment plates 21 which are distributed in a left-right staggered manner, and anaerobic bacteria (RW-100N type, Shandong Scuchi bioengineering Co., Ltd.).
The upper ends of the side walls of the anaerobic reaction chamber 2 and the aerobic reaction chamber 3 are communicated with each other through a second water pipe 31, the lower ends of the side walls of the anaerobic reaction chamber 2 and the aerobic reaction chamber 3 are communicated with each other through a third water pipe 32, the interface of the third water pipe 32 is positioned above the lowest point of the slope of the anaerobic reaction chamber 2 and the aerobic reaction chamber 3, the third water pipe 32 is communicated with the sludge discharge pipe 13 through a second water return pipe 33, a third water valve and a second water pump 34 are respectively installed on the second water return pipe 33, a support frame 6 is arranged in the aerobic reaction chamber 3, a plurality of bacteria rooms 61 are bound on the support frame 6, aerobic bacteria (Fushan De Mizhong chemical engineering Co., Ltd., G-205 type) are distributed on the bacteria rooms 61, an air blower 7 is arranged at the top of the aerobic reaction chamber 3, an aeration pipe 71 is installed on the air blower 7.
The aerobic reaction chamber 3 is communicated with the purification chamber 4 through a fourth water pipe, an interface of the fourth water pipe is positioned above the highest point of a slope of the aerobic reaction chamber 3, an adsorption layer 8 is arranged above the interface of the fourth water pipe inside the purification chamber 4, a drain pipe is communicated with the side wall of the purification chamber 4 and positioned above the adsorption layer 8, the drain pipe is communicated with the first water pipe through a third water return pipe 41, a fourth water valve and a third water pump 42 are respectively arranged on the third water return pipe 41, a water quality monitor 9 is arranged at the top of the purification chamber 4 and the interface of the drain pipe, after the water quality is detected to be unqualified after the treatment, the water body flows back to the first water pipe for renewed treatment, an ultraviolet lamp 43 is arranged at the top inside the purification chamber 4, ultraviolet sterilization is carried out, the purification chamber 4 is provided with an operation port II 44, and bleaching and disinfection powder can be put into.
The inner top surface of the settling chamber 1 is provided with a spray header 14 for a flushing device, and the filter screen 12 is V-shaped, so that solid suspended matters such as hair and the like can be conveniently collected.
The second water passing pipe 31 is provided with a fifth water valve, the fourth water passing pipe is provided with a sixth water valve, and the anaerobic reaction chamber 2, the aerobic reaction chamber 3 and the purification chamber 4 are separated, so that independent management is facilitated.
The adsorption layer 8 comprises a cobblestone layer and an activated carbon layer paved on the cobblestone layer, and is used for adsorbing and purifying the water body.
It should be noted that the preferred embodiments of the present invention have been described for the purpose of preventing redundancy, but that additional variations and modifications of the embodiments may occur to those skilled in the art once they learn of the basic inventive concepts. Therefore, it is intended that the appended claims be interpreted as including preferred embodiments and all such alterations and modifications as fall within the scope of the invention.
It will be apparent to those skilled in the art that various changes and modifications may be made in the present invention without departing from the spirit and scope of the invention. Thus, if such modifications and variations of the present invention fall within the scope of the claims of the present invention and their equivalents, the present invention is also intended to include such modifications and variations.
Claims (3)
1. The utility model provides a high-efficiency livestock-raising water treatment system, which is characterized in that, including the drip chamber (1), anaerobic reaction chamber (2), aerobic reaction chamber (3) and clean room (4) that communicate in proper order, drip chamber (1), anaerobic reaction chamber (2) with the interior bottom surface of aerobic reaction chamber (3) is the slope, drip chamber (1) top is equipped with operation mouth one (11), and lateral wall upper end intercommunication has the inlet tube, drip chamber (1) inside upper end is provided with filter screen (12), the drip chamber (1) outside still is equipped with mud chamber (5), just drip chamber (1) lateral wall lower extreme, be close to the slope minimum department of drip chamber (1) with mud chamber (5) top is through mud pipe (13) intercommunication, install first flow control valve on mud pipe (13), mud chamber (5) bottom intercommunication has the blow off pipe, the sewage discharge pipe is provided with a second flow control valve, a biological membrane filter layer (51) is vertically arranged in the sludge chamber (5), and the sludge discharge pipe (13) and the sewage discharge pipe are positioned on the same side of the biological membrane filter layer (51);
the side wall of the settling chamber (1) is communicated with the side wall of the anaerobic reaction chamber (2) at the highest point close to the slope through a first water passing pipe, a first water valve is mounted on the first water passing pipe, the first water passing pipe is communicated with the sludge chamber (5) through a first water return pipe (52), the first water return pipe (52) and the sludge discharge pipe (13) are respectively distributed on two sides of the biological membrane filter layer (51), a second water valve and a first water pump (53) are respectively mounted on the first water return pipe (52), attachment plates (21) which are distributed in a left-right staggered mode are arranged in the anaerobic reaction chamber (2), and anaerobic bacteria are distributed on the attachment plates (21);
the anaerobic reaction chamber (2) and the upper end of the side wall of the aerobic reaction chamber (3) are communicated through a second water pipe (31) and a third water pipe (32) respectively, the interface of the third water pipe (32) is positioned above the lowest point of the slope of the anaerobic reaction chamber (2) and the aerobic reaction chamber (3), the third water pipe (32) is communicated with the sludge discharge pipe (13) through a second water return pipe (33), a third water valve and a second water pump (34) are respectively installed on the second water return pipe (33), a support frame (6) is arranged in the aerobic reaction chamber (3), a plurality of bacteria rooms (61) are bound on the support frame (6), aerobic bacteria are distributed on the bacteria rooms (61), an air blower (7) is arranged at the top of the aerobic reaction chamber (3), and an aeration pipe (71) is installed on the air blower (7), the aeration pipe (71) penetrates through the top of the aerobic reaction chamber (3) and is laid on the inner wall;
the aerobic reaction chamber (3) is communicated with the purification chamber (4) through a fourth water pipe, an interface of the fourth water pipe is positioned above the highest point of a slope of the aerobic reaction chamber (3), an adsorption layer (8) is arranged inside the purification chamber (4) and above the interface of the fourth water pipe, a drain pipe is communicated with the adsorption layer (8) and above the side wall of the purification chamber (4), the drain pipe is communicated with the first water pipe through a third water return pipe (41), a fourth water valve and a third water pump (42) are respectively arranged on the third water return pipe (41), a water quality monitor (9) is arranged at the top of the purification chamber (4) and the interface of the drain pipe, an ultraviolet lamp (43) is arranged at the top of the purification chamber (4), and the purification chamber (4) is provided with an operation port II (44), the adsorption layer (8) comprises a cobblestone layer and an activated carbon layer paved on the cobblestone layer.
2. A highly efficient livestock breeding water treatment system according to claim 1, wherein a shower head (14) is installed on the inner top surface of the settling chamber (1), and the filter screen (12) is V-shaped.
3. A high efficiency livestock breeding water treatment system according to claim 1, wherein a fifth water valve is mounted on said second water conduit (31) and a sixth water valve is mounted on said fourth water conduit.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201810169882.2A CN108249708B (en) | 2018-03-01 | 2018-03-01 | Efficient livestock-raising water treatment system |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201810169882.2A CN108249708B (en) | 2018-03-01 | 2018-03-01 | Efficient livestock-raising water treatment system |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| CN108249708A CN108249708A (en) | 2018-07-06 |
| CN108249708B true CN108249708B (en) | 2021-05-04 |
Family
ID=62744266
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201810169882.2A Expired - Fee Related CN108249708B (en) | 2018-03-01 | 2018-03-01 | Efficient livestock-raising water treatment system |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN108249708B (en) |
Families Citing this family (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN211035476U (en) * | 2019-09-06 | 2020-07-17 | 唐山维数科技有限公司 | Novel sewage treatment system |
| CN110526519A (en) * | 2019-09-24 | 2019-12-03 | 广西贺州市红星纸业有限公司 | A kind of processing method of paper waste |
| CN118405798B (en) * | 2024-02-02 | 2024-11-19 | 中国水产科学研究院珠江水产研究所 | Intelligent treatment method for aquaculture tail water |
Citations (8)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN1830844A (en) * | 2006-03-22 | 2006-09-13 | 湖南大学 | Simultaneous denitrification and dephosphorization process of urban sewage |
| CN101269881A (en) * | 2008-04-23 | 2008-09-24 | 浙江德安新技术发展有限公司 | Inner loop liquefaction biological reaction apparatus for wastewater treatment |
| JP4409532B2 (en) * | 2005-05-11 | 2010-02-03 | スン リュ，ジ | Apparatus for treating wastewater containing high-concentration nitrogen such as livestock wastewater and manure, and its treatment method |
| CN101759323A (en) * | 2009-12-24 | 2010-06-30 | 江西省科学院能源研究所 | Treatment combined process for pig farm waste water with high nitrogen content |
| CN104351106A (en) * | 2014-11-27 | 2015-02-18 | 苏州苏湘特种水产养殖场 | System for increasing water quality of aquaculture system |
| CN105967435A (en) * | 2016-04-20 | 2016-09-28 | 安徽华骐环保科技股份有限公司 | Double-circulation nitrogen and phosphorus removal wastewater treatment system and process |
| CN106565017A (en) * | 2015-12-24 | 2017-04-19 | 安徽华骐环保科技股份有限公司 | Bicirculating nitrogen and phosphorus removal wastewater treatment system and method |
| CN106938874A (en) * | 2017-04-19 | 2017-07-11 | 长江大学 | Improve livestock breeding wastewater handling process |
Family Cites Families (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101665304B (en) * | 2009-09-29 | 2011-05-04 | 河北农业大学 | Solar Anaerobic Granular Sludge Circulating Reactor |
| CN203878046U (en) * | 2014-04-25 | 2014-10-15 | 天津圣颐和科技有限公司 | Farm waste biochemical digestion and storage system |
| CN203904150U (en) * | 2014-05-28 | 2014-10-29 | 北京齐舜农业科技有限公司 | Fur animal excrement sewage treatment system |
| CN104512985A (en) * | 2014-12-13 | 2015-04-15 | 佛山市高明区合朝农业发展有限公司 | Piggery wastewater anaerobic digestion method for production of biogas |
| CN105084586B (en) * | 2015-07-31 | 2017-06-16 | 四川沃兹凯兰科技有限公司 | The treatment for reuse skid-mounted device of gas field container and pipeline cleaning waste water |
| CN105948381A (en) * | 2016-05-13 | 2016-09-21 | 孙立民 | Environment-friendly sewage treatment equipment |
| CN206266401U (en) * | 2016-12-01 | 2017-06-20 | 广东宇唐环保设备有限公司 | A kind of integrated sewage treating apparatus |
-
2018
- 2018-03-01 CN CN201810169882.2A patent/CN108249708B/en not_active Expired - Fee Related
Patent Citations (8)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP4409532B2 (en) * | 2005-05-11 | 2010-02-03 | スン リュ，ジ | Apparatus for treating wastewater containing high-concentration nitrogen such as livestock wastewater and manure, and its treatment method |
| CN1830844A (en) * | 2006-03-22 | 2006-09-13 | 湖南大学 | Simultaneous denitrification and dephosphorization process of urban sewage |
| CN101269881A (en) * | 2008-04-23 | 2008-09-24 | 浙江德安新技术发展有限公司 | Inner loop liquefaction biological reaction apparatus for wastewater treatment |
| CN101759323A (en) * | 2009-12-24 | 2010-06-30 | 江西省科学院能源研究所 | Treatment combined process for pig farm waste water with high nitrogen content |
| CN104351106A (en) * | 2014-11-27 | 2015-02-18 | 苏州苏湘特种水产养殖场 | System for increasing water quality of aquaculture system |
| CN106565017A (en) * | 2015-12-24 | 2017-04-19 | 安徽华骐环保科技股份有限公司 | Bicirculating nitrogen and phosphorus removal wastewater treatment system and method |
| CN105967435A (en) * | 2016-04-20 | 2016-09-28 | 安徽华骐环保科技股份有限公司 | Double-circulation nitrogen and phosphorus removal wastewater treatment system and process |
| CN106938874A (en) * | 2017-04-19 | 2017-07-11 | 长江大学 | Improve livestock breeding wastewater handling process |
Also Published As
| Publication number | Publication date |
|---|---|
| CN108249708A (en) | 2018-07-06 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN203173939U (en) | Breeding wastewater treatment system | |
| CN108249708B (en) | Efficient livestock-raising water treatment system | |
| CN110590080A (en) | A biofilm sewage treatment equipment | |
| CN109809642A (en) | A kind of remodeling purification tank of multi-stage aerobic processing rural households' sewage | |
| CN101746922B (en) | Garden domestic sewage treatment and reuse system and sewage treatment method | |
| CN207243677U (en) | Non-pump type depth integrated equipment for sewage treatment | |
| CN205953659U (en) | Bury formula deodorization and purify towards lavatory sewage treatment groove | |
| CN202643507U (en) | High-efficiency fluidization-state waste water treatment device without septic tank | |
| CN207933237U (en) | A kind of sewage treatment unit suitable for rural area | |
| CN215886722U (en) | High-efficient integration medical wastewater treatment equipment | |
| CN216039168U (en) | Rural domestic sewage ecological treatment equipment | |
| CN215855350U (en) | A multistage nitrogen and phosphorus removal processing apparatus that intakes for sewage purification | |
| CN215327237U (en) | Microorganism sewage treatment plant | |
| CN201406363Y (en) | Integrated underground sewage treatment equipment | |
| CN214654269U (en) | Environment-friendly sewage treatment equipment | |
| CN212924733U (en) | Novel integrated equipment capable of treating sewage discharge and utilizing | |
| CN210457873U (en) | New energy rural sewage treatment and recovery system | |
| CN201272715Y (en) | Integrated membrane biological sewage treatment device | |
| CN209778597U (en) | Device for deeply removing total nitrogen in wastewater based on biological method | |
| CN107162197A (en) | Three rank O/A decentralized type sewages handle integrated apparatus and method | |
| CN209940758U (en) | Improved purification tank for multistage aerobic treatment of rural household sewage | |
| CN210030309U (en) | Single-family miniature domestic sewage treatment device | |
| CN107265638A (en) | Integral type high ammonia-nitrogen wastewater biological removal reaction unit | |
| CN207330494U (en) | A kind of biological aerated filter | |
| CN206955755U (en) | Three rank O/A decentralized type sewages handle integrated apparatus |
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 | ||
| CB03 | Change of inventor or designer information |
Inventor after: Zhang Shouming Inventor after: Tian Xiuhua Inventor after: Zhao Dan Inventor after: Qiao Lili Inventor after: Zhang Yanguang Inventor after: Xu Juan Inventor after: Li Guangbo Inventor after: Zhao Yanfang Inventor after: Long Fuqing Inventor before: Zhang Shouming Inventor before: Long Fuqing Inventor before: Zhao Dan Inventor before: Qiao Lili Inventor before: Zhang Yanguang Inventor before: Xu Juan Inventor before: Li Guangbo Inventor before: Zhao Yanfang Inventor before: Tian Xiuhua |
|
| CB03 | Change of inventor or designer information | ||
| GR01 | Patent grant | ||
| GR01 | Patent grant | ||
| CF01 | Termination of patent right due to non-payment of annual fee |
Granted publication date: 20210504 |
|
| CF01 | Termination of patent right due to non-payment of annual fee |