CN107628733A - A kind of integrated rural domestic sewage processing method - Google Patents
A kind of integrated rural domestic sewage processing method Download PDFInfo
- Publication number
- CN107628733A CN107628733A CN201711059976.6A CN201711059976A CN107628733A CN 107628733 A CN107628733 A CN 107628733A CN 201711059976 A CN201711059976 A CN 201711059976A CN 107628733 A CN107628733 A CN 107628733A
- Authority
- CN
- China
- Prior art keywords
- sewage
- tank
- sludge
- drained
- treated
- 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.)
- Withdrawn
Links
- 239000010865 sewage Substances 0.000 claims abstract 33
- 239000010802 sludge Substances 0.000 claims abstract 11
- 238000004062 sedimentation Methods 0.000 claims abstract 10
- 238000003672 processing method Methods 0.000 claims abstract 7
- 230000001112 coagulating effect Effects 0.000 claims abstract 4
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract 4
- 238000000034 method Methods 0.000 claims abstract 3
- 238000001556 precipitation Methods 0.000 claims abstract 2
- 239000004576 sand Substances 0.000 claims abstract 2
- 238000000926 separation method Methods 0.000 claims abstract 2
- 238000001914 filtration Methods 0.000 claims 5
- 239000000645 desinfectant Substances 0.000 claims 4
- 239000002002 slurry Substances 0.000 claims 4
- 239000007788 liquid Substances 0.000 claims 3
- OSVXSBDYLRYLIG-UHFFFAOYSA-N chlorine dioxide Inorganic materials O=Cl=O OSVXSBDYLRYLIG-UHFFFAOYSA-N 0.000 claims 1
- QBWCMBCROVPCKQ-UHFFFAOYSA-N chlorous acid Chemical compound OCl=O QBWCMBCROVPCKQ-UHFFFAOYSA-N 0.000 claims 1
- 241000894006 Bacteria Species 0.000 abstract 1
- 230000001580 bacterial effect Effects 0.000 abstract 1
- 230000000694 effects Effects 0.000 abstract 1
Landscapes
- Treatment Of Sludge (AREA)
- Separation Using Semi-Permeable Membranes (AREA)
Abstract
The invention discloses a kind of integrated rural domestic sewage processing method, specifically comprise the following steps:S1:Sanitary sewage is filtered for the first time by grid solarium;S2:The sewage treated by grid is discharged into setting pot, sedimentation separation removal is carried out to the sand in sewage;S3:The sewage treated by setting pot is drained into first shallow lake pond, the sludge in sewage separate removing;S4:The process sewage that just shallow lake pond treats is drained into biological treatment tank and handled;S5:The sewage treated by biological treatment tank is drained into secondary sedimentation tank, secondary precipitation is carried out to the sludge in sewage;S6:The sewage treated by secondary sedimentation tank is drained into coagulating sedimentation tank.After present invention processing sewage within the identical time, sewage bacterial number reduces 68%, the bacterium that can be effectively gone out in decontaminated water using sewage water treatment method in the present invention, improves the effect of sewage disposal, reduces the cost of sewage disposal.
Description
Technical field
The present invention relates to technical field of sewage, more particularly to a kind of integrated rural domestic sewage processing method.
Background technology
Mainly there are kitchen, shower in the source of domestic sewage in rural areas, wash and flush the toilet, its quantity, composition, pollutant concentration
Habits and customs, living standard and water consumption with urban residents are relevant.In general, domestic sewage in rural areas has following features:
Content of organics is higher, and biodegradability is good, and the poisonous and harmful substance content such as heavy metal is low, and water quality and quantity fluctuation is big.
Through retrieval, the A of Chinese patent application publication No. CN 107200432 are disclosed at a kind of integrated rural sanitary sewage
Reason method, including:S1, sewage is discharged into the coarse grid room being sequentially arranged from inside to outside;S2, the sewage for treating coarse grid room
Thin grid room is discharged into, row buffering regulation is entered to sewage;S3, by overflow manner, the water after being handled in thin grid room is discharged into MBR
Film process room;S4, by overflow manner, the water after being handled in MBR film process room is discharged into oxidizing chamber;S5, at thin grid room bottom
Portion sets the first mud discharging mouth, and the second mud discharging mouth is set in MBR film process room bottom, and the 3rd mud discharging mouth is set in oxidizing chamber bottom,
Three mud discharging mouths lead to the mud room of chambers bottom, and mud room is used to accept the sludge in sewage.
The characteristics of country sewage emission source is that discharge capacity is little, and emission point disperses, and sewage is collected by extensive pipe network
Medium-and-large-sized sewage treatment plant is concentrated to have any problem, and it is uneconomical.But be such as allowed to free discharge, then larger shadow is caused to environment
Ring, existing sewage disposal process is comparatively laborious, and processing cost is higher, and operating efficiency is relatively low, and treatment effect is good.
The content of the invention
It is an object of the invention to provide a kind of integrated rural domestic sewage processing method, possesses cost of sewage disposal
Low, the advantages of operating efficiency is high, high treating effect, solve that existing sewage disposal process is comparatively laborious, processing cost is high, work
The problem of efficiency is low.
A kind of integrated rural domestic sewage processing method according to embodiments of the present invention, specifically comprises the following steps:
S1:Sanitary sewage is filtered for the first time by grid solarium;
S2:The sewage treated by grid is discharged into setting pot, carrying out sedimentation separation to the sand in sewage goes
Remove;
S3:The sewage treated by setting pot is drained into first shallow lake pond, the sludge in sewage separate removing;
S4:The process sewage that just shallow lake pond treats is drained into biological treatment tank and handled;
S5:The sewage treated by biological treatment tank is drained into secondary sedimentation tank, the sludge in sewage is carried out
Secondary precipitation;
S6:The sewage treated by secondary sedimentation tank is drained into coagulating sedimentation tank, added in coagulating sedimentation tank
CuSO4, per 1000m31.5-3 ㎏ CuSO is added in sewage4, the debris in sewage is precipitated again;
S7:The sewage treated by coagulating sedimentation tank is drained into filtering tank and carries out filtration treatment;
S8:After adding disinfectant in the liquid after filter tank filtering, the concentration for adding disinfectant is 0.15-0.30 ㎎/L.
On the basis of such scheme, after being precipitated in S3 to the sludge in sewage, logistics is flowed into slurries filter
Filtered, the sludge after filtering is flowed into mud concentration tank and concentrated.
On the basis of such scheme, after secondary to the sludge progress in sewage in S5, partial sludge flows again into life
Handled in thing process tank, excess sludge is flowed on slurries filter and filtered, and the sludge after filtering is flowed into mud
Concentrated in concentration tank.
On the basis of such scheme, the sludge after the mud concentration tank concentration is sent to slurry dewatering tank and is dehydrated.
On the basis of such scheme, in S8, the composition of used disinfectant is ClO2。
On the basis of such scheme, the temperature control of liquid is at 4 DEG C -6 DEG C when disinfectant is added in S8.
The present invention has an advantageous effect in that compared with prior art:
1st, can be respectively to miscellaneous in sewage by setting grid solarium, setting pot, biological treatment tank and secondary sedimentation tank
Thing and sand carry out preliminary filtering, and sewage, which is sent in biological treatment tank, effectively to carry out biological treatment to sewage,
Environment is protected, sets secondary sedimentation tank to carry out secondary precipitation to the impurity in sewage, it is simple and effective to remove in decontaminated water
Impurity, add CuSO in coagulating sedimentation tank4The cuprous iodide sediment of the iodide ion generation white in decontaminated water can be removed,
The debris in decontaminated water, high treating effect can effectively be removed.
2nd, by setting filtering tank to be filtered again to the sewage for removing debris, added in sewage after filtration
Disinfectant can remove the bacterium in decontaminated water, can be effectively to precipitation by setting mud concentration tank and slurry dewatering tank
Sludge is concentrated and is dehydrated, and the sludge after the processing of slurry dewatering tank can be used for filling, is agricultural and make compost, and protect
Environmental beneficial effect, reduce the cost of sewage disposal.
Embodiment
For feature, technological means and the concrete function reached of the present invention can be further appreciated that, below with specific implementation
Mode is described in further detail to the present invention.
Embodiment 1
A kind of integrated rural domestic sewage processing method is present embodiments provided, is specifically comprised the following steps:
S1:Sanitary sewage is filtered for the first time by grid solarium;
S2:The sewage treated by grid is discharged into setting pot, carrying out sedimentation separation to the sand in sewage goes
Remove;
S3:The sewage treated by setting pot is drained into first shallow lake pond, the sludge in sewage separate removing;
S4:The process sewage that just shallow lake pond treats is drained into biological treatment tank and handled;
S5:The sewage treated by biological treatment tank is drained into secondary sedimentation tank, the sludge in sewage is carried out
Secondary precipitation;
S6:The sewage treated by secondary sedimentation tank is drained into coagulating sedimentation tank, added in coagulating sedimentation tank
CuSO4, per 1000m31.5 ㎏ CuSO is added in sewage4, the debris in sewage is precipitated again;
S7:The sewage treated by coagulating sedimentation tank is drained into filtering tank and carries out filtration treatment;
S8:After adding disinfectant in the liquid after filter tank filtering, the concentration for adding disinfectant is 0.15 ㎎/L.
After being precipitated in S3 to the sludge in sewage, logistics is flowed into slurries filter and filtered, the dirt after filtering
Mud is flowed into mud concentration tank and concentrated.
In S5 in sewage sludge carry out it is secondary after, partial sludge is flowed again into biological treatment tank and handled,
Excess sludge is flowed on slurries filter and filtered, and the sludge after filtering is flowed into mud concentration tank and concentrated.
The composition of S8 disinfectants is ClO2。
The temperature control of liquid is at 4 DEG C -6 DEG C when disinfectant is added in S8.
Embodiment 2
A kind of integrated rural domestic sewage processing method is present embodiments provided, is specifically comprised the following steps:
S1:Sanitary sewage is filtered for the first time by grid solarium;
S2:The sewage treated by grid is discharged into setting pot, carrying out sedimentation separation to the sand in sewage goes
Remove;
S3:The sewage treated by setting pot is drained into first shallow lake pond, the sludge in sewage separate removing;
S4:The process sewage that just shallow lake pond treats is drained into biological treatment tank and handled;
S5:The sewage treated by biological treatment tank is drained into secondary sedimentation tank, the sludge in sewage is carried out
Secondary precipitation;
S6:The sewage treated by secondary sedimentation tank is drained into coagulating sedimentation tank, added in coagulating sedimentation tank
CuSO4, per 1000m31.5 ㎏ CuSO is added in sewage4, the debris in sewage is precipitated again;
S7:The sewage treated by coagulating sedimentation tank is drained into filtering tank and carries out filtration treatment;
S8:After adding disinfectant in the liquid after filter tank filtering, the concentration for adding disinfectant is 0.17 ㎎/L.
After being precipitated in S3 to the sludge in sewage, logistics is flowed into slurries filter and filtered, the dirt after filtering
Mud is flowed into mud concentration tank and concentrated.
In S5 in sewage sludge carry out it is secondary after, partial sludge is flowed again into biological treatment tank and handled,
Excess sludge is flowed on slurries filter and filtered, and the sludge after filtering is flowed into mud concentration tank and concentrated.
The composition of S8 disinfectants is ClO2。
The temperature control of liquid is at 4 DEG C -6 DEG C when disinfectant is added in S8.
Embodiment 3
A kind of integrated rural domestic sewage processing method is present embodiments provided, is specifically comprised the following steps:
S1:Sanitary sewage is filtered for the first time by grid solarium;
S2:The sewage treated by grid is discharged into setting pot, carrying out sedimentation separation to the sand in sewage goes
Remove;
S3:The sewage treated by setting pot is drained into first shallow lake pond, the sludge in sewage separate removing;
S4:The process sewage that just shallow lake pond treats is drained into biological treatment tank and handled;
S5:The sewage treated by biological treatment tank is drained into secondary sedimentation tank, the sludge in sewage is carried out
Secondary precipitation;
S6:The sewage treated by secondary sedimentation tank is drained into coagulating sedimentation tank, added in coagulating sedimentation tank
CuSO4, per 1000m31.5 ㎏ CuSO is added in sewage4, the debris in sewage is precipitated again;
S7:The sewage treated by coagulating sedimentation tank is drained into filtering tank and carries out filtration treatment;
S8:After adding disinfectant in the liquid after filter tank filtering, the concentration for adding disinfectant is 0.19 ㎎/L.
After being precipitated in S3 to the sludge in sewage, logistics is flowed into slurries filter and filtered, the dirt after filtering
Mud is flowed into mud concentration tank and concentrated.
In S5 in sewage sludge carry out it is secondary after, partial sludge is flowed again into biological treatment tank and handled,
Excess sludge is flowed on slurries filter and filtered, and the sludge after filtering is flowed into mud concentration tank and concentrated.
The composition of S8 disinfectants is ClO2。
The temperature control of liquid is at 4 DEG C -6 DEG C when disinfectant is added in S8.
Embodiment 4
A kind of integrated rural domestic sewage processing method is present embodiments provided, is specifically comprised the following steps:
S1:Sanitary sewage is filtered for the first time by grid solarium;
S2:The sewage treated by grid is discharged into setting pot, carrying out sedimentation separation to the sand in sewage goes
Remove;
S3:The sewage treated by setting pot is drained into first shallow lake pond, the sludge in sewage separate removing;
S4:The process sewage that just shallow lake pond treats is drained into biological treatment tank and handled;
S5:The sewage treated by biological treatment tank is drained into secondary sedimentation tank, the sludge in sewage is carried out
Secondary precipitation;
S6:The sewage treated by secondary sedimentation tank is drained into coagulating sedimentation tank, added in coagulating sedimentation tank
CuSO4, per 1000m31.5 ㎏ CuSO is added in sewage4, the debris in sewage is precipitated again;
S7:The sewage treated by coagulating sedimentation tank is drained into filtering tank and carries out filtration treatment;
S8:After adding disinfectant in the liquid after filter tank filtering, the concentration for adding disinfectant is 0.23 ㎎/L.
After being precipitated in S3 to the sludge in sewage, logistics is flowed into slurries filter and filtered, the dirt after filtering
Mud is flowed into mud concentration tank and concentrated.
In S5 in sewage sludge carry out it is secondary after, partial sludge is flowed again into biological treatment tank and handled,
Excess sludge is flowed on slurries filter and filtered, and the sludge after filtering is flowed into mud concentration tank and concentrated.
The composition of S8 disinfectants is ClO2。
The temperature control of liquid is at 4 DEG C -6 DEG C when disinfectant is added in S8.
Embodiment 5
A kind of integrated rural domestic sewage processing method is present embodiments provided, is specifically comprised the following steps:
S1:Sanitary sewage is filtered for the first time by grid solarium;
S2:The sewage treated by grid is discharged into setting pot, carrying out sedimentation separation to the sand in sewage goes
Remove;
S3:The sewage treated by setting pot is drained into first shallow lake pond, the sludge in sewage separate removing;
S4:The process sewage that just shallow lake pond treats is drained into biological treatment tank and handled;
S5:The sewage treated by biological treatment tank is drained into secondary sedimentation tank, the sludge in sewage is carried out
Secondary precipitation;
S6:The sewage treated by secondary sedimentation tank is drained into coagulating sedimentation tank, added in coagulating sedimentation tank
CuSO4, per 1000m31.5 ㎏ CuSO is added in sewage4, the debris in sewage is precipitated again;
S7:The sewage treated by coagulating sedimentation tank is drained into filtering tank and carries out filtration treatment;
S8:After adding disinfectant in the liquid after filter tank filtering, the concentration for adding disinfectant is 0.27 ㎎/L.
After being precipitated in S3 to the sludge in sewage, logistics is flowed into slurries filter and filtered, the dirt after filtering
Mud is flowed into mud concentration tank and concentrated.
In S5 in sewage sludge carry out it is secondary after, partial sludge is flowed again into biological treatment tank and handled,
Excess sludge is flowed on slurries filter and filtered, and the sludge after filtering is flowed into mud concentration tank and concentrated.
The composition of S8 disinfectants is ClO2。
The temperature control of liquid is at 4 DEG C -6 DEG C when disinfectant is added in S8.
Embodiment 6
A kind of integrated rural domestic sewage processing method is present embodiments provided, is specifically comprised the following steps:
S1:Sanitary sewage is filtered for the first time by grid solarium;
S2:The sewage treated by grid is discharged into setting pot, carrying out sedimentation separation to the sand in sewage goes
Remove;
S3:The sewage treated by setting pot is drained into first shallow lake pond, the sludge in sewage separate removing;
S4:The process sewage that just shallow lake pond treats is drained into biological treatment tank and handled;
S5:The sewage treated by biological treatment tank is drained into secondary sedimentation tank, the sludge in sewage is carried out
Secondary precipitation;
S6:The sewage treated by secondary sedimentation tank is drained into coagulating sedimentation tank, added in coagulating sedimentation tank
CuSO4, per 1000m31.5 ㎏ CuSO is added in sewage4, the debris in sewage is precipitated again;
S7:The sewage treated by coagulating sedimentation tank is drained into filtering tank and carries out filtration treatment;
S8:After adding disinfectant in the liquid after filter tank filtering, the concentration for adding disinfectant is 0.30 ㎎/L.
After being precipitated in S3 to the sludge in sewage, logistics is flowed into slurries filter and filtered, the dirt after filtering
Mud is flowed into mud concentration tank and concentrated.
In S5 in sewage sludge carry out it is secondary after, partial sludge is flowed again into biological treatment tank and handled,
Excess sludge is flowed on slurries filter and filtered, and the sludge after filtering is flowed into mud concentration tank and concentrated.
The composition of S8 disinfectants is ClO2。
The temperature control of liquid is at 4 DEG C -6 DEG C when disinfectant is added in S8.
Experiment test example
Killing effect of the chlorine dioxide of table one to bacterium in water
One is shown in Table, control group is without the treated sewage of the present invention, and embodiment 1-5 is using processing side in the present invention
The treated sewage of method, the bacterial population within the identical time in sewage reduce 68%, use sewage disposal side in the present invention
The bacterium that method can effectively go out in decontaminated water, the effect of sewage disposal is improved, reduce the cost of sewage disposal.
Part is not described in detail by the present invention, is the known technology of those skilled in the art.
Although an embodiment of the present invention has been shown and described, for the ordinary skill in the art, can be with
A variety of changes, modification can be carried out to these embodiments, replace without departing from the principles and spirit of the present invention by understanding
And modification, the scope of the present invention is defined by the appended.
Claims (6)
1. a kind of integrated rural domestic sewage processing method, it is characterised in that specifically comprise the following steps:
S1:Sanitary sewage is filtered for the first time by grid solarium;
S2:The sewage treated by grid is discharged into setting pot, sedimentation separation removal is carried out to the sand in sewage;
S3:The sewage treated by setting pot is drained into first shallow lake pond, the sludge in sewage separate removing;
S4:The process sewage that just shallow lake pond treats is drained into biological treatment tank and handled;
S5:The sewage treated by biological treatment tank is drained into secondary sedimentation tank, the sludge in sewage carried out secondary
Precipitation;
S6:The sewage treated by secondary sedimentation tank is drained into coagulating sedimentation tank, CuSO is added in coagulating sedimentation tank4,
Per 1000m31.5-3 ㎏ CuSO is added in sewage4, the debris in sewage is precipitated again;
S7:The sewage treated by coagulating sedimentation tank is drained into filtering tank and carries out filtration treatment;
S8:After adding disinfectant in the liquid after filter tank filtering, the concentration for adding disinfectant is 0.15-0.30 ㎎/L.
A kind of 2. integrated rural domestic sewage processing method according to claim 1, it is characterised in that:To dirt in S3
After sludge in water is precipitated, logistics is flowed into slurries filter and filtered, and the sludge after filtering is flowed into mud concentration
Concentrated in tank.
A kind of 3. integrated rural domestic sewage processing method according to claim 1, it is characterised in that:To dirt in S5
Sludge in water carry out it is secondary after, partial sludge is flowed again into biological treatment tank and handled, and excess sludge is flowed into slurry
Filtered on liquid filter, the sludge after filtering is flowed into mud concentration tank and concentrated.
A kind of 4. integrated rural domestic sewage processing method according to Claims 2 or 3, it is characterised in that:The mud
Sludge after slurry concentration tank concentration is sent to slurry dewatering tank and is dehydrated.
A kind of 5. integrated rural domestic sewage processing method according to claim 1, it is characterised in that:In S8, institute
The composition of the disinfectant used is ClO2。
A kind of 6. integrated rural domestic sewage processing method according to claim 1, it is characterised in that:Added in S8
The temperature control of liquid is at 4 DEG C -6 DEG C during disinfectant.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201711059976.6A CN107628733A (en) | 2017-11-01 | 2017-11-01 | A kind of integrated rural domestic sewage processing method |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201711059976.6A CN107628733A (en) | 2017-11-01 | 2017-11-01 | A kind of integrated rural domestic sewage processing method |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CN107628733A true CN107628733A (en) | 2018-01-26 |
Family
ID=61106982
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201711059976.6A Withdrawn CN107628733A (en) | 2017-11-01 | 2017-11-01 | A kind of integrated rural domestic sewage processing method |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN107628733A (en) |
Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN110734198A (en) * | 2019-11-13 | 2020-01-31 | 佛山科学技术学院 | A kind of rural decentralized sewage treatment method |
| CN111704319A (en) * | 2020-06-30 | 2020-09-25 | 桂林理工大学 | A prefabricated modular municipal sewage treatment system and sewage treatment method |
| CN112607959A (en) * | 2020-11-26 | 2021-04-06 | 安徽海航环保科技有限公司 | Environment-friendly sewage treatment process |
| CN114804545A (en) * | 2022-05-31 | 2022-07-29 | 湖南久清环保工程有限公司 | Be applied to sewage purification treatment device that environment was administered |
-
2017
- 2017-11-01 CN CN201711059976.6A patent/CN107628733A/en not_active Withdrawn
Cited By (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN110734198A (en) * | 2019-11-13 | 2020-01-31 | 佛山科学技术学院 | A kind of rural decentralized sewage treatment method |
| CN111704319A (en) * | 2020-06-30 | 2020-09-25 | 桂林理工大学 | A prefabricated modular municipal sewage treatment system and sewage treatment method |
| CN111704319B (en) * | 2020-06-30 | 2023-06-16 | 桂林理工大学 | Prefabricated modularized municipal sewage treatment system and sewage treatment method |
| CN112607959A (en) * | 2020-11-26 | 2021-04-06 | 安徽海航环保科技有限公司 | Environment-friendly sewage treatment process |
| CN114804545A (en) * | 2022-05-31 | 2022-07-29 | 湖南久清环保工程有限公司 | Be applied to sewage purification treatment device that environment was administered |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| KR101346525B1 (en) | Device to cohere and to dispose of wastes water | |
| CN103204605B (en) | A kind of garlic processing wastewater treatment method | |
| CN107628733A (en) | A kind of integrated rural domestic sewage processing method | |
| CN102174763B (en) | Treatment method for paper making waste water | |
| KR102009674B1 (en) | Eco-friendly living sewage treatment system | |
| CN102701531A (en) | Slaughter sewage treatment method | |
| CN102086079B (en) | Method and system for zero-discharge treatment of domestic sewage | |
| CN105417862A (en) | Wastewater treatment system | |
| CN110981081A (en) | Municipal sewage centralized treatment method | |
| CN114315050A (en) | Intelligent centralized collection and treatment method of rural sewage | |
| CN205152011U (en) | Effluent disposal system slaughters | |
| CN103771666A (en) | Energy-saving slaughter wastewater treatment method | |
| CN108164038A (en) | A kind of Water feeding treatment device and processing method | |
| CN103803757A (en) | Bean product waste water treatment method | |
| CN208649061U (en) | Aquaculture wastewater recovery and processing system | |
| CN209161709U (en) | A kind of reusing industrial effluent processing equipment | |
| CN207468436U (en) | Urban sewage treatment system | |
| CN208577592U (en) | A kind of wastewater treatment integration apparatus | |
| CN208776538U (en) | A kind of domestic sewage processing system | |
| CN105884144A (en) | Process for efficiently treating sewage | |
| CN106745599B (en) | Non-crystalline silica inorganic agent and technique with its treated sewage | |
| CN116655134A (en) | Low-cost simple and easy formula aquaculture tail water treatment system | |
| KR101523515B1 (en) | A operation ship for cage culture | |
| CN108793649A (en) | A kind of meat processing waste water processing unit and method | |
| CN209740839U (en) | Multistage circulation sewage 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 | ||
| WW01 | Invention patent application withdrawn after publication | ||
| WW01 | Invention patent application withdrawn after publication |
Application publication date: 20180126 |