CN110498508A - A kind of Quick percolation apparatus and the method using its progress sewage treatment - Google Patents
A kind of Quick percolation apparatus and the method using its progress sewage treatment Download PDFInfo
- Publication number
- CN110498508A CN110498508A CN201910779626.XA CN201910779626A CN110498508A CN 110498508 A CN110498508 A CN 110498508A CN 201910779626 A CN201910779626 A CN 201910779626A CN 110498508 A CN110498508 A CN 110498508A
- Authority
- CN
- China
- Prior art keywords
- layer
- metalling
- height
- ventilation pipe
- percolation apparatus
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Granted
Links
- 238000005325 percolation Methods 0.000 title claims abstract description 55
- 239000010865 sewage Substances 0.000 title claims abstract description 47
- 238000000034 method Methods 0.000 title claims abstract description 30
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 75
- 238000001179 sorption measurement Methods 0.000 claims abstract description 50
- 238000001914 filtration Methods 0.000 claims abstract description 40
- 239000000843 powder Substances 0.000 claims abstract description 37
- 239000004576 sand Substances 0.000 claims abstract description 34
- 239000002023 wood Substances 0.000 claims abstract description 32
- 238000009423 ventilation Methods 0.000 claims description 56
- 239000011148 porous material Substances 0.000 claims description 12
- 235000019738 Limestone Nutrition 0.000 claims description 9
- 239000006028 limestone Substances 0.000 claims description 9
- 239000003463 adsorbent Substances 0.000 claims description 7
- 235000017166 Bambusa arundinacea Nutrition 0.000 claims description 5
- 235000017491 Bambusa tulda Nutrition 0.000 claims description 5
- 241001330002 Bambuseae Species 0.000 claims description 5
- 235000015334 Phyllostachys viridis Nutrition 0.000 claims description 5
- 239000011425 bamboo Substances 0.000 claims description 5
- 239000003610 charcoal Substances 0.000 claims description 5
- 239000000571 coke Substances 0.000 claims description 5
- 239000000203 mixture Substances 0.000 claims description 5
- 238000010521 absorption reaction Methods 0.000 claims description 4
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 abstract description 15
- 239000010802 sludge Substances 0.000 abstract description 9
- 229910052757 nitrogen Inorganic materials 0.000 abstract description 7
- 238000010992 reflux Methods 0.000 abstract description 5
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 abstract description 4
- 229910052760 oxygen Inorganic materials 0.000 abstract description 4
- 239000001301 oxygen Substances 0.000 abstract description 4
- XKMRRTOUMJRJIA-UHFFFAOYSA-N ammonia nh3 Chemical compound N.N XKMRRTOUMJRJIA-UHFFFAOYSA-N 0.000 description 20
- 239000000706 filtrate Substances 0.000 description 8
- 239000005416 organic matter Substances 0.000 description 8
- 230000000694 effects Effects 0.000 description 7
- 230000008595 infiltration Effects 0.000 description 7
- 238000001764 infiltration Methods 0.000 description 7
- 230000009286 beneficial effect Effects 0.000 description 6
- 239000000463 material Substances 0.000 description 5
- 244000005700 microbiome Species 0.000 description 5
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 4
- 238000011026 diafiltration Methods 0.000 description 4
- 238000005516 engineering process Methods 0.000 description 4
- 229910052698 phosphorus Inorganic materials 0.000 description 4
- 239000011574 phosphorus Substances 0.000 description 4
- 235000008733 Citrus aurantifolia Nutrition 0.000 description 3
- 235000011941 Tilia x europaea Nutrition 0.000 description 3
- 238000006243 chemical reaction Methods 0.000 description 3
- 239000004744 fabric Substances 0.000 description 3
- 239000000945 filler Substances 0.000 description 3
- 239000004571 lime Substances 0.000 description 3
- 239000004575 stone Substances 0.000 description 3
- 239000002351 wastewater Substances 0.000 description 3
- VTYYLEPIZMXCLO-UHFFFAOYSA-L Calcium carbonate Chemical compound [Ca+2].[O-]C([O-])=O VTYYLEPIZMXCLO-UHFFFAOYSA-L 0.000 description 2
- 238000005273 aeration Methods 0.000 description 2
- 230000015556 catabolic process Effects 0.000 description 2
- 230000007812 deficiency Effects 0.000 description 2
- 238000006731 degradation reaction Methods 0.000 description 2
- 229910052761 rare earth metal Inorganic materials 0.000 description 2
- 150000002910 rare earth metals Chemical class 0.000 description 2
- 239000002689 soil Substances 0.000 description 2
- 239000004411 aluminium Substances 0.000 description 1
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 description 1
- 229910052782 aluminium Inorganic materials 0.000 description 1
- 229910002114 biscuit porcelain Inorganic materials 0.000 description 1
- 229910000019 calcium carbonate Inorganic materials 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 239000006185 dispersion Substances 0.000 description 1
- 238000005265 energy consumption Methods 0.000 description 1
- 244000144972 livestock Species 0.000 description 1
- 238000005065 mining Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 238000006396 nitration reaction Methods 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 244000144977 poultry Species 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 230000011218 segmentation 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
- C02F3/301—Aerobic and anaerobic treatment in the same reactor
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Biodiversity & Conservation Biology (AREA)
- Microbiology (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Water Treatment By Sorption (AREA)
- Biological Treatment Of Waste Water (AREA)
- Treatment Of Biological Wastes In General (AREA)
Abstract
The invention discloses a kind of Quick percolation apparatus and the methods for carrying out sewage treatment using it, belong to technical field of sewage.The Quick percolation apparatus, including water inlet, water distributor, filtering layer area and snorkel;The filtering layer area is followed successively by coarse sands layer, wood powder layer, first adsorption layer, the first reservoir bed, the first metalling, the second metalling, fine sand layer, the second adsorption layer, the second reservoir bed, third metalling and drainage blanket from top to bottom.The invention also discloses a kind of methods for carrying out sewage treatment using above-mentioned Quick percolation apparatus.Quick percolation apparatus of the invention, nitrogen removal rate 50%-80%, COD removal rate are 80%-95%, without being aerated oxygen supply and sludge reflux, save power consumption;Excess sludge is not generated, secondary pollution is reduced;Structure is simple, easy to operate, occupied area is small, and capital expenditure is few.
Description
Technical field
The present invention relates to a kind of Quick percolation apparatus and the methods for carrying out sewage treatment using it, belong to sewage disposal technology
Field.
Background technique
The removal of ammonia nitrogen in sewage is important performance assessment criteria.Conventional technique generally takes A2/ O, A/O, SBR, segmentation
Aerated oxidation ditch etc..
These techniques are required to a nitrification tank or nitration section, are then refluxed for anaerobic pond (or anaerobism section) just playing instead
Nitrify denitrification.It is required that controlling strictly sludge age in nitrification tank, to ensure longer sludge age, preferable nitrification is just had
Effect.Therefore the reflux ratio of whole system requires larger, and whole energy consumption is higher.The construction cost of multiple reaction tanks, management difficulty
It is higher.
The deficiencies of techniques such as Anammox, short-cut nitrification and denitrification, it is poor that there is also technology stabilities, and application is poor, no
It is main denitrification process to be applied.
Quickly diafiltration is a kind of Novel sewage eco-treatment technology developed in recent years, is applicable not only at sanitary sewage
Reason, the purification for being also admirably suitable for polluted river water improve.The technology mostly uses the good crude media of permeance property as master
Material is percolated instead of natural soil layer, the advantage of artificial swamp and conventional soil filtration system is combined, particularly suitable for sewage
Source dispersion, the incomplete rural area of sewage treatment facility or outlying district.Traditional rapid infiltration system is to low-concentration ammonia-nitrogen (NH3-
N < 50mg/L) removal effect it is preferable, it is often insufficient up to 80% or more, however poor to the removal effect of total nitrogen (TN)
30%, it is difficult to qualified discharge.When ammonia nitrogen in sewage concentration is higher, conventional filtration system treatment effect is poor.
In consideration of it, it is necessary to study a kind of new Quick percolation apparatus, so as to solve the deficiencies in the prior art.
Summary of the invention
An object of the present invention is to provide a kind of Quick percolation apparatus.Quick percolation apparatus of the invention, in water inlet
COD concentration < 1000mg/L, when the ammonia nitrogen concentration of water inlet is 300-400mg/L, by Quick percolation apparatus of the invention, ammonia nitrogen
Removal rate reaches 70-90%, and nitrogen removal rate 10%-30%, COD removal rate reaches 40%-70%, and treatment effeciency is high.
The technical scheme to solve the above technical problems is that a kind of Quick percolation apparatus, including water inlet, water distribution
Pipe, filtering layer area and snorkel;The water distributor is connected with the water inlet, and the water distributor is positioned horizontally in the filtering layer area
Top, water distributor lower end interval are provided with multiple water distributing pores;The filtering layer area be followed successively by from top to bottom coarse sands layer, wood powder layer,
First adsorption layer, the first reservoir bed, the first metalling, the second metalling, fine sand layer, the second adsorption layer, the second reservoir bed, third
Metalling and drainage blanket;It is transversely provided with the first ventilation pipe in first metalling, is laterally set in the third metalling
There is the second ventilation pipe;Uniform intervals are provided with several air vents on the side wall of the first ventilation pipe and the second ventilation pipe;Institute
The lower end and middle part for stating snorkel are separately connected one end of the second ventilation pipe and the first ventilation pipe positioned at the same side
The upper end of nozzle, the snorkel is higher than 30cm-50cm at the top of the coarse sands layer;Draining is transversely provided in the drainage blanket
Pipe, treated, and sewage is discharged through the water outlet of the drainpipe.
The principle of the present invention is:
First, the present invention improves the structure in filtering layer area.From top, filtrate follows " thick → thin → thick → thin "
Rule, and between coarse sands layer and the first metalling be equipped with the first reservoir bed, be equipped between fine sand layer and third metalling
Second reservoir bed is respectively arranged with the first ventilation pipe and the second ventilation pipe in the first metalling and third metalling.Existing skill
The Quick percolation apparatus of art does not have the report of such setting.
Second, the present invention improves the material in filtering layer area.It is respectively provided in first adsorption layer and the second adsorption layer
Adsorbent material has the ability of absorption organic matter.Adsorption capacity is insufficient, then organic matter treatment effeciency is poor, and adsorption capacity is too
By force, internal aperture is too small, easily causes microorganism growth too fast, results in blockage.So granularity is suitable, internal proper pore size
Filler, can effectively adsorb ammonia nitrogen, organic matter biochemical degradation and block because surface microorganism film is blocked up.
Third, the present invention improve the function in filtering layer area.The first reservoir bed and the second reservoir bed being arranged to
In lower infiltration process, there is suction function, top filtrate is formed into negative pressuren zone, outside air can guarantee automatically into filtrate
Infiltration process forms effective " aerobic → anaerobism → aerobic → anaerobism " region, make ammonia nitrogen can in infiltration process Efficient Conversion
For NO3 -And NO2 -, without aeration.And in filtration system lower part, NO3 -And NO2 -Part denitrification, nitrogen removal rate 10%-
30%, COD removal rate reach 40%-70%.
4th, wood powder layer is arranged in the present invention in filtering layer.Wood powder filtrate is the few timber of oiliness, leaf sawdust, is being percolated
C/N ratio can be effectively increased in the process, improve rear end ABR reactor denitrification effect.
To sum up, Quick percolation apparatus of the invention, nitrogen removal rate 50%-80%, COD removal rate are 80%-95%,
Without being aerated oxygen supply and sludge reflux, power consumption is saved;Excess sludge is not generated, secondary pollution is reduced;Structure is simple, operation is simple
Just, occupied area is small, and capital expenditure is few.
Beneficial effects of the present invention:
1, Quick percolation apparatus of the invention, in the COD concentration < 1000mg/L of water inlet, the ammonia nitrogen concentration of water inlet is 300-
When 400mg/L, by Quick percolation apparatus of the invention, ammonia nitrogen removal frank reaches 70-90%, nitrogen removal rate 10%-
30%, COD removal rate reach 40%-70%, and treatment effeciency is high.
2, Quick percolation apparatus of the invention saves power consumption without being aerated oxygen supply and sludge reflux;Remaining dirt is not generated
Mud reduces secondary pollution.
3, Quick percolation apparatus of the invention, structure is simple, easy to operate, occupied area is small, and capital expenditure is few.
4, Quick percolation apparatus of the invention is particularly suitable for polluted river, rural decentralized wastewater, Small Urban life
At the denitrogenation processing and the higher livestock and poultry cultivation sewage of concentration of sewage and the still unlapped outlying district sewage of city planting ductwork
Reason.
Based on the above technical solution, the present invention can also be improved as follows.
Further, the height of the filtering layer area entirety is 165cm-200cm, wherein the height of the coarse sands layer is 30cm-
35cm, the height of the wood powder layer are 20cm-25cm, and the height of the first adsorption layer is 5cm-10cm, first water storage
The height of layer is 15cm-20cm, and the height of first metalling is 15cm-20cm, and the height of second metalling is
10cm-15cm, the height of the fine sand layer are 15cm-20cm, and the height of second adsorption layer is 5cm-10cm, described second
The height of reservoir bed is 15cm-20cm, and the height of the third metalling is 15cm-20cm, and the height of the drainage blanket is
20cm-25cm。
Further, the partial size for the coarse sand filled in the coarse sands layer is 1mm-2mm.
Further, the partial size for the wood powder filled in the wood powder layer is 0.5mm-2mm.
Be using above-mentioned further beneficial effect: the powder that wood powder generates after the processing of various timber is seeping
C/N ratio can be effectively increased during filter, improve denitrification effect.
Further, the adsorbent filled in the first adsorption layer and the second adsorption layer is coke blacking and bamboo charcoal powder by matter
Amount is than being (20-50): the mixture of (50-80), partial size are 0.1mm-1mm.
Be using above-mentioned further beneficial effect: above-mentioned mixed type filler has good porosity, has absorption
The ability of organic matter.Adsorption capacity is insufficient, then organic matter treatment effeciency is poor, and adsorption capacity is too strong, and internal aperture is too small then easy
Cause microorganism growth too fast, results in blockage.
Further, the rubble filled in first metalling and the third metalling is that partial size is 3mm-10mm
Lime stone rubble, the rubble filled in second metalling are the lime stone rubble that partial size is 20mm-40mm.
Using above-mentioned further beneficial effect is: the main component of limestone gravel is calcium carbonate, using limestone
Rubble, adsorption capacity are stronger.
Further, the partial size for the fine sand filled in the fine sand layer is 0.5mm-1mm.
Further, the first ventilation pipe and one end nozzle of the second ventilation pipe far from the snorkel are open,
Pipe diameter >=32mm and≤75mm, length are less than or equal to the 80% of pond body length.
Further, the aperture of the air vent is 10mm-12mm.
It is using above-mentioned further beneficial effect: is equipped with ventilation pipe between the first metalling and third metalling, changes
Tracheae is equipped with air vent, and pipe of taking a breath is connected with snorkel, can enter filtering layer area in order to air in this way.
Further, the open at both ends of the drainpipe 19, pipe diameter 75mm-200mm, length are less than or equal to pond body
The 90% of length.
The second object of the present invention is to provide a kind of method for carrying out sewage treatment using above-mentioned Quick percolation apparatus.This
Invention carries out sewage treatment using above-mentioned Quick percolation apparatus, and treatment effeciency is high, and method is simple, and operation is easy, and market prospects are wide
It is wealthy, it is suitble to large-scale promotion application.
The technical scheme to solve the above technical problems is that a kind of carry out sewage using above-mentioned Quick percolation apparatus
The method of processing, includes the following steps:
Untreated sewage is collected through pipe network, enters from the inlet water distributor, then enters filtering layer area by water distributing pore
In, successively by coarse sands layer, wood powder layer, first adsorption layer, the first reservoir bed, the first metalling, the second metalling, fine sand layer,
The processing of second adsorption layer, the second reservoir bed and third metalling, treated, and sewage is pooled to drainage blanket, going out through drainpipe
Mouth of a river discharge, atmosphere are had respectively entered in the first ventilation pipe and the second ventilation pipe by the upper port of snorkel.
It should be noted that using above-mentioned Quick percolation apparatus carry out sewage treatment when, can be according to water inlet, selection into
Row level-one is quickly percolated or second level is quickly percolated or three-level is quickly percolated, even more multistage quickly diafiltration.
Beneficial effects of the present invention:
The present invention carries out sewage treatment using above-mentioned Quick percolation apparatus of stating, and treatment effeciency is high, and method is simple, and operation is held
Easily, wide market is suitble to large-scale promotion application.
Detailed description of the invention
Fig. 1 is the structural schematic diagram of Quick percolation apparatus of the invention.
In attached drawing, parts list represented by the reference numerals are as follows:
1, water inlet, 2, water distributor, 3, filtering layer area, 4, snorkel, 5, coarse sands layer, 6, wood powder layer, 7, first adsorption layer, 8,
First reservoir bed, the 9, first metalling, the 10, second metalling, 11, fine sand layer, the 12, second adsorption layer, the 13, second reservoir bed,
14, third metalling, 15, drainage blanket, the 16, first ventilation pipe, the 17, second ventilation pipe, 18, air vent, 19, drainpipe.
Specific embodiment
Principles and features of the present invention are described below in conjunction with specific attached drawing, example is served only for explaining this hair
It is bright, it is not intended to limit the scope of the present invention.
Embodiment 1
As shown in Figure 1, the Quick percolation apparatus of the present embodiment, including water inlet 1, water distributor 2, filtering layer area 3 and snorkel
4;The water distributor 2 is connected with the water inlet 1, and the water distributor 2 is positioned horizontally in the top in the filtering layer area 3, the cloth
2 lower end interval of water pipe is provided with multiple water distributing pores;The filtering layer area 3 is followed successively by coarse sands layer 5 from top to bottom, wood powder layer 6, first adsorbs
Layer the 7, first reservoir bed 8, the first metalling 9, the second metalling 10, fine sand layer 11, the second adsorption layer 12, the second reservoir bed 13,
Third metalling 14 and drainage blanket 15;The first ventilation pipe 16 is transversely provided in first metalling 9, in the third rubble
The second ventilation pipe 17 is transversely provided in layer 14;Uniform intervals on the side wall of the first ventilation pipe 16 and the second ventilation pipe 17
It is provided with several air vents 18;The lower end and middle part of the snorkel 4 are separately connected the second ventilation pipe 17 positioned at the same side
With one end nozzle of the first ventilation pipe 16, the upper end of the snorkel 6 is higher than the 5 top 30cm of coarse sands layer;Described
Drainpipe 19 is transversely provided in drainage blanket 15, treated, and sewage is discharged through the water outlet of the drainpipe 19.
The principle of the present invention is:
First, the present invention improves the structure in filtering layer area.From top, filtrate follows " thick → thin → thick → thin "
Rule, and between coarse sands layer and the first metalling be equipped with the first reservoir bed, be equipped between fine sand layer and third metalling
Second reservoir bed is respectively arranged with the first ventilation pipe and the second ventilation pipe in the first metalling and third metalling.Existing skill
The Quick percolation apparatus of art does not have the report of such setting.
Second, the present invention improves the material in filtering layer area.It is respectively provided in first adsorption layer and the second adsorption layer
Adsorbent material has the ability of absorption organic matter.Adsorption capacity is insufficient, then organic matter treatment effeciency is poor, and adsorption capacity is too
By force, internal aperture is too small, easily causes microorganism growth too fast, results in blockage.So granularity is suitable, internal proper pore size
Filler, can effectively adsorb ammonia nitrogen, organic matter biochemical degradation and block because surface microorganism film is blocked up.
Third, the present invention improve the function in filtering layer area.The first reservoir bed and the second reservoir bed being arranged to
In lower infiltration process, there is suction function, top filtrate is formed into negative pressuren zone, outside air can guarantee automatically into filtrate
Infiltration process forms effective " aerobic → anaerobism → aerobic → anaerobism " region, make ammonia nitrogen can in infiltration process Efficient Conversion
For NO3 -And NO2 -, without aeration.And in filtration system lower part, NO3 -And NO2 -Part denitrification, nitrogen removal rate 10%-
30%, COD removal rate reach 40%-70%.
4th, wood powder layer is arranged in the present invention in filtering layer.Wood powder filtrate is the few timber of oiliness, leaf sawdust, is being percolated
C/N ratio can be effectively increased in the process, improve rear end ABR reactor denitrification effect.
To sum up, Quick percolation apparatus of the invention, nitrogen removal rate 50%-80%, COD removal rate are 80%-95%,
Without being aerated oxygen supply and sludge reflux, power consumption is saved;Excess sludge is not generated, secondary pollution is reduced;Structure is simple, operation is simple
Just, occupied area is small, and capital expenditure is few.
The height in the filtering layer area 3 is 190cm, wherein the height of the coarse sands layer 5 is 30cm, the height of the wood powder layer 6
Degree is 25cm, and the height of the first adsorption layer 7 is 5cm, and the height of first reservoir bed 8 is 20cm, first rubble
The height of layer 9 is 15cm, and the height of second metalling 10 is 15cm, and the height of the fine sand layer 11 is 15cm, described the
The height of two adsorption layers 12 is 10cm, and the height of second reservoir bed 13 is 15cm, and the height of the third metalling 14 is
20cm, the height of the drainage blanket 15 are 20cm.
The partial size for the coarse sand filled in the coarse sands layer 5 is 1mm-2mm.
The partial size for the wood powder filled in the wood powder layer 6 is 0.5mm-2mm.
The adsorbent filled in the first adsorption layer 7 and the second adsorption layer 12 be coke blacking and bamboo charcoal powder in mass ratio
For the mixture of 20:80), partial size is 0.1mm-1mm.
The rubble filled in first metalling 9 and the third metalling 14 is the lime that partial size is 3mm-10mm
Stone rubble, the rubble filled in second metalling 10 are the lime stone rubble that partial size is 20mm-40mm.
The partial size for the fine sand filled in the fine sand layer 11 is 0.5mm-1mm.
The first ventilation pipe 16 and the second ventilation one end nozzle of the pipe 17 far from the snorkel 4 are open, pipe
Road diameter is 32mm, and length is less than or equal to the 80% of pond body length.
The aperture of the air vent 18 is 10mm-12mm.
The open at both ends of the drainpipe 19, pipe diameter 75mm, length are less than or equal to the 90% of pond body length.
On city, the south china pig farm Xin Lian, three are carried out altogether using the method that above-mentioned Quick percolation apparatus carries out sewage treatment
Grade quickly diafiltration, includes the following steps:
Untreated sewage, influent COD 1000-1500mg/L, ammonia nitrogen 300-600mg/L, total phosphorus 15-45mg/
L is collected through pipe network, is entered water distributor 2 from the water inlet 1 of first Quick percolation apparatus, is then entered filter by water distributing pore
In floor area 3, successively pass through coarse sands layer 5, wood powder layer 6, first adsorption layer 7, the first reservoir bed 8, the first metalling 9, the second rubble
The processing of layer 10, fine sand layer 11, the second adsorption layer 12, the second reservoir bed 13 and third metalling 14, treated, and sewage collects
To drainage blanket 15, the water outlet through drainpipe 19 is discharged to the water inlet 1 of second Quick percolation apparatus, and atmosphere passes through snorkel
4 upper port has respectively entered in the first ventilation pipe 16 and the second ventilation pipe 17.In the processing side of second Quick percolation apparatus
Water outlet row of the method in first Quick percolation apparatus, treated drainpipe 19 of the sewage through second Quick percolation apparatus
The water inlet 1 for arriving third Quick percolation apparatus out, using the processing of third Quick percolation apparatus, treated, and sewage is passed through
The water outlet of the drainpipe 19 of third Quick percolation apparatus is discharged, and water outlet COD is 95mg/L, ammonia nitrogen 10mg/L, and total phosphorus is
4mg/L。
It can be seen that the method that the present embodiment carries out sewage treatment using above-mentioned Quick percolation apparatus, COD removal rate are
60%-90%, ammonia nitrogen removal frank 70%-98%, total tp removal rate are 50%-90%.
Embodiment 2
As shown in Figure 1, the Quick percolation apparatus of the present embodiment, including water inlet 1, water distributor 2, filtering layer area 3 and snorkel
4;The water distributor 2 is connected with the water inlet 1, and the water distributor 2 is positioned horizontally in the top in the filtering layer area 3, the cloth
2 lower end interval of water pipe is provided with multiple water distributing pores;The filtering layer area 3 is followed successively by coarse sands layer 5 from top to bottom, wood powder layer 6, first adsorbs
Layer the 7, first reservoir bed 8, the first metalling 9, the second metalling 10, fine sand layer 11, the second adsorption layer 12, the second reservoir bed 13,
Third metalling 14 and drainage blanket 15;The first ventilation pipe 16 is transversely provided in first metalling 9, in the third rubble
The second ventilation pipe 17 is transversely provided in layer 14;Uniform intervals on the side wall of the first ventilation pipe 16 and the second ventilation pipe 17
It is provided with several air vents 18;The lower end and middle part of the snorkel 4 are separately connected the second ventilation pipe 17 positioned at the same side
With one end nozzle of the first ventilation pipe 16, the upper end of the snorkel 4 is higher than the 5 top 40cm of coarse sands layer;Described
Drainpipe 19 is transversely provided in drainage blanket 15, treated, and sewage is discharged through the water outlet of the drainpipe 19.
Wherein, the height in the filtering layer area 3 is 194cm, wherein the height of the coarse sands layer 5 is 32cm, the wood powder layer
6 height is 22cm, and the height of the first adsorption layer 7 is 8cm, and the height of first reservoir bed 8 is 18cm, described first
The height of metalling 9 is 18cm, and the height of second metalling 10 is 12cm, and the height of the fine sand layer 11 is 18cm, institute
The height for stating the second adsorption layer 12 is 8cm, and the height of second reservoir bed 13 is 18cm, the height of the third metalling 14
For 18cm, the height of the drainage blanket 15 is 22cm.
The partial size for the coarse sand filled in the coarse sands layer 5 is 1mm-2mm.
The partial size for the wood powder filled in the wood powder layer 6 is 0.5mm-2mm.
The adsorbent filled in the first adsorption layer 7 and the second adsorption layer 12 be coke blacking and bamboo charcoal powder in mass ratio
For the mixture of 50:50, partial size is 0.1mm-1mm.
The rubble filled in first metalling 9 and the third metalling 14 is the lime that partial size is 3mm-10mm
Stone rubble, the rubble filled in second metalling 10 are the lime stone rubble that partial size is 20mm-40mm.
The partial size for the fine sand filled in the fine sand layer 11 is 0.5mm-1mm.
The first ventilation pipe 16 and the second ventilation one end nozzle of the pipe 17 far from the snorkel 4 are open, pipe
Road diameter is 50mm, and length is less than or equal to the 80% of pond body length.
The aperture of the air vent 18 is 10mm-12mm.
The open at both ends of the drainpipe 19, pipe diameter 150mm, length are less than or equal to the 90% of pond body length.
He Prefecture Long Ya primary school sanitary wastewater (being free of sanitary sewage), sewage treatment is carried out using above-mentioned Quick percolation apparatus
Method, carry out level-one be quickly percolated, include the following steps:
Untreated sewage is collected through pipe network, influent COD 80-200mg/L, ammonia nitrogen 60-350mg/L, total phosphorus 10-
25mg/L enters water distributor 2 from water inlet 1, is then entered in filtering layer area 3 by water distributing pore, successively by coarse sands layer 5, wood
Bisque 6, first adsorption layer 7, the first reservoir bed 8, the first metalling 9, the second metalling 10, fine sand layer 11, the second adsorption layer 12,
The processing of second reservoir bed 13 and third metalling 14, treated, and sewage is pooled to drainage blanket 15, the water outlet through drainpipe 19
Mouth discharge, water outlet COD are 15mg/L, ammonia nitrogen 10-60mg/L, total phosphorus 3-8mg/L, and atmosphere passes through the upper port of snorkel 4
It has respectively entered in the first ventilation pipe 16 and the second ventilation pipe 17.
It can be seen that the method that the present embodiment carries out sewage treatment using above-mentioned Quick percolation apparatus, COD removal rate are
80%-92%, ammonia nitrogen removal frank 84%-97.5%, total tp removal rate are 88%.
Embodiment 3
As shown in Figure 1, the Quick percolation apparatus of the present embodiment, including water inlet 1, water distributor 2, filtering layer area 3 and snorkel
4;The water distributor 2 is connected with the water inlet 1, and the water distributor 2 is positioned horizontally in the top in the filtering layer area 3, the cloth
2 lower end interval of water pipe is provided with multiple water distributing pores;The filtering layer area 3 is followed successively by coarse sands layer 5 from top to bottom, wood powder layer 6, first adsorbs
Layer the 7, first reservoir bed 8, the first metalling 9, the second metalling 10, fine sand layer 11, the second adsorption layer 12, the second reservoir bed 13,
Third metalling 14 and drainage blanket 15;The first ventilation pipe 16 is transversely provided in first metalling 9, in the third rubble
The second ventilation pipe 17 is transversely provided in layer 14;Uniform intervals on the side wall of the first ventilation pipe 16 and the second ventilation pipe 17
It is provided with several air vents 18;The lower end and middle part of the snorkel 4 are separately connected the second ventilation pipe 17 positioned at the same side
With one end nozzle of the first ventilation pipe 16, the upper end of the snorkel 4 is higher than the 5 top 50cm of coarse sands layer;Described
Drainpipe 19 is transversely provided in drainage blanket 15, treated, and sewage is discharged through the water outlet of the drainpipe 19.
Wherein, the height in the filtering layer area 3 is 195cm, wherein the height of the coarse sands layer 5 is 35cm, the wood powder layer
6 height is 20cm, and the height of the first adsorption layer 7 is 10cm, and the height of first reservoir bed 8 is 15cm, described the
The height of one metalling 9 is 20cm, and the height of second metalling 10 is 10cm, and the height of the fine sand layer 11 is 20cm,
The height of second adsorption layer 12 is 5cm, and the height of second reservoir bed 13 is 20cm, the height of the third metalling 14
Degree is 15cm, and the height of the drainage blanket 15 is 25cm.
The partial size for the coarse sand filled in the coarse sands layer 5 is 1mm-2mm.
The partial size for the wood powder filled in the wood powder layer 6 is 0.5mm-2mm.
The adsorbent filled in the first adsorption layer 7 and the second adsorption layer 12 be coke blacking and bamboo charcoal powder in mass ratio
For the mixture of 35:65, partial size is 0.1mm-1mm.
The rubble filled in first metalling 9 and the third metalling 14 is the lime that partial size is 3mm-10mm
Stone rubble, the rubble filled in second metalling 10 are the lime stone rubble that partial size is 20mm-40mm.
The partial size for the fine sand filled in the fine sand layer 11 is 0.5mm-1mm.
The first ventilation pipe 16 and the second ventilation one end nozzle of the pipe 17 far from the snorkel 4 are open, pipe
Road diameter is 75mm, and length is less than or equal to the 80% of pond body length.
The aperture of the air vent 18 is 12mm.
The open at both ends of the drainpipe 19, pipe diameter 200mm, length are less than or equal to the 90% of pond body length.
The method for carrying out sewage treatment using above-mentioned Quick percolation apparatus, includes the following steps:
Limited liability company's rare earth mining wastewater is developed in middle aluminium He Prefecture rare earth, utilizes above-mentioned Quick percolation apparatus
(level-one diafiltration), the method for carrying out sewage treatment includes the following steps:
Untreated sewage is collected through pipe network, influent COD 100-150mg/L, ammonia nitrogen 100-200mg/L, from water inlet
Mouth 1 enters water distributor 2, is then entered in filtering layer area 3 by water distributing pore, successively adsorbs by coarse sands layer 5, wood powder layer 6, first
Layer the 7, first reservoir bed 8, the first metalling 9, the second metalling 10, fine sand layer 11, the second adsorption layer 12,13 and of the second reservoir bed
The processing of third metalling 14, treated, and sewage is pooled to drainage blanket 15, and the water outlet discharge through drainpipe 19 is discharged COD
For 20mg/L, ammonia nitrogen 2-4mg/L, atmosphere has respectively entered the first ventilation pipe 16 and second by the upper port of snorkel 4 and changes
In tracheae 17.
It can be seen that the method that the present embodiment carries out sewage treatment using above-mentioned Quick percolation apparatus, COD removal rate are
86%, ammonia nitrogen removal frank 98%.
The foregoing is merely presently preferred embodiments of the present invention, is not intended to limit the invention, it is all in spirit of the invention and
Within principle, any modification, equivalent replacement, improvement and so on be should all be included in the protection scope of the present invention.
Claims (10)
1. a kind of Quick percolation apparatus, which is characterized in that including water inlet (1), water distributor (2), filtering layer area (3) and snorkel
(4);The water distributor (2) is connected with the water inlet (1), and the water distributor (2) is positioned horizontally in the upper of the filtering layer area (3)
Side, water distributor (2) the lower end interval is provided with multiple water distributing pores;The filtering layer area (3) be followed successively by from top to bottom coarse sands layer (5),
Wood powder layer (6), first adsorption layer (7), the first reservoir bed (8), the first metalling (9), the second metalling (10), fine sand layer
(11), the second adsorption layer (12), the second reservoir bed (13), third metalling (14) and drainage blanket (15);In first rubble
(9) are inner is transversely provided with the first ventilation pipe (16) for layer, are transversely provided with the second ventilation pipe (17) the third metalling (14) is inner;Institute
It states uniform intervals on the side wall of the first ventilation pipe (16) and the second ventilation pipe (17) and is provided with several air vents (18);It is described logical
The lower end and middle part of tracheae (4) are separately connected the second ventilation pipe (17) and the first ventilation pipe (16) positioned at the same side
One end nozzle, the upper end of the snorkel (4) is higher than 30cm-50cm at the top of the coarse sands layer (5);In the drainage blanket (15)
In be transversely provided with drainpipe (19), treated sewage is discharged through the water outlet of the drainpipe (19).
2. Quick percolation apparatus according to claim 1, which is characterized in that the height of filtering layer area (3) entirety is
165cm-200cm, wherein the height of the coarse sands layer (5) is 30cm-35cm, and the height of the wood powder layer (6) is 20cm-
25cm, the height of the first adsorption layer (7) are 5cm-10cm, and the height of first reservoir bed (8) is 15cm-20cm, institute
The height for stating the first metalling (9) is 15cm-20cm, and the height of second metalling (10) is 10cm-15cm, the fine sand
The height of layer (11) is 15cm-20cm, and the height of second adsorption layer (12) is 5cm-10cm, second reservoir bed (13)
Height be 15cm-20cm, the height of the third metalling (14) is 15cm-20cm, and the height of the drainage blanket (15) is
20cm-25cm。
3. Quick percolation apparatus according to claim 1, which is characterized in that the coarse sand filled in the coarse sands layer (5)
Partial size is 1mm-2mm;The partial size for the wood powder filled in the wood powder layer (6) is 0.5mm-2mm.
4. Quick percolation apparatus according to claim 1, which is characterized in that the first adsorption layer (7) and the second absorption
The adsorbent filled in layer (12) is coke blacking and bamboo charcoal powder is (20-50) in mass ratio: the mixture of (50-80), partial size
It is 0.1mm-1mm.
5. Quick percolation apparatus according to claim 1, which is characterized in that first metalling (9) and the third
The rubble filled in metalling (14) is the lime stone rubble that partial size is 3mm-10mm, filling in second metalling (10)
Rubble be lime stone rubble that partial size is 20mm-40mm.
6. Quick percolation apparatus according to claim 1, which is characterized in that the fine sand filled in the fine sand layer (11)
Partial size is 0.5mm-1mm.
7. Quick percolation apparatus according to claim 1, which is characterized in that the first ventilation pipe (16) and described second
One end nozzle of the ventilation pipe (17) far from the snorkel (4) is open, and pipe diameter >=32mm and≤75mm, length is small
In equal to the 80% of pond body length.
8. Quick percolation apparatus according to claim 1, which is characterized in that the aperture of the air vent (18) is 10mm-
12mm。
9. Quick percolation apparatus according to claim 1, which is characterized in that the open at both ends of the drainpipe (19), pipe
Road diameter is 75mm-200mm, and length is less than or equal to the 90% of pond body length.
10. a kind of method for carrying out sewage treatment using the described in any item Quick percolation apparatus of claim 1-9, feature exist
In including the following steps:
Untreated sewage is collected through pipe network, is entered water distributor (2) from water inlet (1), is then entered filtering layer by water distributing pore
In area (3), successively pass through coarse sands layer (5), wood powder layer (6), first adsorption layer (7), the first reservoir bed (8), the first metalling
(9), the second metalling (10), fine sand layer (11), the second adsorption layer (12), the second reservoir bed (13) and third metalling (14)
Processing, treated, and sewage is pooled to drainage blanket (15), and the water outlet discharge through drainpipe (19), atmosphere passes through snorkel (4)
Upper port have respectively entered the first ventilation pipe (16) and second ventilation pipe (17) in.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201910779626.XA CN110498508B (en) | 2019-08-22 | 2019-08-22 | Rapid infiltration device and method for sewage treatment by using same |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201910779626.XA CN110498508B (en) | 2019-08-22 | 2019-08-22 | Rapid infiltration device and method for sewage treatment by using same |
Publications (2)
Publication Number | Publication Date |
---|---|
CN110498508A true CN110498508A (en) | 2019-11-26 |
CN110498508B CN110498508B (en) | 2023-11-21 |
Family
ID=68588802
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201910779626.XA Active CN110498508B (en) | 2019-08-22 | 2019-08-22 | Rapid infiltration device and method for sewage treatment by using same |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN110498508B (en) |
Citations (10)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2000232829A (en) * | 1999-02-17 | 2000-08-29 | Yamamoto Co Ltd | Filtration equipment for waste liquid or the like of hydroponic apparatus |
CN2889440Y (en) * | 2006-02-13 | 2007-04-18 | 刘哲人 | Quick percolation apparatus for mixed sewage oxidized pond |
US20090261036A1 (en) * | 2008-04-16 | 2009-10-22 | William Lucas | Bioretention system and method |
CN102674631A (en) * | 2012-05-10 | 2012-09-19 | 复旦大学 | Method and system for advanced treatment of centralized rural domestic sewage |
CN203346228U (en) * | 2013-06-28 | 2013-12-18 | 舟山市水利水务围垦局 | Domestic sewage treatment artificial wetland |
CN105859039A (en) * | 2016-05-17 | 2016-08-17 | 中国科学院广州地球化学研究所 | Unpowered high-load underground leachate treatment compound system and method |
CN206680349U (en) * | 2017-04-09 | 2017-11-28 | 林慈涛 | A kind of environmental protection type agricultural sewage-treatment plant |
CN109423937A (en) * | 2017-08-28 | 2019-03-05 | 上海景域园林建设发展有限公司 | A kind of residential quarters system for reclaiming rainwater |
CN208617622U (en) * | 2017-11-10 | 2019-03-19 | 江西挺进环保科技有限公司 | A kind of basin-wide rare-earth mining area tail water filtration process coupled system |
CN109695190A (en) * | 2018-11-27 | 2019-04-30 | 新沂市大明科技开发有限公司 | A kind of Industrial Zone sponge urban ground paving structure |
-
2019
- 2019-08-22 CN CN201910779626.XA patent/CN110498508B/en active Active
Patent Citations (10)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2000232829A (en) * | 1999-02-17 | 2000-08-29 | Yamamoto Co Ltd | Filtration equipment for waste liquid or the like of hydroponic apparatus |
CN2889440Y (en) * | 2006-02-13 | 2007-04-18 | 刘哲人 | Quick percolation apparatus for mixed sewage oxidized pond |
US20090261036A1 (en) * | 2008-04-16 | 2009-10-22 | William Lucas | Bioretention system and method |
CN102674631A (en) * | 2012-05-10 | 2012-09-19 | 复旦大学 | Method and system for advanced treatment of centralized rural domestic sewage |
CN203346228U (en) * | 2013-06-28 | 2013-12-18 | 舟山市水利水务围垦局 | Domestic sewage treatment artificial wetland |
CN105859039A (en) * | 2016-05-17 | 2016-08-17 | 中国科学院广州地球化学研究所 | Unpowered high-load underground leachate treatment compound system and method |
CN206680349U (en) * | 2017-04-09 | 2017-11-28 | 林慈涛 | A kind of environmental protection type agricultural sewage-treatment plant |
CN109423937A (en) * | 2017-08-28 | 2019-03-05 | 上海景域园林建设发展有限公司 | A kind of residential quarters system for reclaiming rainwater |
CN208617622U (en) * | 2017-11-10 | 2019-03-19 | 江西挺进环保科技有限公司 | A kind of basin-wide rare-earth mining area tail water filtration process coupled system |
CN109695190A (en) * | 2018-11-27 | 2019-04-30 | 新沂市大明科技开发有限公司 | A kind of Industrial Zone sponge urban ground paving structure |
Also Published As
Publication number | Publication date |
---|---|
CN110498508B (en) | 2023-11-21 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN109250821B (en) | Hierarchical biofiltration retention system | |
US11878920B2 (en) | Stormwater runoff treatment substrate and stormwater bioretention system constructed by using substrate | |
CN104817239B (en) | A kind of heavily contaminated water course in situ water purification system and purification method | |
CN102503036B (en) | High-efficiency denitrification artificial soil subsurface infiltration sewage treatment composite system and method | |
CN208292826U (en) | More PROCESS COUPLING multistage artificial wet land systems | |
CN109607952A (en) | A kind of reinforced phosphor-removing composite artificial wet land treating system | |
CN105174468B (en) | A kind of cellular-type composite stereo artificial wet land system and sewage water treatment method | |
CN104828946A (en) | Biocatalysis packing subsurface infiltration system for enhancing denitrification | |
CN109534623A (en) | The system for improving drowned flow artificial wet land wastewater treatment efficiency is added based on charcoal | |
CN210656590U (en) | Buried rural domestic sewage treatment system | |
WO2020133930A1 (en) | High-efficiency biodegradation filter reactor and method using same for treating polluted water | |
CN110104900A (en) | A kind of environmentally friendly high efficiency composition thermal power plant domestic sewage processing system and method | |
CN205740688U (en) | A kind of artificial wet land treating system of residents in rural community percolate | |
CN111484132A (en) | Composite artificial wetland system for advanced treatment of tail water and sewage treatment method | |
CN204625450U (en) | A kind of Novel heavy polluted river channel original position water purification system | |
CN1257854C (en) | Waste water cryogenic treating apparatus for deaminizating phosphor-removing ventilating layer | |
CN110746055A (en) | River course normal position water purification and advanced wastewater treatment system | |
CN105753271A (en) | Biological filter-biological contact oxidation-steel slag absorption sewage treatment system and method for sewage treatment by utilizing system | |
CN201648121U (en) | Horizontal submerged flow artificial wet land | |
CN110498508A (en) | A kind of Quick percolation apparatus and the method using its progress sewage treatment | |
CN202390283U (en) | Saturated flow filter bed for processing contaminated water | |
CN111777263B (en) | Resourceful treatment method for aquaculture wastewater | |
CN210103705U (en) | Environment-friendly efficient composite domestic sewage treatment system for thermal power plant | |
CN110498509B (en) | High ammonia nitrogen sewage treatment device and sewage treatment method using same | |
CN210945009U (en) | Rapid infiltration 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 | ||
GR01 | Patent grant | ||
GR01 | Patent grant |