CN108793646A - A kind of landscape type domestic sewage ecologically treating system - Google Patents
A kind of landscape type domestic sewage ecologically treating system Download PDFInfo
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- CN108793646A CN108793646A CN201811047620.5A CN201811047620A CN108793646A CN 108793646 A CN108793646 A CN 108793646A CN 201811047620 A CN201811047620 A CN 201811047620A CN 108793646 A CN108793646 A CN 108793646A
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- 239000010865 sewage Substances 0.000 title claims abstract description 70
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 181
- 241000196324 Embryophyta Species 0.000 claims abstract description 47
- 238000005273 aeration Methods 0.000 claims abstract description 43
- 230000003647 oxidation Effects 0.000 claims abstract description 43
- 238000007254 oxidation reaction Methods 0.000 claims abstract description 43
- 241000251468 Actinopterygii Species 0.000 claims abstract description 33
- 240000002853 Nelumbo nucifera Species 0.000 claims abstract description 30
- 235000006508 Nelumbo nucifera Nutrition 0.000 claims abstract description 30
- 235000006510 Nelumbo pentapetala Nutrition 0.000 claims abstract description 30
- 241000238571 Cladocera Species 0.000 claims abstract description 23
- 238000001914 filtration Methods 0.000 claims abstract description 16
- 241000237858 Gastropoda Species 0.000 claims abstract description 14
- 238000005276 aerator Methods 0.000 claims abstract description 12
- 241000209490 Nymphaea Species 0.000 claims abstract description 5
- 235000016791 Nymphaea odorata subsp odorata Nutrition 0.000 claims abstract description 5
- 239000004927 clay Substances 0.000 claims description 16
- 241000252234 Hypophthalmichthys nobilis Species 0.000 claims description 7
- 238000000354 decomposition reaction Methods 0.000 claims description 7
- 230000012010 growth Effects 0.000 claims description 7
- 241000252233 Cyprinus carpio Species 0.000 claims description 6
- 241001124553 Lepismatidae Species 0.000 claims description 6
- 241001233037 catfish Species 0.000 claims description 6
- 235000013305 food Nutrition 0.000 claims description 6
- 238000012423 maintenance Methods 0.000 claims description 5
- 238000005507 spraying Methods 0.000 claims description 5
- 235000014676 Phragmites communis Nutrition 0.000 claims description 4
- 239000010828 animal waste Substances 0.000 claims description 4
- 230000003628 erosive effect Effects 0.000 claims description 3
- 239000011241 protective layer Substances 0.000 claims description 3
- 238000012545 processing Methods 0.000 abstract description 15
- 230000008901 benefit Effects 0.000 abstract description 8
- 241000195493 Cryptophyta Species 0.000 description 13
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 11
- 229910052760 oxygen Inorganic materials 0.000 description 11
- 239000001301 oxygen Substances 0.000 description 11
- 239000000463 material Substances 0.000 description 9
- 239000005416 organic matter Substances 0.000 description 8
- 230000009286 beneficial effect Effects 0.000 description 6
- 238000004140 cleaning Methods 0.000 description 6
- 230000000050 nutritive effect Effects 0.000 description 5
- 238000010586 diagram Methods 0.000 description 4
- 239000010802 sludge Substances 0.000 description 4
- 239000000126 substance Substances 0.000 description 4
- YUWBVKYVJWNVLE-UHFFFAOYSA-N [N].[P] Chemical compound [N].[P] YUWBVKYVJWNVLE-UHFFFAOYSA-N 0.000 description 3
- 230000008859 change Effects 0.000 description 3
- 230000000694 effects Effects 0.000 description 3
- 239000012634 fragment Substances 0.000 description 3
- 238000003306 harvesting Methods 0.000 description 3
- QGZKDVFQNNGYKY-UHFFFAOYSA-O Ammonium Chemical compound [NH4+] QGZKDVFQNNGYKY-UHFFFAOYSA-O 0.000 description 2
- 241000208340 Araliaceae Species 0.000 description 2
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- 235000005035 Panax pseudoginseng ssp. pseudoginseng Nutrition 0.000 description 2
- 235000003140 Panax quinquefolius Nutrition 0.000 description 2
- 230000009471 action Effects 0.000 description 2
- 230000005791 algae growth Effects 0.000 description 2
- 239000003153 chemical reaction reagent Substances 0.000 description 2
- 239000000356 contaminant Substances 0.000 description 2
- 230000029087 digestion Effects 0.000 description 2
- 238000007865 diluting Methods 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 235000008434 ginseng Nutrition 0.000 description 2
- 229910001385 heavy metal Inorganic materials 0.000 description 2
- 229910052751 metal Inorganic materials 0.000 description 2
- 238000000034 method Methods 0.000 description 2
- 244000005700 microbiome Species 0.000 description 2
- 238000006213 oxygenation reaction Methods 0.000 description 2
- 230000008569 process Effects 0.000 description 2
- 239000007921 spray Substances 0.000 description 2
- 241000894006 Bacteria Species 0.000 description 1
- 241001609213 Carassius carassius Species 0.000 description 1
- 241000192700 Cyanobacteria Species 0.000 description 1
- 206010021143 Hypoxia Diseases 0.000 description 1
- 229910002651 NO3 Inorganic materials 0.000 description 1
- NHNBFGGVMKEFGY-UHFFFAOYSA-N Nitrate Chemical compound [O-][N+]([O-])=O NHNBFGGVMKEFGY-UHFFFAOYSA-N 0.000 description 1
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 1
- 244000273256 Phragmites communis Species 0.000 description 1
- 241000235342 Saccharomycetes Species 0.000 description 1
- 238000010521 absorption reaction Methods 0.000 description 1
- 239000005422 algal bloom Substances 0.000 description 1
- 150000001413 amino acids Chemical class 0.000 description 1
- 230000001580 bacterial effect Effects 0.000 description 1
- 230000033228 biological regulation Effects 0.000 description 1
- 229910052793 cadmium Inorganic materials 0.000 description 1
- BDOSMKKIYDKNTQ-UHFFFAOYSA-N cadmium atom Chemical compound [Cd] BDOSMKKIYDKNTQ-UHFFFAOYSA-N 0.000 description 1
- 150000001720 carbohydrates Chemical class 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 239000003925 fat Substances 0.000 description 1
- 230000036541 health Effects 0.000 description 1
- 230000007954 hypoxia Effects 0.000 description 1
- 230000006872 improvement Effects 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 235000015097 nutrients Nutrition 0.000 description 1
- 229910052698 phosphorus Inorganic materials 0.000 description 1
- 239000011574 phosphorus Substances 0.000 description 1
- 102000004169 proteins and genes Human genes 0.000 description 1
- 108090000623 proteins and genes Proteins 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 239000002689 soil Substances 0.000 description 1
- 230000006641 stabilisation Effects 0.000 description 1
- 238000011105 stabilization Methods 0.000 description 1
- 230000009182 swimming Effects 0.000 description 1
- 231100000331 toxic Toxicity 0.000 description 1
- 230000002588 toxic effect Effects 0.000 description 1
Classifications
-
- 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
- C02F3/30—Aerobic and anaerobic 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
- C02F3/32—Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae
- C02F3/327—Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae characterised by animals and plants
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- Life Sciences & Earth Sciences (AREA)
- Engineering & Computer Science (AREA)
- Biodiversity & Conservation Biology (AREA)
- Microbiology (AREA)
- Hydrology & Water Resources (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Biotechnology (AREA)
- Botany (AREA)
- Biological Treatment Of Waste Water (AREA)
Abstract
The invention discloses a kind of landscape type domestic sewage ecologically treating systems, sanitary sewage is discharged into sewage holding pond, it is introduced in spiral aerator by water pump, it is introduced and is aerated by transparent conduit pipe afterwards, in anaerobic and aerobic biochemistry integral pool, biology is re-introduced into after processing to cultivate in oxidation pond I, being re-introduced into pond after processing has water lily and snail, water flea and the biochemical of a small amount of ominivore-fish are cultivated in oxidation pond II, being entered back into after processing has ominivore-fish and snail in pond, the biology of water plant and lotus class plant is cultivated in decomposing pool, it is finally discharged into and decomposes in pond, biology is cultivated also to enter after the water that decomposing pool overflows is filtered by ladder aeration filtration pond and be decomposed in pond, it decomposes pond a part of water is back to again in biology cultivation decomposing pool.Water body of the present invention itself can restore the normal ecosystem, save a large amount of people, object and financial resources；The sewage of processing can carry out the foster plant of fish, lotus class, form landscape type farm, generate economic benefit, and cost of sewage disposal is low.
Description
Technical field
The present invention relates to a kind of domestic sewage processing systems.
Background technology
Sanitary sewage is mainly made of organic matters such as carbohydrate, protein, amino acid, fat, nitrogen and phosphorus content
It is relatively high, so a large amount of algal growns, when algalbloom, water hypoxia is easily caused, especially cyanobacteria is also toxic,
It causes water quality to degenerate, fouls, so must handle sewage.Typically now sewage disposal is to kill algae with chemical substance
With other harmful microorganisms, and sewage precipitated, is digested, due to it was recognized that can be drawn with chemical substance treatment sewage
Into other harmful substances, secondary pollution, the poor quality of the water after processing are formed to water body；And face is taken up an area in this sewage disposal
Product is big, and big to the environmental pollution of treated sewage position, cost of sewage disposal is very high.For these features, sanitary sewage at present
Improvement has gradually been broken away from chemically and physically to combine to administer and shifted to biochemical processings such as artificial swamp, biofilter or stabilization ponds
Excessively, the rich nutritive material in sewage is absorbed using planting plants, limitation algae reproduction growth is further disliked to avoid water quality
Change.Wetland ecotourism processing combining form be：Oxidation pond+current wetland+surface-flow.Sewage is biochemical after oxidation pond oxidation
Organic matter, then be absorbed and utilized through the water plant in surface-flow etc., to achieve the purpose that administer sewage.But due to plant
It is slow to absorb rich nutritive material speed, wants to reach regulation effect, plant Wetland Area must be big, otherwise cannot meet at large amount of sewage
Reason demand；And later maintenance is again too cumbersome, to ensure that the sustainable operation of artificial swamp, later stage need to put into a large amount of people
Power, material resources, financial resources, including the harvesting of plant residue, the cleaning of Oxidation Pond Sludge and salvage surface-flow, current wetland, water channel
Logical silt cleaning etc., so maintenance and management be wetland ecotourism processing fatal crux；And due to the poor water mass in wetland, institute
The plant of kind plantation cannot form economic benefit, and cost of sewage disposal is very high.
Invention content
Purpose of the present invention is to solve the above-mentioned problems in the prior art, provide at a kind of landscape type domestic sewage ecological
Reason system, the processing system water body itself can restore the normal ecosystem, without the harvesting of plant residue, Oxidation Pond Sludge
The work such as cleaning and the logical silt cleaning of salvaging surface-flow, current wetland, water channel, save a large amount of human and material resources and financial resources；Nothing
Any reagent treatment for having secondary pollution to water need to be added；And the sewage index of processing can reach the standard of Pyatyi water or more, no
The heavy metal contaminants such as leaded, cadmium can carry out the foster plant of fish, lotus class etc. in the subsequent pond of sewage disposal, form scape
Guan Shi farms see for ginseng, generate economic benefit, and cost of sewage disposal is low.
To achieve the above object, the technical solution that the present invention uses is：A kind of landscape type domestic sewage ecological processing
System, including sewage holding pond, water pump, spiral aerator, diversion transparent pipeline, aeration, anaerobic and aerobic biochemistry integral pool,
Biology cultivates oxidation pond I, biochemical cultivation oxidation pond II, biology and cultivates decomposing pool, ladder aeration filtration pond, buffer pool and decomposing pool
The pool；Sanitary sewage is introduced into sewage holding pond, and sewage holding pond is connected the water inlet of spiral aerator by water pump, and spiral exposes
The water inlet of the water outlet connection diversion transparent pipeline of device of air, the water outlet connection aeration of diversion transparent pipeline, anaerobism are become reconciled
The water inlet of oxygen biochemistry integral pool；It is aerated, the water outlet of the separate water inlet of anaerobic and aerobic biochemistry integral pool is connected by pipeline
Biology cultivates the top water inlet of oxidation pond I；Biology cultivates the top water outlet of the separate top water inlet of oxidation pond I by pipe
The biochemical top water inlet for cultivating oxidation pond II of road connection, the top that biochemistry cultivates the separate top water inlet of oxidation pond II goes out
The mouth of a river is connected the top water inlet that biology cultivates decomposing pool by pipeline, and biology cultivates the top of the separate top water inlet of decomposing pool
Water outlet is connected by downward inclined pipe and decomposes pond；Biology cultivates decomposing pool and is also provided with gap in top water outlet one end,
The gap connects the staged water inlet in ladder aeration filtration pond by one or more overflow pipe, ladder aeration filtration pond
Upper end water outlet is connected another water inlet for decomposing pond by pipeline；The water decomposed in pond leads to buffer pool by another water pump
Interior, the top water outlet of buffer pool connects the water inlet that biology cultivates another separate upper part water outlet of decomposing pool by pipeline；
The aeration, anaerobic and aerobic biochemistry integral pool are longer shallower, and front end water inlet is covered with the protective layer of erosion control pool wall, rear portion
By the animal wastes of filter screen holding maintenance fermented, the size in water velocity and pond ensures sewage by this pond for addition
Time is 2 hours or more；It is clay that the biology, which cultivates I bottom of pond of oxidation pond, and being grown in pond has lotus class plant, has water in pond
The size in flea, water velocity and pond ensures that the time that sewage passes through this pond is 2 hours or more；The biochemical cultivation oxidation pond
II bottom of pond is clay, interior growth has a water lily, also snail, water flea and using water flea and plankton be on a small quantity that food removes silver carp
The size in ominivore-fish in addition, water velocity and pond ensures that the time that sewage passes through this pond is 2 hours or more；Described
It is clay that biology, which cultivates decomposing pool bottom of pond, and interior support has using water flea and phytoplankton as the ominivore-fish of food and snail, plantation
There are a water plant and lotus class plant, the size in water velocity and pond ensures that sewage by the time in this pond is 12 hours or more；It is described
Decomposition pond bottom of pond be clay, interior main support has filter-feeding fish silver carp and bighead, at the same also support have snakeheaded fish, catfish, carp,
The omnivorous fish such as crucian, silverfish, ornamental fish and screw, kind are implanted with water plant and reed etc.；Ladder aeration filtration pond front end is
Multiple ladders higher than pond are aerated water inlet, and bottom of pond is clay, and kind lotus class plant and water plant, a small amount of fish etc. are implanted in pond.
Sanitary sewage is discharged into sewage holding pond and carries out purification sludge settling.Then spiral aerator is introduced by water pump
It is interior, it is aerated during helical feed, activates molecular structure water, increase dissolved oxygen.Then it is introduced by transparent conduit pipe
In aeration, anaerobic and aerobic biochemistry integral pool, sunlight is in transparent conduit pipe, the microorganism in preliminary biochemistry water body,
Hydrone is further activated by the flowing of water body；In aeration, anaerobic and aerobic biochemistry integral pool aeration oxygen replenishing outdoor first, add
Volatile material is taken out of the water surface by strong nitrification ammonium ion, and preliminary exposition organic matter can at plant the ammonium nitrification of nonabsorable
The nitrate of absorption adds the animal wastes fermented in the pond of rear portion, changes the N/P ratio of water body, make beneficial algae and water
The growing environment of the planktonic organisms such as flea, meanwhile, containing beneficial bacteriums such as a large amount of saccharomycete in the excrement fermented, increase bacterial population
Amount, enhances the capacity of decomposition of water body.Sewage is re-introduced into biology and cultivates in oxidation pond I, and since environment is suitable, beneficial algae is in preliminary
Growing, the rich nutritive materials such as a large amount of nitrogen phosphorus absorbed in water bodys；Water flea eats algae in pond；The change of the lotus class plant of growth
Sense effect inhibits blue algae growth, absorbs rich nutritive material in lotus class growing process；Bottom of pond clay has stronger adsorptivity,
Organic matter and metallic element can largely be adsorbed；By diluting water body oxygenation, capacity of decomposition is further strengthened.Sewage is re-introduced into
Biochemistry is cultivated in oxidation pond II, which inhibits blue algae growth, interior growth beneficial algae and water lily, a large amount of nitrogen phosphorus absorbed in water body
Equal rich nutritive materials, while intervening fish, snail, are allowed to be formed preliminary ecological circulation, and fish eat water flea, and water flea eats algae
Class；A small amount of wind vane of the fish as water treatment effect adjusts the amount of being discharged into of sewage with the health condition of fish；Bottom of pond is glutinous
Soil has stronger adsorptivity, can largely adsorb organic matter and metallic element；By diluting water body oxygenation, further strengthen
Capacity of decomposition.Treated, and sewage enters back into biology cultivation decomposing pool, this pond is undercurrent pond, the battalion that biochemical front has been decomposed
It supports substance and generates algae, the remnant organic matters such as fish and snail digestion algae, water flea, water flea corpse and organic matter fragment；Water plant
Continue biochemical remaining nutriment with lotus class plant to be digested and assimilated；So far, a large amount of nutrient rich such as nitrogen phosphorus in sewage
Matter is absorbed substantially, and beneficial algae is eaten by water flea, fish and snail in water, and water flea, water flea corpse and organic matter fragment etc. are residual
Remaining organic matter is eaten by fish and snail, will not be polluted again to water body, and the aquatic plants such as algae, water plant and lotus class plant
The oxygen of generation can support the growth of water flea, fish and snail completely, form good water body environment, be come out in water outlet
Treated, and water can reach the standard of five class water.Finally these water of handling that treated well are discharged into and decomposes pond memory and puts,
The omnivorous fish such as silver carp and bighead filter-feeding fish, snakeheaded fish, catfish, carp, crucian, silverfish, ornamental fish and screw are also in pond
Continue remnant organic matters, beneficial algae, water plant and the reeds such as digestion algae, water flea, water flea corpse and organic matter fragment to continue to disappear
Consume nutriment.When biology, which cultivates the water in decomposing pool, is higher than gap, the water being higher by is spilled off ladder aeration filtration
In pond, to keep biology to cultivate the water level of decomposing pool, and the water overflowed is aerated water inlet by the ladder in ladder aeration filtration pond
It is further filtered by the plant in it in into ladder aeration filtration pond, keeps water quality more preferable；These are further processed
Sewage be discharged into decompose pond in, keep the water quality in decomposition pond more preferable.Periodically fishing fish, snail, taken at regular intervals lotus rhizome, lotus
The plants such as son, lotus leaf, these can generate economic benefit, and generate ornamental type, form garden type sewage disposal system.Due to dirt
The water quality of water process can reach the standard of Pyatyi water or more, so, it is well suited for this cultivation, generates economic benefit, generates ornamental
Benefit, so, the processing cost of this sewage disposal system is very low, the later stage generate economic benefit can be more than sewage disposal at
This.
In short, sewage ecological treatment system water body itself of the present invention can restore the normal ecosystem, it is not necessarily to plant residue
Harvesting, Oxidation Pond Sludge cleaning and the work such as the logical silt cleaning of salvaging surface-flow, current wetland, water channel, save a large amount of
Human and material resources and financial resources；Without adding any reagent treatment for having secondary pollution to water；And the sewage index of processing can reach
Or it is very suitable for cultivating, behind sewage disposal without heavy metal contaminants such as lead, cadmiums more than standard more than Pyatyi water
Pond interior energy carry out the foster plant of fish, lotus class etc., form landscape type farm, seen for ginseng, generate economic benefit, sewage
Processing cost is low.Table 1 is test comparison value table.
Table 1
It is further preferred that the invention also includes be connected to the biochemical centre cultivated between oxidation pond II and biology cultivation decomposing pool
Aeration tank；The top water inlet of intermediate aeration tank is connected to the biochemical top water outlet for cultivating oxidation pond II by pipeline,
Top water outlet is connected to the top water inlet that the biology cultivates decomposing pool by pipeline；It is there are one in intermediate aeration tank or multiple
Disc water spraying device.Disc water spraying device sprays to water in the air under the action of water pump, flows back in pond again after contacting with the air, makes
Water is fully aerated, and activates hydrone, increases dissolved oxygen, is kept the oxygen for entering biology cultivation decomposing pool more abundant, is sufficiently fed
Biology cultivates oxygen in decomposing pool.
It is further preferred that the spiral aerator includes the outer shell-and-tube inner-spiral type sluice of circular pipe type, pipe
Air inlet block valve is installed, air inlet block valve connects air pump on the outer wall of formula shell.
It is further preferred that it is preferably lotus that the biology, which cultivates the lotus class plant grown in I pond of oxidation pond,.
Description of the drawings
Fig. 1 is the structural schematic diagram of the first embodiment of the invention；
Fig. 2 is by the structural schematic diagram of second of embodiment of the invention；
Fig. 3 is the internal structure schematic diagram of spiral aerator in the present invention；
Fig. 4 is the internal structure schematic diagram of intermediate aeration tank in the present invention.
Specific implementation mode:
The invention will be further described with reference to the accompanying drawings and detailed description.
Embodiment 1 shown in as shown in Figure 1, Figure 3 and Figure 4, the present embodiment include sewage holding pond 1, water pump 2, spiral aeration dress
3 are set, diversion transparent pipeline 4, aeration, anaerobic and aerobic biochemistry integral pool 5, biology cultivates oxidation pond I 6, biochemistry cultivates oxidation pond
II 7, biology cultivates decomposing pool 8, ladder aeration filtration pond 16, buffer pool 11 and decomposes pond 9.Sanitary sewage is introduced into sewage
In holding pond 1, sewage holding pond 1 is connected the water inlet of spiral aerator 3 by water pump 2, and the water outlet of spiral aerator 3 connects
Connect the water inlet of diversion transparent pipeline 4, the water outlet connection aeration of diversion transparent pipeline 4, anaerobic and aerobic biochemistry integral pool 5
Water inlet.Preferably, the spiral aerator 3 includes circular pipe type shell 19 and pipe inner-spiral type sluice 20, circular pipe type
Air inlet block valve 18 is installed, air inlet block valve 18 connects air pump on the outer wall of shell 19.The biochemical one of aeration, anaerobic and aerobic
The water outlet of the separate water inlet in pond 5 is connected the top water inlet that biology cultivates oxidation pond I 6 by pipeline.Biology cultivates oxidation pond
The top water outlet of I 6 separate top water inlet connects the biochemical top water inlet for cultivating oxidation pond II 7 by pipeline, raw
The top water outlet for changing the separate top water inlet for cultivating oxidation pond II 7 connects the upper of biology cultivation decomposing pool 8 by pipeline
Portion's water inlet, the top water outlet that biology cultivates the separate top water inlet of decomposing pool 8 connect decomposing pool by downward inclined pipe
The pool 9.Biology cultivates decomposing pool 8 and is also provided with gap in top water outlet one end, which passes through one or more overflow pipe
（The present embodiment is 2）Connect the staged water inlet in ladder aeration filtration pond 16, the upper end water outlet in ladder aeration filtration pond 16
Mouth is connected by pipeline and decomposes pond 9.Decompose pond 9 in water led in buffer pool 11 by another water pump 10, buffer pool 11 it is upper
Portion's water outlet is connected the water inlet that biology cultivates another separate upper part water outlet of decomposing pool 8 by pipeline.The aeration is detested
Oxygen and aerobic biochemical integral pool 5 are longer shallower, and front end water inlet is covered with the protective layer of erosion control pool wall, and rear portion is added by filter screen
The size in the animal wastes of holding maintenance fermented, water velocity and pond ensures that the time that sewage passes through this pond is 2 hours
More than.It is clay that the biology, which cultivates I 6 bottom of pond of oxidation pond, and being grown in pond has lotus class plant, the lotus class plant of the present embodiment
For lotus, there is water flea in pond, the size in water velocity and pond ensures that sewage by the time in this pond is 2 hours or more.It is described
Biochemical II 7 bottom of pond of oxidation pond of cultivating be clay, interior growth has a water lily, also snail, water flea and on a small quantity with water flea and plant of swimming
Object is the ominivore-fish in addition to silver carp of food：Such as snakeheaded fish, catfish, carp, crucian, silverfish, ornamental fish and screw,
Water velocity and the size in pond ensure that the time that sewage passes through this pond is 2 hours or more.The biology cultivates 8 bottom of pond of decomposing pool
For clay, interior support has using water flea and phytoplankton as the ominivore-fish of food and snail, fish such as snakeheaded fish, catfish, carp, crucian carp
Fish, silverfish, ornamental fish and screw etc.；Kind is implanted with water plant and lotus class plant, and the lotus class plant of the present embodiment is lotus；Its water flow velocity
The size in degree and pond ensures that the time that sewage passes through this pond is 12 hours or more.9 bottom of decomposition pond pond is clay, interior master
It has supported filter-feeding fish silver carp and bighead, while also having supported and have snakeheaded fish, catfish, carp, crucian, silverfish, ornamental fish and screw etc.
Omnivorous fish；Kind is implanted with water plant and reed etc..Ladder aeration filtration pond front end be multiple ladders higher than pond be aerated into
The mouth of a river, bottom of pond are clay, and kind lotus class plant and water plant, a small amount of fish etc. are implanted in pond.
Embodiment 2 as shown in Figure 2, Figure 3 and Figure 4, the other structures of the present embodiment are with embodiment 1, the only embodiment
Further include being connected to the biochemical intermediate aeration tank 13 cultivated between oxidation pond II 7 and biology cultivation decomposing pool 8.Intermediate aeration tank
13 top water inlet is connected to the biochemical top water outlet for cultivating oxidation pond II 7 by pipeline, and upper part water outlet is by pipe
Road is connected to the top water inlet that the biology cultivates decomposing pool 8.In intermediate aeration tank there are one or multiple disc water spraying devices
14.Disc water spraying device 14 sprays to water in the air under the action of another water pump 15, flows back in pond again after contacting with the air, makes water
Fully aeration activates hydrone, increases dissolved oxygen, keeps the oxygen for cultivating decomposing pool into biology more abundant, is sufficiently fed life
Object cultivates oxygen in decomposing pool.
Above-described embodiment is only preferred and illustrative, and those skilled in the art can do according to the description of this patent
Change with technology, is all covered by the protection domain of this patent.
Claims (5)
1. a kind of landscape type domestic sewage ecologically treating system, it is characterised in that：Including sewage holding pond, water pump, spiral aeration
Device, diversion transparent pipeline, aeration, anaerobic and aerobic biochemistry integral pool, biology cultivates oxidation pond I, biochemistry cultivates oxidation pond II,
Biology cultivates decomposing pool, ladder aeration filtration pond, buffer pool and decomposes pond；Sanitary sewage is introduced into sewage holding pond, dirty
Water holding pond is connected the water inlet of spiral aerator by water pump, the water outlet connection diversion transparent pipeline of spiral aerator
Water inlet, the water outlet connection aeration of diversion transparent pipeline, the water inlet of anaerobic and aerobic biochemistry integral pool；Aeration, anaerobism and
The water outlet of the separate water inlet of aerobic biochemical integral pool is connected the top water inlet that biology cultivates oxidation pond I by pipeline；Biology
The top water outlet for cultivating the separate top water inlet of oxidation pond I connects the biochemical top water inlet for cultivating oxidation pond II by pipeline
Mouthful, the top water outlet that biochemistry cultivates the separate top water inlet of oxidation pond II cultivates the upper of decomposing pool by pipeline connection biology
Portion's water inlet, the top water outlet that biology cultivates the separate top water inlet of decomposing pool connect decomposing pool by downward inclined pipe
The pool；Biology cultivates decomposing pool and is also provided with gap in top water outlet one end, which is connected by one or more overflow pipe
The staged water inlet in ladder aeration filtration pond is connect, the upper end water outlet in ladder aeration filtration pond is connected by pipeline decomposes pond
Another water inlet；The water decomposed in pond is led to by another water pump in buffer pool, and the top water outlet of buffer pool is connected by pipeline
Biology cultivates the water inlet of another separate upper part water outlet of decomposing pool；The aeration, anaerobic and aerobic biochemistry integral pool
Longer shallower, front end water inlet is covered with the protective layer of erosion control pool wall, and fermenting by filter screen holding maintenance is added at rear portion
The size in animal wastes, water velocity and pond ensures that the time that sewage passes through this pond is 2 hours or more；The biology is cultivated
I bottom of pond of oxidation pond is clay, and being grown in pond has lotus class plant, there is water flea, the size guarantee sewage of water velocity and pond in pond
Time by this pond is 2 hours or more；Biochemical II bottom of pond of oxidation pond of cultivating is clay, and interior growth has water lily, also
Snail, water flea and on a small quantity using water flea and plankton as the ominivore-fish in addition to silver carp of food, water velocity and
The size in pond ensures that the time that sewage passes through this pond is 2 hours or more；It is clay that the biology, which cultivates decomposing pool bottom of pond, interior to support
Have using water flea and phytoplankton as the ominivore-fish of food and snail, kind is implanted with water plant and lotus class plant, water velocity and
The size in pond ensures that the time that sewage passes through this pond is 12 hours or more；The decomposition pond bottom of pond is clay, interior main foster
There are filter-feeding fish silver carp and a bighead, while also supporting and there are omnivorous fish：Snakeheaded fish, catfish, carp, crucian, silverfish, ornamental fish and spiral shell
Silk, kind are implanted with water plant and reed；Ladder aeration filtration pond front end is that multiple ladders higher than pond are aerated water inlet, bottom of pond
Kind it is implanted with lotus class plant and water plant, a small amount of fish for clay, in pond.
2. landscape type domestic sewage ecologically treating system according to claim 1, it is characterised in that：It further includes being connected to
Biochemistry cultivates the intermediate aeration tank between oxidation pond II and biology cultivation decomposing pool；The top water inlet of intermediate aeration tank is by pipeline
It is connected to the biochemical top water outlet for cultivating oxidation pond II, upper part water outlet is connected to the biology and is cultivated by pipeline to be divided
The top water inlet of Xie Chi；In intermediate aeration tank there are one or multiple disc water spraying devices.
3. landscape type domestic sewage ecologically treating system according to claim 1 or 2, it is characterised in that：The spiral
Aerator includes the outer shell-and-tube inner-spiral type sluice of circular pipe type, and air inlet block valve is equipped on the outer wall of circular pipe type shell,
Air inlet
Block valve connects air pump.
4. landscape type domestic sewage ecologically treating system according to claim 3, it is characterised in that：The biology is cultivated
The lotus class plant grown in I pond of oxidation pond is lotus.
5. landscape type domestic sewage ecologically treating system according to claim 1 or 2, it is characterised in that：The biology
It is lotus to cultivate the lotus class plant grown in I pond of oxidation pond.
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Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN107619153A (en) * | 2017-09-25 | 2018-01-23 | 罗定市丰智酒业有限公司 | A kind of liquor production wastewater biodegradation system Construction method |
| CN112537848A (en) * | 2020-11-30 | 2021-03-23 | 华川技术有限公司 | Process for improving quality of tail water of sewage plant |
Citations (12)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH11128990A (en) * | 1997-10-30 | 1999-05-18 | Shimizu Corp | Water quality clarification apparatus |
| KR20030086176A (en) * | 2002-05-03 | 2003-11-07 | 주식회사 진명엔지니어링건축사사무소 | System to make up the mode of ecological park in apartment |
| KR20080007964A (en) * | 2006-07-19 | 2008-01-23 | 상 을 이 | A waste water natural purgation system using aquatic trees and plants |
| CN102234165A (en) * | 2010-04-28 | 2011-11-09 | 中国科学院生态环境研究中心 | System for purifying sewage with constructed wetland, and system method for purifying pollution source water from water works |
| CN102351378A (en) * | 2011-07-12 | 2012-02-15 | 江西致远环保技术有限公司 | Method and system for processing rural sewage in artificial wetlands |
| CN102923906A (en) * | 2012-10-24 | 2013-02-13 | 天津大学 | Campus landscape water-body water-quality maintaining and self-purifying system integrating functions of landscape and biological ecological restoration |
| CN103159383A (en) * | 2013-04-15 | 2013-06-19 | 云南省科学技术情报研究院 | Rural domestic sewage biological treatment system |
| CN103253822A (en) * | 2012-05-25 | 2013-08-21 | 河海大学 | Compound constructed wetland tail water treatment system |
| CN104058545A (en) * | 2013-03-18 | 2014-09-24 | 平湖市新埭镇周玉良牧场 | Method for treating aquaculture sewage through combination of biological carrier and ecological restoration technology |
| CN204237675U (en) * | 2014-08-29 | 2015-04-01 | 温州大学 | One way of life sewage disposal and reclaiming system |
| CN104496106A (en) * | 2014-10-30 | 2015-04-08 | 杭州师范大学 | Campus rainwater ecological cleaning integrated-processing method and ecological cleaning integration system |
| CN208732878U (en) * | 2018-09-10 | 2019-04-12 | 河北雄安德荫源环境科技有限公司 | A kind of landscape type domestic sewage ecologically treating system |
-
2018
- 2018-09-10 CN CN201811047620.5A patent/CN108793646B/en active Active
Patent Citations (12)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH11128990A (en) * | 1997-10-30 | 1999-05-18 | Shimizu Corp | Water quality clarification apparatus |
| KR20030086176A (en) * | 2002-05-03 | 2003-11-07 | 주식회사 진명엔지니어링건축사사무소 | System to make up the mode of ecological park in apartment |
| KR20080007964A (en) * | 2006-07-19 | 2008-01-23 | 상 을 이 | A waste water natural purgation system using aquatic trees and plants |
| CN102234165A (en) * | 2010-04-28 | 2011-11-09 | 中国科学院生态环境研究中心 | System for purifying sewage with constructed wetland, and system method for purifying pollution source water from water works |
| CN102351378A (en) * | 2011-07-12 | 2012-02-15 | 江西致远环保技术有限公司 | Method and system for processing rural sewage in artificial wetlands |
| CN103253822A (en) * | 2012-05-25 | 2013-08-21 | 河海大学 | Compound constructed wetland tail water treatment system |
| CN102923906A (en) * | 2012-10-24 | 2013-02-13 | 天津大学 | Campus landscape water-body water-quality maintaining and self-purifying system integrating functions of landscape and biological ecological restoration |
| CN104058545A (en) * | 2013-03-18 | 2014-09-24 | 平湖市新埭镇周玉良牧场 | Method for treating aquaculture sewage through combination of biological carrier and ecological restoration technology |
| CN103159383A (en) * | 2013-04-15 | 2013-06-19 | 云南省科学技术情报研究院 | Rural domestic sewage biological treatment system |
| CN204237675U (en) * | 2014-08-29 | 2015-04-01 | 温州大学 | One way of life sewage disposal and reclaiming system |
| CN104496106A (en) * | 2014-10-30 | 2015-04-08 | 杭州师范大学 | Campus rainwater ecological cleaning integrated-processing method and ecological cleaning integration system |
| CN208732878U (en) * | 2018-09-10 | 2019-04-12 | 河北雄安德荫源环境科技有限公司 | A kind of landscape type domestic sewage ecologically treating system |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN107619153A (en) * | 2017-09-25 | 2018-01-23 | 罗定市丰智酒业有限公司 | A kind of liquor production wastewater biodegradation system Construction method |
| CN112537848A (en) * | 2020-11-30 | 2021-03-23 | 华川技术有限公司 | Process for improving quality of tail water of sewage plant |
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| Publication number | Publication date |
|---|---|
| CN108793646B (en) | 2024-06-11 |
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