CN108083435A - A kind of buried phosphate fertilizer reclamation set and sewage water treatment method on the spot - Google Patents

A kind of buried phosphate fertilizer reclamation set and sewage water treatment method on the spot Download PDF

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Publication number
CN108083435A
CN108083435A CN201711271906.7A CN201711271906A CN108083435A CN 108083435 A CN108083435 A CN 108083435A CN 201711271906 A CN201711271906 A CN 201711271906A CN 108083435 A CN108083435 A CN 108083435A
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China
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sludge
treatment
sewage
treatment area
partition
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CN201711271906.7A
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Chinese (zh)
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CN108083435B (en
Inventor
赵茜
张茹
刘磊
王洪波
王金鹤
马永山
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Shandong Jianzhu University
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Shandong Jianzhu University
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/30Aerobic and anaerobic processes
    • C02F3/301Aerobic and anaerobic treatment in the same reactor
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/02Biological treatment
    • C02F11/04Anaerobic treatment; Production of methane by such processes
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/30Aerobic and anaerobic processes
    • C02F3/308Biological phosphorus removal
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05FORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
    • C05F5/00Fertilisers from distillery wastes, molasses, vinasses, sugar plant or similar wastes or residues, e.g. from waste originating from industrial processing of raw material of agricultural origin or derived products thereof
    • C05F5/002Solid waste from mechanical processing of material, e.g. seed coats, olive pits, almond shells, fruit residue, rice hulls
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A40/00Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
    • Y02A40/10Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
    • Y02A40/20Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses

Abstract

The present invention discloses a kind of buried phosphate fertilizer reclamation set and sewage water treatment method on the spot, the reclamation set on the spot uses integrated construction, Anaerobic Treatment area, three-phase separating device, Aerobic Process for Treatment area, sloping plate deposition district and the decomposed treatment region of sludge are organically combined together, and the integrated apparatus is embedded in subsurface, has the advantages such as reinforced phosphor-removing, environmentally protective and recycling phosphorus;The sewage water treatment method of the present invention can realize the removal of total nitrogen and organic matter, anaerobic and aerobic are cascaded to realize anaerobic phosphate release and the aerobic purpose for absorbing phosphorus, under the degradation treatment effect of activated sludge, realize effectively removing for total nitrogen and organic matter, Composting treatment is carried out to excess sludge simultaneously, can realize recyclable, the innoxious and recycling of the phosphorus pollution of new rural village sanitary sewage.

Description

A kind of buried phosphate fertilizer reclamation set and sewage water treatment method on the spot
Technical field
The present invention relates to sewage treatment fields, and in particular to a kind of buried phosphate fertilizer reclamation set and sewage disposal side on the spot Method.
Background technology
In daily life, the sanitary sewages such as cheap Powdered Detergent Containing Phosphate pass through due to a lack of perfect sewage disposal system The approach such as diafiltration or directly unordered discharge enter river, lake etc., and the discharge of a large amount of phosphorus causes water pollution and eutrophication The problems such as.Therefore, phosphorous domestic sewage treatment becomes a research hotspot urgently to be resolved hurrily.
It is mainly focused on the removal of phosphor in sewage both at home and abroad at present, and the recycling of phosphorus is not affected by abundant attention always. For the removal of phosphorus, bioprocess technology, ecological process and biological-ecological group technology are mainly used in engineering at present, specifically Method includes A/O, biofilter, septic tank, stabilization pond, artificial swamp and soil filtration technology etc..From the point of view of operational effect, Each technique all there are it is more or less the problem of.For example, stabilization pond treatment technology is to utilize microbial degradation, sedimentation, conversion, retention The effects that remove pollutant, however total phosphorus content is high in water outlet, water outlet situation not up to standard occurs, and with take up a large area, It gives an offensive smell and the shortcomings for the treatment of effect is unstable.Although the production that Treatment Technology of Constructed Wetland can give full play to resource is dived Power, but its dephosphorization efficiency is relatively low.Using more ripe anaerobic-aerobic biological treatment technique-reinforced phosphor-removing technique fortune In row, although phosphorus ligands efficiency is higher, industrial wastewater is unavoidably mixed into city domestic sewage, causes heavy metal and other Poisonous and harmful substance is coexisted in phosphorus in excess sludge, it is difficult to recycle, solid is used as after final concentrated, digestion, dehydration Waste is landfilled processing.In this way, phosphorus is not only wasted as a kind of scarce resource, if also to Groundwater after permeating the ground Matter causes profound influence, and being discharged into rivers and lakes after the molten leaching of rainwater is also easy to cause body eutrophication.In fact, new rural village society There are dramatically different, which is not polluted by industrial enterprise for area's sanitary sewage and city domestic sewage, without heavy metal and other Poisonous and harmful substance, organic constituents only contain COD(COD), nitrogen, phosphorus etc..Therefore, the phosphorus in domestic sewage in rural areas Recycle the interference from undesirable element.In this way, sanitary sewage excess sludge after biological treatment passes through and stalk, green manure, weeds Vegetable matters is waited to become composting fertilizer after stack retting.Compared with municipal sewage phosphorus recycles, new rural planning is nearer from farmland, raw The phosphorus recycling of sewage living not only has more advantage in feasibility, but also can realize and apply on the spot or closely have and save fortune The advantages such as take, be easy to operate.
The content of the invention
The technical problem to be solved in the present invention is to provide a kind of buried phosphate fertilizer reclamation set and sewage water treatment method on the spot, It can solve the problems, such as that total tp removal rate is low low with recovery utilization rate in existing new rural village phosphorus-containing wastewater treatment technology, realize phosphorous The recycling of sewage.
In order to solve the technical problem, the technical solution adopted by the present invention is:Reuse fills a kind of buried phosphate fertilizer on the spot Put, including treatment tank, subsection setup inside the treatment tank and be sequentially communicated Anaerobic Treatment area, Aerobic Process for Treatment area, Sloping plate deposition district and sludge decomposed treatment region are equipped between Anaerobic Treatment area and aerobic treatment region and realize that gas-liquid-solid three-phase is separated Three-phase separating device;Anaerobic Treatment area top is equipped with sewage water inlet pipe, and bottom is equipped with multiple blenders;The Aerobic Process for Treatment Pencil filler, aerator and blender are equipped in area, aerator and blender are located at the bottom in Aerobic Process for Treatment area, and pencil is filled out Material position is in the top of aerator and blender;Precipitation baffle, sludge hopper, outlet pipe, phosphorous is equipped in the sloping plate deposition district Mud return line and phosphorus containing sludge recovery tube, multiple precipitation baffles are located above sludge hopper, outlet pipe one end and sloping plate deposition district The discharging device of top is connected, and the other end is extended to outside treatment tank;Phosphorus containing sludge return duct one end and sludge hopper bottom phase Even, the other end extends to Aerobic Process for Treatment area;Phosphorus containing sludge recovery tube one end is connected with sludge hopper bottom, and the other end extends to sludge Decomposed treatment region;The peephole that feeds intake is equipped at the top of the decomposed treatment region of sludge.
Buried phosphate fertilizer of the present invention reclamation set on the spot, Anaerobic Treatment area and aerobic treatment region by first partition every It opens, Aerobic Process for Treatment area and sloping plate deposition district are separated by second partition, and sloping plate deposition district and the decomposed treatment region of sewage pass through the 3rd Partition plate separates;Three-phase separating device is located in first partition, and second partition, which is equipped with, to be made Aerobic Process for Treatment area sewage flow to inclined plate to sink First effluent weir in shallow lake area, the 3rd partition plate are equipped with the second effluent weir made outside sloping plate deposition district flow direction median treatment tank.
Buried phosphate fertilizer of the present invention reclamation set on the spot, the three-phase separating device include the first lower partition, the One baffle and second baffle, the first lower partition are arranged in first partition, and the top and bottom of the first lower partition and the The hole of certain length is left between one partition plate, first baffle is obliquely installed in the lower end of first partition, and second baffle tilts The junction of first partition and treatment tank lower wall is arranged at, air cleft is set out between the first lower partition and first baffle, Between first baffle and second baffle water outlet is set to stitch, between the first lower partition and second baffle sludge reflux is set to stitch.
Buried phosphate fertilizer of the present invention reclamation set on the spot, between the first lower partition and first baffle and second baffle Angle be n, the value range of n is 30 ° ~ 40 °.
Buried phosphate fertilizer of the present invention reclamation set on the spot, the aerator include air compressor machine, aeration tube and multiple Aeration head, aeration tube one end are connected with air compressor machine, and the other end extends to Aerobic Process for Treatment area bottom, and multiple aeration heads are arranged at aerobic On the aeration tube for the treatment of region bottom, and aeration head is located at the lower section of blender.
Buried phosphate fertilizer of the present invention reclamation set on the spot, the angle precipitated between baffle and ground is β, wherein β's Value range is 45 ° ~ 60 °.
The volume fraction of buried phosphate fertilizer of the present invention reclamation set on the spot, Anaerobic Treatment area and aerobic treatment region is 1: 2。
Buried phosphate fertilizer of the present invention reclamation set on the spot, the described Anaerobic Treatment area, three-phase separating device, good of including Oxygen treatment region, sloping plate deposition district and the decomposed treatment region of sludge are embedded in subsurface.
The invention also discloses a kind of sewage water treatment method, based on above-mentioned buried phosphate fertilizer, reuse fills this method on the spot It puts, comprises the following steps:S01), Anaerobic Treatment:By COD be 50 ~ 400mg/L, biochemical oxygen demand (BOD) is 25 ~ 100mg/ L, top sewage of the waste water that total nitrogen concentration is 5 ~ 10mg/L and pH value is 7.2 ~ 7.5 with 0.5 ~ 0.8m/h from Anaerobic Treatment area Water inlet pipe introduces Anaerobic Treatment area, and anaerobic reaction is carried out in Anaerobic Treatment area, mixing is constantly stirred by blender, profit Phosphorus is fully discharged with anaerobic bacteria, while the organic matter absorbed in sewage of degrading, be translated into the substances such as PHAs, during Anaerobic Treatment Between for 8 ~ 12h, the sewage after Anaerobic Treatment enters three-phase separating device, and point of gas, liquid, solid is carried out in three-phase separating device From;
S02), Aerobic Process for Treatment:Sewage after separation is entered by the water outlet seam of three-phase separating device in Aerobic Process for Treatment area, good Oxygen treatment region carries out absorption degradation using the biomembrane that pencil filler is formed to pollutant, that is, controls the hydraulic detention time to be 4 ~ 6h, mixed genetic-neural network are 400 ~ 500 mg/L, dissolved oxygen is that 3.0 ~ 6.0mg/L carries out Aerobic biological process, will Phosphorus in sewage and the organic matter removal of remaining difficult degradation, by treated in Aerobic Process for Treatment area, sewage passes through the first effluent weir Into sloping plate deposition district;
S03), sloping plate deposition processing:Through treated in Aerobic Process for Treatment area, waste water enters sloping plate deposition district by the first effluent weir, Separation of solid and liquid is completed with shallow pond sedimentation theory in sloping plate deposition district, that is, controls dissolved oxygen as 0.5 ~ 1.5mg/L, total phosphorus 0.5 ~ 1.0mg/L, sedimentation time are 3 ~ 5h, and solid matter sinks to sludge hopper under the effect of gravity, and supernatant is then gradually increasing, through the After two effluent weirs are collected, Treated sewage reusing is discharged from outlet pipe, the partial sludge of sludge hopper is back to by phosphorus containing sludge return duct Aerobic Process for Treatment area, excess sludge then enter the decomposed treatment region of sludge by phosphorus containing sludge recovery tube;
S04), the decomposed processing of sludge:After excess sludge enters the decomposed treatment region of sludge by phosphorus containing sludge recovery tube, and through feeding intake The substances such as stalk and wheat husk that peephole adds carry out Composting treatment, realize the recycling of excess sludge, recovery section Phosphate fertilizer.
Beneficial effects of the present invention:The device of the invention uses integrated construction, and Anaerobic Treatment area, three phase separation are filled Put, Aerobic Process for Treatment area, sloping plate deposition district and the decomposed treatment region of sludge are organically combined together, and the integrated apparatus is embedded in ground Under face, there are the advantages such as reinforced phosphor-removing, environmentally protective and recycling phosphorus;The present invention sewage water treatment method can realize total nitrogen and Anaerobic and aerobic are cascaded to realize anaerobic phosphate release and the aerobic purpose for absorbing phosphorus, in activity by the removal of organic matter Under the degradation treatment effect of sludge, effectively removing for total nitrogen and organic matter is realized, while Composting treatment is carried out to excess sludge, It can realize recyclable, the innoxious and recycling of the phosphorus pollution of new rural village sanitary sewage;Through apparatus of the present invention, treated goes out Water can carry out Treated sewage reusing, flush the toilet for family, greening irrigation etc.;4th, sewage water treatment method of the invention utilizes sloping plate deposition Effect while the desilting area of sedimentation basin is increased, shortens the particle settling height sedimentation time, improves sewage disposal effect Rate.
Description of the drawings
Fig. 1 is the structure diagram of buried phosphate fertilizer reclamation set on the spot;
Fig. 2 is the enlarged drawing of three-phase separating device;
In figure:1st, compression pump;2nd, sewage water inlet pipe;3-1, pond left wall;3-2, pond lower wall;3-3, pond right wall;3-4, pond upper wall;4、 Anaerobic Treatment area;5th, blender;6th, air cleft is gone out;7th, water outlet is stitched;8th, sludge reflux stitches;9th, the first lower partition;10th, three phase separation Device;11-1, first baffle;11-2, second baffle;12nd, blender;13rd, aeration head;14th, Aerobic Process for Treatment area;15th, pencil is filled out Material;16th, aeration tube;17th, phosphorus containing sludge return duct;18th, sludge reflux pump;19th, sludge hopper;20th, phosphorus containing sludge recovery tube;21、 The decomposed treatment region of sludge;22nd, the 3rd partition plate;23rd, feed intake peephole;24th, outlet pipe;25th, water outlet pump;26th, the second effluent weir; 27th, sloping plate deposition district;28th, sludge settling baffle;29th, the first effluent weir;30th, air compressor machine;31st, second partition;32nd, first every Plate.
Specific embodiment
The present invention is further illustrated in the following with reference to the drawings and specific embodiments.
Embodiment 1
As shown in Figure 1, a kind of buried phosphate fertilizer reclamation set on the spot, including Anaerobic Treatment area 4, three-phase separating device 10, aerobic Treatment region 14, sloping plate deposition district 27 and the decomposed treatment region 21 of sludge;It is set between the Anaerobic Treatment area 4 and Aerobic Process for Treatment area 14 First partition 32 is put, second partition 31, sloping plate deposition district 27 and sludge are set between Aerobic Process for Treatment area 14 and sloping plate deposition district 27 3rd partition plate 22 is set between decomposed treatment region 21.Pond left wall 3-1, pond lower wall 3-2, pond right wall 3-3 ponds upper wall 3-4 form sewage Processing pond, Anaerobic Treatment area, Aerobic Process for Treatment area, sloping plate deposition district and the decomposed treatment region subsection setup of sludge are in treatment tank It portion and is sequentially communicated.
The Anaerobic Treatment area 4 by compression pump 1, sewage water inlet pipe 2, pond left wall 3-1, pond lower wall 3-2, pond upper wall 3-4, First partition 32, several blenders 5 form;The pond body in the Anaerobic Treatment area is by pond left wall 3-1, pond lower wall 3-2, pond Upper wall 3-4, the first lower partition 9 and first partition 32 surround, and the sewage water inlet pipe 2 is arranged on the upper of Anaerobic Treatment area 4 Portion, the compression pump 1 is arranged on the corresponding ground of pond left wall 3-1, and is connected with sewage water inlet pipe 2, described several Blender 5 is laid in the bottom in Anaerobic Treatment area 4.
As shown in Figure 1, 2, the three-phase separating device 10 is arranged at the bottom of first partition 32, and as Anaerobic Treatment The water outlet in area 4.The three-phase separating device includes the first lower partition 9, first baffle 11-1 and second baffle 11-2, and first Lower partition 9 is arranged in first partition 32, and is left between the top and bottom of the first lower partition 9 and first partition 32 The hole of certain length, first baffle 11-1 are obliquely installed in the lower end of first partition 32, second baffle 11-2 be obliquely installed in The junction of first partition 32 and treatment tank lower wall 3-2, outlet is set between the first lower partition 9 and first baffle 11-1 Seam 6 sets water outlet to stitch 7, between the first lower partition 9 and second baffle 11-2 between first baffle 11-1 and second baffle 11-2 Sludge reflux is set to stitch 9.In the present embodiment, the folder between the first lower partition 9 and first baffle 11-1 and second baffle 11-2 Angle is n, and the value range of n is 30 ° ~ 40 °.
The Aerobic Process for Treatment area 14 by first partition 32, second partition 31, pond lower wall 3-2, pond upper wall 3-4, several Blender 12, several aeration heads 13, aeration tube 16, air compressor machine 30,15 and first effluent weir 29 of pencil filler form;Described The pond body in Aerobic Process for Treatment area 4 is enclosed by the first lower partition 9, first partition 32, second partition 31, pond lower wall 3-2 and pond upper wall 3-4 Into the both sides of first lower partition 9, first partition 32 and second partition 31 are separately fixed on pond lower wall 3-2 and pond On wall 3-4, several described blenders 12 are laid in the bottom in Aerobic Process for Treatment area 14, and the aeration tube 16 is arranged on The bottom of oxygen treatment region 14, and pass through pipeline and connected with the air compressor machine 30 on ground, several described aeration heads 13 are laid On aeration tube 16, first effluent weir 29 is fixedly connected with second partition 31, pond lower wall 3-2 and pond upper wall 3-4, and is made For the water outlet of aerobic treatment region 14.
The sloping plate deposition district 27 is gone out by second partition 30, pond lower wall 3-2, the 3rd partition plate 22, pond upper wall 3-4, second Mill weir 26, several sludge settling baffles 28, sludge reflux pump 18, phosphorus containing sludge return duct 17, sludge hopper 19, phosphorus containing sludge return Closed tube 20, water outlet pump 25 and outlet pipe 24 form, the pond body of the sloping plate deposition district 27 by second partition 31, pond lower wall 3-2, 3rd partition plate 22 and pond upper wall 3-4 are surrounded.Second effluent weir 26 be fixedly connected on the 3rd partition plate 22, pond lower wall 3-2 and Pond upper wall 3-4, and positioned at 27 top of sloping plate deposition district, the angle between several described sludge settling baffles 28 and ground is β, wherein β are 45 ° ~ 60 °, and the sludge reflux pump 18 is connected with phosphorus containing sludge return duct 17, the sloping plate deposition district The excess sludge generated in 27 enters the decomposed treatment region 21 of sludge by phosphorus containing sludge recovery tube 20, and the water outlet pump 25 passes through Pipeline is connected with the second effluent weir 26 and outlet pipe 24.
Multiple precipitation baffles 28 are located at 19 top of sludge hopper, 24 one end of outlet pipe and the second water outlet above sloping plate deposition district Weir 26 is connected, and the other end is extended to outside treatment tank;17 one end of sewage backflow pipe is connected with 19 bottom of sludge hopper, and the other end prolongs Extend Aerobic Process for Treatment area 14;20 one end of sewage recovery tube is connected with 19 bottom of sludge hopper, and the other end extends to the decomposed processing of sludge Area 21.
The decomposed treatment region 21 of the sludge is by the 3rd partition plate 22, pond lower wall 3-2, pond right wall 3-3, pond upper wall 3-4 and throwing Material peephole 23 forms, the pond body of the decomposed treatment region 21 of the sludge by the 3rd partition plate 22, pond lower wall 3-2, pond right wall 3-3 and Pond upper wall 3-4 is surrounded, and the peephole 23 that feeds intake is arranged on the upper wall 3-4 of pond, and is corresponded to positioned at the decomposed treatment region 21 of sludge Pond upper wall 3-4 center.
A kind of buried phosphate fertilizer suitable for the phosphorous sanitary sewage of new rural village described in present embodiment reclamation set on the spot Using integrated construction, by Anaerobic Treatment area 4, three-phase separating device 10, Aerobic Process for Treatment area 14, sloping plate deposition district 27 and sludge Decomposed treatment region 21 is organically combined together, and the integrated apparatus is embedded in subsurface, have reinforced phosphor-removing, it is environmentally protective and Recycle the advantages such as phosphorus.
The operation principle of present embodiment:Phosphorus-containing wastewater is by being suitable for the buried phosphate fertilizer of the phosphorous sanitary sewage of new rural village just The top sewage water inlet pipe 2 in the Anaerobic Treatment area 4 of ground reclamation set enters, in anaerobic reaction area 4 by blender 5 constantly into Row is stirred, and the anaerobic bacteria in Anaerobic Treatment area 4 fully discharges phosphorus, while the organic matter absorbed in sewage of degrading, and is converted For substances such as PHAs.Sewage after Anaerobic Treatment enters three-phase separating device 10, in three-phase separating device 10 into promoting the circulation of qi, Liquid, solid separation.Sewage after separation is by the water outlet seam 7 of three-phase separating device 10 into suitable for the phosphorous life of new rural village The Aerobic Process for Treatment area 14 of the buried phosphate fertilizer of sewage reclamation set on the spot, is formed in Aerobic Process for Treatment area 14 by pencil filler 15 The absorption degradation of biomembrane, by the phosphorus in sewage and the organic matter removal of remaining difficult degradation.By Aerobic Process for Treatment area 14 Treated, and sewage enters the buried phosphate fertilizer reuse on the spot for being suitable for the phosphorous sanitary sewage of new rural village by the first effluent weir 29 The sloping plate deposition district 27 of device completes separation of solid and liquid in sloping plate deposition district 27 with shallow pond sedimentation theory, and solid matter is in weight Power effect is lowered into sludge hopper 19, and supernatant is then gradually increasing, and after the collection of the second effluent weir 26, is discharged from outlet pipe 24, can Be used for family flush the toilet, greening irrigation etc., realize Treated sewage reusing.The excess sludge that sloping plate deposition district 27 generates is returned through phosphorus containing sludge Closed tube 20 into the buried phosphate fertilizer reclamation set on the spot suitable for the phosphorous sanitary sewage of new rural village the decomposed treatment region 21 of sludge, Compost reaction occurs with adding the substances such as stalk and wheat husk through the peephole 23 that feeds intake, realizes the recycling of excess sludge, returns Receiving portions phosphate fertilizer.
Embodiment 2
Present embodiment discloses a kind of sewage water treatment method, and using buried phosphate fertilizer described in embodiment 1, reuse fills this method on the spot Realization is put, is comprised the following steps:
First, Anaerobic Treatment:By COD(COD)For 50 ~ 400mg/L, BOD5(Biochemical oxygen demand (BOD))For 25 ~ 100mg/L, always Top sewage water inlet pipe 2 of the waste water that nitrogen is 5 ~ 10mg/L and pH value is 7.2 ~ 7.5 with 0.5 ~ 0.8m/h from Anaerobic Treatment area 4 Into carrying out anaerobic reaction in anaerobic reaction area 4, be constantly stirred mixing by blender 5, fully released using anaerobic bacteria Phosphorus is put, while the organic matter absorbed in sewage of degrading, the substances such as PHAs are translated into, the Anaerobic Treatment time is 8 ~ 12h, through detesting Treated that sewage enters three-phase separating device 10 for oxygen, and the separation of gas, liquid, solid is carried out in three-phase separating device 10;
2nd, Aerobic Process for Treatment:Sewage after separation is entered by the water outlet seam 7 of three-phase separating device 10 in Aerobic Process for Treatment area 14, Absorption degradation is carried out to pollutant using the biomembrane that pencil filler 15 is formed in Aerobic Process for Treatment area 14, that is, waterpower is controlled to stop It is 4 ~ 6h, MLSS to stay the time(Mixed genetic-neural network)For 400 ~ 500 mg/L, DO(Dissolved oxygen)For 3.0 ~ 6.0mg/L Aerobic biological process is carried out, the phosphorus in sewage and the organic matter removal of remaining difficult degradation are handled by Aerobic Process for Treatment area 14 Sewage afterwards enters sloping plate deposition district 27 by the first effluent weir 29;
3rd, sloping plate deposition is handled:Through treated in Aerobic Process for Treatment area 14, waste water enters sloping plate deposition district by the first effluent weir 29 27, separation of solid and liquid is completed with shallow pond sedimentation theory in sloping plate deposition district 27, that is, controls DO(Dissolved oxygen)For 0.5 ~ 1.5mg/ L, total phosphorus are 0.5 ~ 1.0mg/L, and the sedimentation time is 3 ~ 5h, and solid matter sinks to sludge hopper 19 under the effect of gravity, and supernatant is then It is gradually increasing, after the collection of the second effluent weir 26, is discharged from outlet pipe 24 with Treated sewage reusing, the partial sludge of sludge hopper 19 passes through Phosphorus containing sludge return duct 17 is back to Aerobic Process for Treatment area 14, and excess sludge is then decomposed into sludge by phosphorus containing sludge recovery tube 20 Treatment region 21;
4th, the decomposed processing of sludge:Excess sludge by phosphorus containing sludge recovery tube 20 into after the decomposed treatment region 21 of sludge, and through throwing Material peephole 23 adds the substances such as stalk and wheat husk and carries out Composting treatment, realizes the recycling of excess sludge, recoverer Divide phosphate fertilizer.
Sewage water treatment method described in present embodiment can realize the removal of total nitrogen and organic matter, and anaerobic and aerobic are connected Together to realize anaerobic phosphate release and the aerobic purpose for absorbing phosphorus, under the degradation treatment effect of activated sludge, total nitrogen is realized With effectively removing for organic matter, while Composting treatment is carried out to excess sludge, can realize that the phosphorus of new rural village sanitary sewage is dirty Recyclable, the innoxious and recycling of dye.
Sewage water treatment method described in present embodiment is acted on using sloping plate deposition, is increasing the desilting area of sedimentation basin Meanwhile the particle settling height sedimentation time is shortened, improve sewage treating efficiency.
Embodiment 3
The present embodiment is as different from Example 2:The Anaerobic Treatment time described in step 1 is 8h ~ 10h.Other and specific reality It is identical to apply mode two.
Embodiment 4
The present embodiment is as different from Example 2:The hydraulic detention time that controls described in step 2 is 4 ~ 8h, MLSS(Mixing Liquid suspended sediment concentration)For 450 ~ 550mg/L, DO(Dissolved oxygen)Aerobic biological process is carried out for 4.0 ~ 6.0mg/L.It is other with Embodiment 2 is identical.
Embodiment 5
The present embodiment is as different from Example 2:Described in step 3 DO is controlled in sloping plate deposition district(Dissolved oxygen)For 0.5 ~ 1.0mg/L, total phosphorus are 0.5 ~ 0.8 mg/L, and the sedimentation time is 4h ~ 8h.It is other same as Example 2.
Using the effect of following verification experimental verifications present invention:
Experiment one:At the buried phosphate fertilizer for the phosphorous sanitary sewage of the new rural village of the invention on the spot sewage of reclamation set Reason method carries out according to the following steps:
First, Anaerobic Treatment:By COD(COD)Average is 398.73mg/L, BOD5(Biochemical oxygen demand (BOD))For 89.48mg/ L, the waste water that total nitrogen is 9.76mg/L and pH value is 7.2 ~ 7.5 with 0.8m/h from the top sewage water inlet pipe 2 in Anaerobic Treatment area 4 into Enter, anaerobic reaction is carried out in anaerobic reaction area 4, mixing is constantly stirred by blender 5, is fully discharged using anaerobic bacteria Phosphorus, while the organic matter absorbed in sewage of degrading, are translated into the substances such as PHAs, the Anaerobic Treatment time is 9h, at anaerobism Sewage after reason enters three-phase separating device 10, and the separation of gas, liquid, solid is carried out in three-phase separating device 10;
2nd, Aerobic Process for Treatment:Sewage after separation is entered by the water outlet seam 7 of three-phase separating device 10 in Aerobic Process for Treatment area 14, Absorption degradation is carried out to pollutant using the biomembrane that pencil filler 15 is formed in Aerobic Process for Treatment area 14, that is, waterpower is controlled to stop It is 4h, MLSS to stay the time(Mixed genetic-neural network)For 533.78 mg/L, DO(Dissolved oxygen)It is carried out for 5.57mg/L aerobic Biological treatment, by the phosphorus in sewage and the organic matter removal of remaining difficult degradation, by treated in Aerobic Process for Treatment area 14 sewage Sloping plate deposition district 27 is entered by the first effluent weir 29;
3rd, sloping plate deposition is handled:Through treated in Aerobic Process for Treatment area 14, waste water enters sloping plate deposition district by the first effluent weir 29 27, separation of solid and liquid is completed with shallow pond sedimentation theory in sloping plate deposition district 27, that is, controls DO(Dissolved oxygen)For 1.15mg/L, always Phosphorus is 0.53mg/L, sedimentation time 4h, and solid matter sinks to sludge hopper 19 under the effect of gravity, and supernatant is then gradually increasing, After the collection of the second effluent weir 26, discharged from outlet pipe 24 with Treated sewage reusing, the partial sludge of sludge hopper 19 passes through phosphorus containing sludge Return duct 17 is back to Aerobic Process for Treatment area 14, and excess sludge then enters the decomposed treatment region of sludge by phosphorus containing sludge recovery tube 20 21;
4th, the decomposed processing of sludge:Excess sludge by phosphorus containing sludge recovery tube 20 into after the decomposed treatment region 21 of sludge, and through throwing Material peephole 23 adds stalk and the mixture of wheat husk carries out Composting treatment, realizes the recycling of excess sludge, recycling Part phosphate fertilizer.
Using GB18918-2002《Integrated wastewater discharge standard》Detect the index of this experiment outlet pipe water outlet:COD(Chemistry Oxygen demand)For 58.25 ± 14.05mg/L, BOD5(Biochemical oxygen demand (BOD))It is 0.53mg/L for 9.43 ± 2.21mg/L and total nitrogen, Meet GB secondary standards, wherein COD(COD)Removal rate for 85.39%, the removal rate of total nitrogen is 94.57%.
Described above is only that the basic principle of the present invention and preferred embodiment, those skilled in the art do according to the present invention The improvement and replacement gone out, belongs to the scope of protection of the present invention.

Claims (9)

1. a kind of buried phosphate fertilizer reclamation set on the spot, it is characterised in that:Including treatment tank, subsection setup in sewage disposal Pond inside and the Anaerobic Treatment area, Aerobic Process for Treatment area, sloping plate deposition district and the decomposed treatment region of sludge that are sequentially communicated, Anaerobic Treatment area It is equipped between aerobic treatment region and realizes the separated three-phase separating device of gas-liquid-solid three-phase;Anaerobic Treatment area top is equipped with dirt Water water inlet pipe, bottom are equipped with multiple blenders;Pencil filler, aerator and blender are equipped in the Aerobic Process for Treatment area, is exposed Device of air and blender are located at the bottom in Aerobic Process for Treatment area, and pencil filler is located at the top of aerator and blender;It is described oblique Precipitation baffle, sludge hopper, outlet pipe, phosphorus containing sludge return duct and phosphorus containing sludge recovery tube, multiple precipitations are equipped in plate settling zone Baffle is located above sludge hopper, and outlet pipe one end is connected with the discharging device above sloping plate deposition district, and the other end extends to sewage Outside processing pond;Phosphorus containing sludge return duct one end is connected with sludge hopper bottom, and the other end extends to Aerobic Process for Treatment area;Phosphorus containing sludge returns Closed tube one end is connected with sludge hopper bottom, and the other end extends to the decomposed treatment region of sludge;It is equipped with and throws at the top of the decomposed treatment region of sludge Expect peephole.
2. buried phosphate fertilizer according to claim 1 reclamation set on the spot, it is characterised in that:Anaerobic Treatment area and aerobic place Reason area is separated by first partition, and Aerobic Process for Treatment area and sloping plate deposition district are separated by second partition, sloping plate deposition district and sewage Decomposed treatment region is separated by the 3rd partition plate;Three-phase separating device is located in first partition, and second partition, which is equipped with, makes aerobic place Reason area's sewage flows to the first effluent weir of sloping plate deposition district, and the 3rd partition plate, which is equipped with, makes sloping plate deposition district flow direction median sewage disposal The second effluent weir outside pond.
3. buried phosphate fertilizer according to claim 2 reclamation set on the spot, it is characterised in that:The three-phase separating device bag The first lower partition, first baffle and second baffle are included, the first lower partition is arranged in first partition, and the first lower partition Top and bottom and first partition between leave the hole of certain length, first baffle is obliquely installed under first partition End, second baffle are obliquely installed the junction in first partition and treatment tank lower wall, the first lower partition and first baffle Between air cleft is set out, between first baffle and second baffle set water outlet stitch, set between the first lower partition and second baffle Put sludge reflux seam.
4. buried phosphate fertilizer according to claim 3 reclamation set on the spot, it is characterised in that:First lower partition and first Angle between baffle and second baffle is n, and the value range of n is 30 ° ~ 40 °.
5. buried phosphate fertilizer according to claim 1 reclamation set on the spot, it is characterised in that:The aerator includes sky Press, aeration tube and multiple aeration heads, aeration tube one end are connected with air compressor machine, and the other end extends to Aerobic Process for Treatment area bottom, more A aeration head is arranged on the aeration tube of Aerobic Process for Treatment area bottom, and aeration head is located at the lower section of blender.
6. buried phosphate fertilizer according to claim 1 reclamation set on the spot, it is characterised in that:It precipitates between baffle and ground Angle be β, wherein the value range of β be 45 ° ~ 60 °.
7. buried phosphate fertilizer according to claim 1 reclamation set on the spot, it is characterised in that:Anaerobic Treatment area and aerobic place The volume fraction for managing area is 1:2.
8. buried phosphate fertilizer according to claim 1 reclamation set on the spot, it is characterised in that:The Anaerobic Treatment area, three Phase-separating device, Aerobic Process for Treatment area, sloping plate deposition district and the decomposed treatment region of sludge are embedded in subsurface.
9. a kind of sewage water treatment method, it is characterised in that:This method is based on buried phosphate fertilizer reuse on the spot described in claim 1 Device comprises the following steps:S01), Anaerobic Treatment:Be 50 ~ 400mg/L by COD, biochemical oxygen demand (BOD) be 25 ~ The waste water that 100mg/L, total nitrogen concentration are 5 ~ 10mg/L and pH value is 7.2 ~ 7.5 is with 0.5 ~ 0.8m/h from the upper of Anaerobic Treatment area Portion's sewage water inlet pipe introduces Anaerobic Treatment area, and anaerobic reaction is carried out in Anaerobic Treatment area, is constantly stirred by blender Mixing, fully discharges phosphorus using anaerobic bacteria, while the organic matter absorbed in sewage of degrading, and is translated into the substances such as PHAs, detests Oxygen processing time is 8 ~ 12h, and the sewage after Anaerobic Treatment enters three-phase separating device, in three-phase separating device into promoting the circulation of qi, Liquid, solid separation;
S02), Aerobic Process for Treatment:Sewage after separation is entered by the water outlet seam of three-phase separating device in Aerobic Process for Treatment area, good Oxygen treatment region carries out absorption degradation using the biomembrane that pencil filler is formed to pollutant, that is, controls the hydraulic detention time to be 4 ~ 6h, mixed genetic-neural network are 400 ~ 500 mg/L, dissolved oxygen is that 3.0 ~ 6.0mg/L carries out Aerobic biological process, will Phosphorus in sewage and the organic matter removal of remaining difficult degradation, by treated in Aerobic Process for Treatment area, sewage passes through the first effluent weir Into sloping plate deposition district;
S03), sloping plate deposition processing:Through treated in Aerobic Process for Treatment area, waste water enters sloping plate deposition district by the first effluent weir, Separation of solid and liquid is completed with shallow pond sedimentation theory in sloping plate deposition district, that is, controls dissolved oxygen as 0.5 ~ 1.5mg/L, total phosphorus 0.5 ~ 1.0mg/L, sedimentation time are 3 ~ 5h, and solid matter sinks to sludge hopper under the effect of gravity, and supernatant is then gradually increasing, through the After two effluent weirs are collected, Treated sewage reusing is discharged from outlet pipe, the partial sludge of sludge hopper is back to by phosphorus containing sludge return duct Aerobic Process for Treatment area, excess sludge then enter the decomposed treatment region of sludge by phosphorus containing sludge recovery tube;
S04), the decomposed processing of sludge:After excess sludge enters the decomposed treatment region of sludge by phosphorus containing sludge recovery tube, and through feeding intake The substances such as stalk and wheat husk that peephole adds carry out Composting treatment, realize the recycling of excess sludge, recovery section Phosphate fertilizer.
CN201711271906.7A 2017-12-06 2017-12-06 Buried phosphate fertilizer on-site recycling device and sewage treatment method Active CN108083435B (en)

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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110104827A (en) * 2019-04-30 2019-08-09 贵州开磷集团矿肥有限责任公司 A kind of phosphate fertilizer sewage treatment process
CN110801171A (en) * 2019-11-29 2020-02-18 中国农业大学 Unpowered sinking type microbial ecological toilet

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101544423A (en) * 2009-04-29 2009-09-30 重庆大学 A/O denitrification sewage treatment process and device capable of realizing sludge reduction
CN201395547Y (en) * 2009-06-05 2010-02-03 重庆大学 Sewage treatment device
CN102745866A (en) * 2012-07-19 2012-10-24 北京世纪国瑞环境工程技术有限公司 Non-hazardous recycling treatment method for excrement
CN105293701A (en) * 2015-11-06 2016-02-03 武汉芳笛环保股份有限公司 Carbon source reserve type immobilized bioreactor (IBR)
CN205856266U (en) * 2016-08-01 2017-01-04 安徽泛亚环保科技有限公司 Large-scale integrated sewage treating apparatus
CN107399817A (en) * 2017-08-08 2017-11-28 北京工业大学 Continuous stream A2The apparatus and method of O denitrification dephosphorizations+Anammox parallel connection SBR short distance nitration Treating Municipal Sewages

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101544423A (en) * 2009-04-29 2009-09-30 重庆大学 A/O denitrification sewage treatment process and device capable of realizing sludge reduction
CN201395547Y (en) * 2009-06-05 2010-02-03 重庆大学 Sewage treatment device
CN102745866A (en) * 2012-07-19 2012-10-24 北京世纪国瑞环境工程技术有限公司 Non-hazardous recycling treatment method for excrement
CN105293701A (en) * 2015-11-06 2016-02-03 武汉芳笛环保股份有限公司 Carbon source reserve type immobilized bioreactor (IBR)
CN205856266U (en) * 2016-08-01 2017-01-04 安徽泛亚环保科技有限公司 Large-scale integrated sewage treating apparatus
CN107399817A (en) * 2017-08-08 2017-11-28 北京工业大学 Continuous stream A2The apparatus and method of O denitrification dephosphorizations+Anammox parallel connection SBR short distance nitration Treating Municipal Sewages

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110104827A (en) * 2019-04-30 2019-08-09 贵州开磷集团矿肥有限责任公司 A kind of phosphate fertilizer sewage treatment process
CN110801171A (en) * 2019-11-29 2020-02-18 中国农业大学 Unpowered sinking type microbial ecological toilet

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