CN103043852B - Wastewater treatment process and device - Google Patents
Wastewater treatment process and device Download PDFInfo
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- CN103043852B CN103043852B CN201210544086.5A CN201210544086A CN103043852B CN 103043852 B CN103043852 B CN 103043852B CN 201210544086 A CN201210544086 A CN 201210544086A CN 103043852 B CN103043852 B CN 103043852B
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Abstract
The present invention provides a wastewater treatment process and a device. The process includes the following steps: preprocessing, coagulation flotation processing, biological contact oxidation processing and secondary sedimentation processing. The device includes a pretreatment device, a coagulation flotation pool, a biological contact oxidation pool and a secondary sedimentation pool, wherein the coagulation flotation pool includes a coagulation flotation separation pool body and a coagulation flotation device, and the biological contact oxidation pool is provided with a filler. The coagulation flotation process and the biological contact oxidation process are combined in the wastewater treatment process of the present invention. The characteristics of large specific surface between the micro-nano bubbles evenly diffused in water and fiber bundle-shaped filler, and good mutual contact adsorption effect are used. Therefore oxygen content in the wastewater and oxygen transfer efficiency are improved, the driving force for oxygen to transfer into biofilm and the depth penetrating into the biofilm are increased, the biofilm activity is improved, the active microbial biomass is increased, and the degradation rate of organic matters is improved.
Description
Technical field
The present invention relates to a kind of sewage treatment process and device, particularly relate to a kind of coagulation air-float and biological contact oxidation process of utilizing in conjunction with the technique and the device that carry out sewage disposal.
Background technology
Modern sewage disposal technology, divides by processing mode, can be divided into physical treatment, chemical treatment and biological treatment.Physical treatment method, is called again mechanical improvement method.Mainly for separating of the suspension material in waste water.The advantage of the method maximum is simple, Yi Hang, respond well, and very economical.Conventional physics improvement method has: gravitational separation process, centrifugal separation, filtration method and evaporative crystallization method etc.The main handling object of method of chemical treatment is the pollution substance of solvability or colloidality in waste water.It both can make pollutant separate with water, also can change some pollution substance and organism etc., therefore can reach the degree of purification higher than physical method.Particularly will reclaim useful matter from waste water time, or in waste water, contain that certain is poisonous, harmful and be difficult for being degraded by microorganisms material time, adopt chemical harnessing method the most suitable.But Chemo-Therapy logos often need adopt chemical agent or material, therefore working cost is generally all higher, and operation is also stricter etc. with the requirement of management.And, in the pre-treatment or last handling process of chemical method, conventionally also need to be used in conjunction with physics improvement method.Utilize the method for microbiological treatment waste water, be called biological treatment or biochemical treatment process.In the process of microbial life activity, a part of deliquescent organic substance is for the synthesis of protoplasma and the repertory of cell; A part becomes meta-bolites, and gives off energy, and supplies with the plasmic synthetic and vital movement of microorganism, makes the microorganism ground growth and breeding that can keep, thereby makes waste water obtain purification, and biological treatment utilizes this function exactly.According to the respiratory characteristic of microorganism, be divided into aerobic, anaerobism and facultative three major types microorganism, and aerobic treatment two class bioremediations.
Biological contact oxidation process belongs to aerobic biological process for treating, it be the microbial film being attached on carrier (filler) be main, a kind of High-efficient Water treatment process of purification of organic waste water, has the biomembrance process of activated sludge process feature, has the advantage of activated sludge process and biomembrance process concurrently.Its method is, in the body of pond, filler is set, and at the bottom of pond, aeration carries out oxygenation to sewage, and makes body interior sewage in pond in flow state, to ensure that sewage fully contacts with the filler in sewage.In general biological contact oxidation process, requisite oxygen is supplied with by blast aeration, but because the sludge loading in biological contact oxidation process is larger, causes the required aeration rate of whole biological contact oxidation pond large, and energy consumption is higher; Blast aeration bubble is larger, easily impacts microbial film, can cause biofilm detachment; And oxygen skewness in water.
Summary of the invention
Based on this, be necessary the problem for prior art, a kind of new sewage treatment process and device simple in structure, easy to use are provided.
Technical scheme of the present invention is as follows:
A kind of sewage treatment process, described technique comprises the following steps:
A: pre-treatment: will need sewage to be processed after pre-treatment, and be driven in coagulation floatation through lift pump; This step is removed large-sized floating matter, suspended substance and less solid matter;
B: coagulation air-float processing: be provided with coagulation air-float device in coagulation floatation, sewage is carried out, after coagulation air-float separating treatment, entering in biological contact oxidation pond; In dissolved air flotation process, the molecule that the density in removal sewage and water are approaching;
C: bio-contact oxidation processing: be provided with filler in described biological contact oxidation pond, different quality object is adopted to the means of taming targetedly, select suitable biological bacteria, biological bacteria is bred at filling surface raised growth, form microbial film, in this step, taking BOD, COD as main pollutent is removed, remove nitrogen phosphorus simultaneously;
D: secondary sedimentation processing: sewage overflow to the secondary sedimentation basins through bio-contact oxidation processing directly discharges after precipitation process and subsequent disposal.
Therein in an embodiment, in step C, enter in the sewage of biological contact oxidation pond and contain the micro-nano bubble that diffustivity is good, the diameter of described micro-nano bubble is 1 to 50 μ m.
In an embodiment, in step C, described filler is half soft bat wool therein; The volume of described filler account for described biological contact oxidation pond volume 70% to 85%, the biofilm amount of described filler is 220kg/m
3to 380kg/m
3.
In an embodiment, in step B, the residence time of described sewage in coagulation floatation is 30 to 60 minutes therein, and in step C, the time that described sewage stops in biological contact oxidation pond is 1 to 6 hour.
Another object of the present invention is achieved through the following technical solutions:
A kind of waste disposal plant, described waste disposal plant comprises pretreatment unit, coagulation floatation, biological contact oxidation pond and secondary sedimentation basins;
Described coagulation floatation comprises coagulation air-float separate tank pond body and coagulation air-float device, in described biological contact oxidation pond, be provided with filler, described pretreatment unit is connected by lift pump with described coagulation floatation, the water outlet of described coagulation floatation is communicated with the water-in of described biological contact oxidation pond, and the water outlet of described biological contact oxidation pond is communicated with the water-in of secondary sedimentation basins.
Therein in an embodiment, described coagulation air-float device is micro-nano bubble generator, described micro-nano bubble generator comprises pressured air-dissolving device and micro-nano bubble releasing device, described pressured air-dissolving device and micro-nano bubble releasing device are connected, described pressured air-dissolving device comprises water inlet pipe, pressurizing device, dissolved air water tank and dissolved air water delivery line, described micro-nano bubble releasing device comprises micro-nano bubble generator, on described micro-nano bubble generator, is provided with jet hole; Described pretreatment unit is connected by water inlet pipe with described dissolved air water tank, described pressurizing device is connected with described dissolved air water tank, one end of described dissolved air water delivery line is connected with described dissolved air water tank, the other end of described dissolved air water delivery line is connected with described micro-nano bubble generator, and described micro-nano bubble generator is arranged on the bottom of described coagulation floatation body.
In an embodiment, described biological contact oxidation pond comprises pond body and filler therein, and described filler is half soft bat wool, the volume of described filler account for described pond body volume 70% to 85%.
In an embodiment, the water outlet of described coagulation floatation is communicated with the water-in of the bottom that is arranged on described biological contact oxidation pond by connecting pipeline therein.
Therein in an embodiment, described air-floating apparatus arranges 2 micro-nano bubble releasing devices, one of them micro-nano bubble releasing device is arranged in described coagulation floatation, and another micro-nano bubble releasing device is arranged on the bottom of described biological contact oxidation pond.
In an embodiment, described coagulation floatation is also provided with gas floatation separation device therein, and described gas floatation separation device comprises slag scraper, and described slag scraper is arranged on the top of described coagulation floatation.
The invention has the beneficial effects as follows:
1 sewage treatment process of the present invention is processed by coagulation air-float and bio-contact oxidation processing combines, and first utilizes coagulation air-float to carry out coagulating treatment, then directly will pass into biological contact oxidation pond through coagulation air-float water after treatment, utilize the water inlet of the coagulation air-float sewage that contains micro-nano bubble after treatment as biological contact oxidation pond, owing to containing micro-nano bubble through coagulation air-float sewage after treatment, and micro-nano gas ducks in drink and can evenly spread, and the specific surface area of half soft fiber bundle-like filler is large, and Contact-sorption between micro-nano bubble and fiber bundle-like filler is effective, thereby micro-nano bubble is good to the adhesion effect of filler, can improve oxygen amount in sewage and the transfer efficiency of oxygen, increase oxygen to the impellent shifting in microbial film with to depth of penetration in microbial film, biomembrane activity is improved, active biomass increases, improve organic matter degradation rate.
2 waste disposal plants of the present invention are simple in structure, reduced the aerating apparatus of biological contact oxidation pond, can reduce thus the volume of biological contact oxidation pond, reduce construction investment;
3 waste disposal plants of the present invention can be by regulating micro-nano bubble generator to regulate micro-nano bubble amount and the concentration in the water inlet of biological contact oxidation pond, and then can make to keep higher dissolved oxygen concentration to adapt to the variation of water quality, the water yield in biological contact oxidation pond, suitability is wide.
Brief description of the drawings
Below in conjunction with concrete drawings and the specific embodiments, the present invention is further elaborated.
Fig. 1 is the overall schematic of an embodiment of sewage treatment process of the present invention;
Fig. 2 is the overall schematic of an embodiment of waste disposal plant of the present invention;
Fig. 3 is the overall schematic of an embodiment of the coagulation air-float device of waste disposal plant of the present invention;
Fig. 4 is the overall schematic of an embodiment of the biological contact oxidation pond of waste disposal plant of the present invention.
Embodiment
The invention provides a kind of new sewage treatment process and device, sewage treatment process of the present invention combines coagulation air-float and bio-contact oxidation processing, utilize micro-nano bubble that coagulation air-float the produces adhewsive action to biological contact oxidation pond, save the aerating apparatus of biological contact oxidation pond, reduced the volume of biological contact oxidation pond.Below in conjunction with specific embodiment, the present invention is described in further details.
Referring to Fig. 1, the invention provides a kind of sewage treatment process, this technique comprises the following steps:
A: pre-treatment: will need sewage collecting to be processed in water collecting basin after pre-treatment, be driven in coagulation floatation through lift pump; This step is removed large-sized floating matter, suspended substance and less solid matter;
B: coagulation air-float processing: be provided with coagulation air-float device in coagulation floatation, sewage is carried out, after coagulation air-float processing, entering in biological contact oxidation pond; In dissolved air flotation process, the approaching molecule of density and water in removal sewage, as part oil content, fiber etc.;
C: bio-contact oxidation processing: be provided with filler in described biological contact oxidation pond, different quality object is adopted to the means of taming targetedly, preferably suitable biological bacteria, add biological bacteria, biological bacteria is bred at filling surface raised growth, form microbial film, in this step, be removed taking BOD, COD as main pollutent;
D: secondary sedimentation processing: sewage overflow to the secondary sedimentation basins through bio-contact oxidation processing directly discharges after precipitation process and other subsequent disposal.Other described subsequent disposal can be to disinfect.
The present embodiment is processed by coagulation air-float and bio-contact oxidation is processed combination, and coagulation air-float is processed on the one hand can remove oil content, the fiber etc. in sewage, and after processing by coagulation air-float on the other hand, sewage contains a large amount of micro-nano bubbles.And micro-nano bubble has good adhewsive action to filler.Coagulation air-float processing in the present embodiment is the processing of micro-nano bubble coagulation air-float.So-called micro-nano bubble coagulation air-float is to make air under certain pressure, be dissolved in water and reach hypersaturated state, then makes pressure air-dissolving Shuitu so reduce to normal pressure, and the air being at this moment dissolved in the water is overflowed from water with the form of micro-nano bubble.
It is mainly the circulating contact by between microbial film, organism and oxygen three that biological contact oxidation process is purified waste water.Little through the micro-nano bubble volume in coagulation air-float sewage after treatment, quantity is many, and good dispersity easily evenly spreads with water body, and the lifetime in water is long.The sewage that contains micro-nano bubble enters after contact-oxidation pool, first, owing to having increased gas-liquid Contact area, can improve oxygen transfer efficiency, and can ensure has sufficient dissolved oxygen in water body, and reduces aeration rate.And due to the laterally evenly diffusion of micro-nano bubble, in mobile process, oxygen in sewage is evenly distributed, in micro-nano bubble, contained oxygen can fully contact with microbial film with organism simultaneously, moreover the surface of micro-nano bubble can enrichment electric charge, improve biomembranous activity, improved biomembranous vigor and oxidation capacity.The present embodiment using through coagulation air-float sewage after treatment directly as the water inlet of biological contact oxidation pond, utilize the adhewsive action of micro-nano bubble to filler, improve the oxygen amount in sewage, improve the transfer efficiency of dirty water oxygen, increase oxygen to the impellent shifting in microbial film with to the depth of penetration in microbial film, make biomembranous active raising, active biomass increases, and has improved organic degradation rate.Can reduce like this aeration rate of biological contact oxidation pond, reduce aeration rate and the floor space of biological contact oxidation pond, save engineering investment cost.
Preferably, as a kind of embodiment, in steps A, adopt grid device to carry out pre-treatment.The pretreated time of grid device is 5 to 7 hours.Due to the follow-up coagulation air-float that also will carry out, therefore the pretreated time can be slightly short.
Preferably, as a kind of embodiment, in step C, enter in the sewage of biological contact oxidation pond and contain the micro-nano bubble that diffustivity is good, the diameter of described micro-nano bubble be 1 to 50 μ m wherein diameter be that 1 to 20 μ m accounts for the more than 50% of all micro-nano bubbles; Can improve like this biological activity, thereby be conducive to the metabolism of microorganism, the cumulative volume of general micro-nano bubble accounts for 1% to 20% of sewage cumulative volume, and preferably, the cumulative volume of micro-nano bubble accounts for 10% to 15% of sewage cumulative volume.
Preferably, as a kind of embodiment, in step C, described filler is half soft bat wool, utilizes the adsorption between micro-nano bubble and bat wool, improves oxygen utilization efficiency, reduces oxygen usage quantity.The volume of described filler account for described biological contact oxidation pond volume 70% to 85%, the biofilm amount of described filler is 220kg/m
3to 380kg/m
3.Half soft bat wool light weight, intensity are high, and physics, stable chemical performance are durable in use; And half soft bat wool is three-dimensional arrangement in the water of turbulent fluctuation, can better contact with micro-nano bubble, surface-area is large, and microbial film quantity is many, adhewsive action is strong, can fully contact with micro-nano bubble with sewage; And half soft bat wool is difficult for blocked.The clearance rate of half soft cellulose filler is large, is conducive to the rising of micro-nano bubble, and the interface being also conducive between microbial film and sewage is upgraded simultaneously.It is little, with low cost that the filler of employing fibrous bundle produces sludge quantity in sewage treatment process.The biomass of above-mentioned biofilm can form thick and closely knit microbial film on the filler of biological contact oxidation pond.The volume of described filler account for whole biological contact oxidation pond volume 70% to 85%; The sewage that enters biological contact oxidation pond in the present embodiment enters from the bottom of biological contact oxidation pond, and therefore half of the present embodiment soft bat wool should be arranged in whole biological contact oxidation pond uniformly to ensure fully contacting of filler and micro-nano bubble.The half soft bat wool that the present invention adopts has certain intensity.The present invention organically combines half soft bat wool and micro-nano bubble, acting in conjunction, micro-nano bubble can improve the biomembranous biological activity on half soft bat wool surface, promote biomembranous metabolism, the area that contacts, adsorbs between half soft bat wool and micro-nano bubble is simultaneously larger, can be by enough micro-nano bubble absorption at filling surface, extend the lifetime that gas ducks in drink, improve the utilization ratio of oxygen in bubble, enough spaces are provided to again the movement of micro-nano bubble.
Preferably, as a kind of embodiment, in step B, the time that described sewage stops in coagulation floatation is 30 to 60 minutes, and in step C, the time that described sewage stops in biological contact oxidation pond is 1 to 6 hour.Sewage has important impact in the residence time of coagulation floatation to sewage disposal, if overstand, the bubbles volume that air supporting produces can reduce and then have influence on the treatment effect of follow-up biological contact oxidation pond, if the residence time is too short, the poor effect of coagulation air-float, the bubble that same micro-nano bubble generator produces is too low, and the air bubble content in sewage is low, also can affect the treatment effect of follow-up biological contact oxidation pond.Same, also there is very important impact the residence time of sewage in biological contact oxidation pond on sewage disposal; If overstand, nutritive substance exhaust the deterioration that easily causes wastewater treatment efficiency, if the residence time is too short, pollution substance is not also able to do in time to be absorbed by mushroom microorganism, can cause equally process result degrades.The present invention stops sewage 30 to 60 minutes in coagulation floatation, and now sewage remove oil content, the fiber etc. in sewage by coagulation air-float, and the micro-nano air bubble content in sewage is moderate simultaneously; Sewage of the present invention stops 1 to 6 hour in biological contact oxidation pond, and the nutritive ingredient in sewage can meet microbial growth demand, and the organic substance in sewage can be decomposed by microorganism in time, and microorganism active is stronger, and treatment effect is better.
Embodiment 1
Needing the sewage water yield of processing is 300 tons/day, and the water quality of sewage is as shown in table 1, and above-mentioned sewage collecting, to water collecting basin,, is driven in coagulation floatation through sewage pump after 5 hours through grid pre-treatment;
In coagulation floatation, be provided with micro-nano bubble generator, first sewage being carried out to coagulation air-float processes 30 minutes, secondly, in biological contact oxidation pond, be filled with the half soft bat wool that accounts for whole biological contact oxidation pond volumetric spaces 85%, biological bacteria is joined in biological contact oxidation pond, add sewage and fill, standing 24 hours emptying; And then add biological bacteria, now grow microbial film on half soft bat wool surface.The biological bacteria that the biomass that utilizes biofilm is 380kg/m3 is to the sewage disposal in biological contact oxidation pond after 3 hours, and overflow is to secondary sedimentation basins; Process 1.5 to 2 hours at secondary sedimentation basins.
In the present embodiment, the volume of water collecting basin is 1000 cubic metres, and the volume of coagulation coagulation floatation is 100 cubic metres, and the volume of biological contact oxidation pond is 200 cubic metres, and the volume of secondary sedimentation basins is 100 cubic metres.Be 300-400 cubic meter and adopt the volume of at present general design biological contact oxidation pond, therefore, adopt sewage treatment process of the present invention, can reduce the volume of biological contact oxidation pond, reduce construction investment.
Embodiment 2
Sewage pretreatment time is 7 hours, the coagulation air-float treatment time is 60 minutes, in biological contact oxidation pond, be filled with the half soft bat wool that accounts for whole biological contact oxidation pond volumetric spaces 70%, the biomass of biological bacteria biofilm is 220kg/m3, the treatment time of biological contact oxidation pond is 6 hours, other technical process, with embodiment 1, are not repeating.Water-quality guideline after treatment is in table 1.
Table 1 is processed the contrast of front sewage quality and the rear water quality of the embodiment of the present invention 1 ~ 2 processing:
| Water-quality guideline | COD(mg/L） | BOD(mg/L） | SS（mg/L） | pH | NH 3-N |
| Before processing | 2000 | 150 | 110 | 7.5 | 60 |
| Embodiment 1 | 100 | 10 | 5 | 7 | 5 |
| Embodiment 2 | 110 | 12 | 4 | 7.1 | 5 |
As can be seen from Table 1, utilize the water quality of sewage treatment process processing of the present invention to meet national GB8978-1996 " integrated wastewater discharge standard " primary standard, obvious to the organism treatment effect in sewage.
Based on same inventive concept, referring to Fig. 2 to Fig. 4, the present invention also provides a kind of waste disposal plant, and described waste disposal plant comprises pretreatment unit 1, coagulation floatation 2, biological contact oxidation pond 3 and secondary sedimentation basins 4; Described coagulation floatation 2 comprises coagulation air-float separate tank pond body 21 and coagulation air-float device, in described biological contact oxidation pond 3, be provided with filler 31, described pretreatment unit 1 is connected by lift pump 11 with described coagulation floatation 2, the water outlet of described coagulation floatation 2 is communicated with the water-in of described biological contact oxidation pond 3, and the water outlet of described biological contact oxidation pond 3 is communicated with the water-in of secondary sedimentation basins 4.The present embodiment is connected coagulation floatation with biological contact oxidation pond, water by coagulation air-float processing directly enters biological contact oxidation pond, micro-nano bubble after utilizing coagulation air-float to process in sewage can make the organism in sewage fully contact with the microorganism in biological contact oxidation pond, while is due to the even diffusion of micro-nano bubble, oxygen in sewage in biological contact oxidation pond is evenly distributed, and micro-nano bobble rise velocity is slow, lift velocity is approximately 3 hours/meter, and micro-nano bubble volume is little, corresponding specific surface area is large, ensureing under the condition of same oxygen level, can reduce the aeration rate in biological contact oxidation pond, facility investment and running cost are saved, and the volume of biological contact oxidation pond is reduced.Pretreatment unit in the present embodiment is grid.
Preferably, described waste disposal plant also comprises water collecting basin 5, and described water collecting basin is used for collecting need sewage to be processed.
Preferably, as a kind of embodiment, described air-floating apparatus is micro-nano bubble generator, described micro-nano bubble generator comprises pressured air-dissolving device and micro-nano bubble releasing device, described pressured air-dissolving device and micro-nano bubble releasing device are connected, described pressured air-dissolving device comprises water inlet pipe 22, pressurizing device, dissolved air water tank 23 and dissolved air water delivery line 24, described micro-nano bubble releasing device comprises micro-nano bubble generator 25, on described micro-nano bubble generator 25, is provided with jet hole; Described pretreatment unit 1 is connected by water inlet pipe 22 with described dissolved air water tank 23, described pressurizing device is connected with described dissolved air water tank 23, one end of described dissolved air water delivery line 24 is connected with described dissolved air water tank, the other end of described dissolved air water delivery line 24 is connected with described micro-nano bubble generator 25, and described micro-nano bubble generator 25 is arranged on the bottom of described coagulation floatation body 21.Coagulation air-float treatment scheme in the present embodiment is to be raised pump through the sewage of pretreatment unit processing to promote while entering dissolved air water tank, sewage is generally pressurized to 2 ~ 3 normal atmosphere, pass into a certain amount of pressurized air by pressurizing device toward dissolved air water tank 23 simultaneously, the sewage gas-vapor mix with certain pressure stays for some time in dissolved air water tank, carry out the dissolving of mixing wastewater with air and air, then discharging micro-nano bubble by the jet hole of micro-nano bubble generator makes it enter coagulation floatation, micro-nano bubble generator produces negative pressure simultaneously, in the process that these micro-nano bubbles rise with oil content, the fiber isodensity small-particle approaching with water fully contacts, after absorption, rise to the water surface, form foam and be separated, water is separated thus.In the present embodiment, the diameter of the micro-nano bubble producing is 1-50 μ m, the water that enters dissolved air water tank is through waste disposal plant water outlet after treatment, the water yield that enters dissolved air water tank accounts for whole coagulation floatation and processes 30% of the water yield, reflux ratio is herein 30%, and described water inlet pipe 22 is connected with the outlet pipeline of whole waste disposal plant; Described micro-nano bubble generator is spherical.
Preferably, as a kind of embodiment, described pressurizing device is force (forcing) pump.
Preferably, as a kind of embodiment, described pressurizing device is gas self-straw 26 and water level sensor 27, and described gas self-straw 26 is arranged on described water inlet pipe 22, is provided with gas and adjusts valve 261 from pipette on gas self-straw; Described water level sensor 27 is arranged on the inside of described dissolved air water tank 23, be used for controlling gas and adjust valve 261 from pipette, make the water level in dissolved air water tank 23 maintain preset level, and obtain the gas dissolving water of preset concentration, and then regulate micro-nano bubble amount and concentration in the water inlet of biological contact oxidation pond.
More excellent, the pressured air-dissolving device of the present embodiment also comprises pressure transmitter 28 and outlet valve 29, pressure transmitter 28 and outlet valve 29 are arranged on dissolved air water delivery line 24, and near dissolved air water tank 23.In the present embodiment, by lift pump 11, sewage is sucked from pretreatment unit, gas self-straw is negative pressure, thereby adjusts valve self-priming gas by gas from pipette, can be to the pressure fluid of carrying gas-liquid mixed in water inlet pipe; The pressure that detects dissolved air water tank with pressure transmitter regulates with outlet valve simultaneously, the pressure in dissolved air water tank can be adjusted to preset value, adjusts valve by water level sensor control from pipette, makes the water level in dissolved air water tank remain on preset level.
Preferably, as a kind of embodiment, described biological contact oxidation pond 3 comprises pond body 32 and filler 31, and described filler is half soft bat wool, the volume of described filler 31 account for described pond body 32 volume 70% to 85%, be provided with shore pipe in the bottom of described pond body.
Preferably, as a kind of embodiment, the water outlet of described coagulation floatation is communicated with the water-in of the bottom that is arranged on described biological contact oxidation pond by connecting pipeline.This is for micro-nano bubble is stirred more fully to the sewage in biological contact oxidation pond.
Preferably, as a kind of embodiment, described air-floating apparatus arranges 2 micro-nano bubble releasing devices, and one of them micro-nano bubble generator 25 is arranged in described coagulation floatation, and another micro-nano bubble generator 33 is arranged on the bottom of described biological contact oxidation pond.In the present embodiment, the micro-nano bubble releasing device of micro-nano bubble generator is separately positioned on to coagulation floatation and biological contact oxidation pond, can avoids like this problem of the aeration deficiency of biological contact oxidation pond.
Preferably, as a kind of embodiment, described coagulation floatation is also provided with gas floatation separation device, and described gas floatation separation device comprises slag scraper 201, and described slag scraper is arranged on the top of described coagulation floatation.Described gas floatation separation device is for the treatment of the scum silica frost that swims in sewage level.
Finally, it should be noted that, in this patent document, the relational terms such as first, second grade is only for an entity or operation are separated with another entity or operational zone, and not necessarily requires or imply and between these entities or operation, have any relation or sequentially.And, in this patent document, term " comprises ", " comprising " or its any other variant, it is intended to contain but not exclusive inclusion, thereby make to comprise process, method, article or the equipment of a series of key elements, not only comprise these key elements, but also comprise and clearly not listing and other key elements that those skilled in the art can know, or be also included as the known requisite key element of these processes, method, article or equipment.
The above embodiment has only expressed several embodiment of the present invention, and it describes comparatively concrete and detailed, but can not therefore be interpreted as the restriction to the scope of the claims of the present invention.It should be pointed out that for the person of ordinary skill of the art, without departing from the inventive concept of the premise, can also make some distortion and improvement, these all belong to protection scope of the present invention.Therefore, the protection domain of patent of the present invention should be as the criterion with claims.
Claims (6)
1. a sewage treatment process, is characterized in that, described technique comprises the following steps:
A: pre-treatment: will need sewage to be processed after pre-treatment, and be driven in coagulation floatation through lift pump; This step is removed large-sized floating matter, suspended substance and less solid matter;
B: coagulation air-float processing: be provided with coagulation air-float device in coagulation floatation, sewage is carried out, after coagulation air-float separating treatment, entering in biological contact oxidation pond; In dissolved air flotation process, the molecule that the density in removal sewage and water are approaching; In step B, the residence time of described sewage in coagulation floatation is 30 to 60 minutes;
C: bio-contact oxidation processing: be provided with filler in described biological contact oxidation pond, different quality object is adopted to the means of taming targetedly, select suitable biological bacteria, biological bacteria is bred at filling surface raised growth, form microbial film, in this step, taking BOD, COD as main pollutent is removed, remove nitrogen phosphorus simultaneously; In step C, enter in the sewage of biological contact oxidation pond and contain the micro-nano bubble that diffustivity is good, the diameter of described micro-nano bubble is 1 to 50 μ m, and wherein diameter is that 1 to 20 μ m accounts for the more than 50% of all micro-nano bubbles; In step C, the time that described sewage stops in biological contact oxidation pond is 1 to 6 hour;
D: secondary sedimentation processing: sewage overflow to the secondary sedimentation basins through bio-contact oxidation processing directly discharges after precipitation process and subsequent disposal.
2. sewage treatment process according to claim 1, is characterized in that, in step C, described filler is half soft bat wool; The volume of described filler account for described biological contact oxidation pond volume 70% to 85%, the biofilm amount of described filler is 220kg/m
3to 380kg/m
3.
3. a waste disposal plant, is characterized in that, described waste disposal plant comprises pretreatment unit, coagulation floatation, biological contact oxidation pond and secondary sedimentation basins;
Described coagulation floatation comprises coagulation air-float separate tank pond body and coagulation air-float device, in described biological contact oxidation pond, be provided with filler, described pretreatment unit is connected by lift pump with described coagulation floatation, the water outlet of described coagulation floatation is communicated with the water-in of described biological contact oxidation pond, and the water outlet of described biological contact oxidation pond is communicated with the water-in of secondary sedimentation basins;
Described biological contact oxidation pond comprises pond body and filler, and described filler is half soft bat wool, the volume of described filler account for described pond body volume 70% to 85%;
Described coagulation air-float device is micro-nano bubble generator, described micro-nano bubble generator comprises pressured air-dissolving device and micro-nano bubble releasing device, described pressured air-dissolving device and micro-nano bubble releasing device are connected, described pressured air-dissolving device comprises water inlet pipe, pressurizing device, dissolved air water tank and dissolved air water delivery line, described micro-nano bubble releasing device comprises micro-nano bubble generator, on described micro-nano bubble generator, is provided with jet hole; Described pretreatment unit is connected by water inlet pipe with described dissolved air water tank, described pressurizing device is connected with described dissolved air water tank, one end of described dissolved air water delivery line is connected with described dissolved air water tank, the other end of described dissolved air water delivery line is connected with described micro-nano bubble generator, and described micro-nano bubble generator is arranged on the bottom of described coagulation floatation body.
4. waste disposal plant according to claim 3, is characterized in that, the water outlet of described coagulation floatation is communicated with the water-in of the bottom that is arranged on described biological contact oxidation pond by connecting pipeline.
5. waste disposal plant according to claim 3, it is characterized in that, described air-floating apparatus arranges 2 micro-nano bubble releasing devices, one of them micro-nano bubble releasing device is arranged in described coagulation floatation, and another micro-nano bubble releasing device is arranged on the bottom of described biological contact oxidation pond.
6. waste disposal plant according to claim 3, is characterized in that, described coagulation floatation is also provided with gas floatation separation device, and described gas floatation separation device comprises slag scraper, and described slag scraper is arranged on the top of described coagulation floatation.
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| CN201210544086.5A CN103043852B (en) | 2012-12-14 | 2012-12-14 | Wastewater treatment process and device |
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| CN104086042B (en) * | 2014-06-20 | 2016-03-16 | 上海勘测设计研究院 | The former enhanced water pretreatment process in a kind of micro-polluted drinking water water source |
| CN105819620A (en) * | 2016-03-30 | 2016-08-03 | 广州资源环保科技股份有限公司 | Wastewater treatment technology and device beneficial to removing black and odorous water |
| CN107311364A (en) * | 2017-08-30 | 2017-11-03 | 丹阳市百盛电器有限公司 | The plasma treatment appts and method of a kind of fruits and vegetables industry sewage |
| CN107944601A (en) * | 2017-11-07 | 2018-04-20 | 中国石油天然气集团公司 | Using characteristic contamination Source Tracing as the sewage disposal appraisal procedure and device instructed |
| CN108911003A (en) * | 2018-07-27 | 2018-11-30 | 金强 | A kind of micro-nano bubble air-float degreasing device and technique |
| CN110627325A (en) * | 2019-10-16 | 2019-12-31 | 新疆水处理工程技术研究中心有限公司 | Process method for treating food wastewater |
| CN110921992A (en) * | 2019-12-15 | 2020-03-27 | 刘彬 | Water cleaning system based on air floatation design |
| CN111204929B (en) * | 2020-01-17 | 2023-04-07 | 内江师范学院 | Municipal sewage treatment method based on biological contact oxidation process |
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| CN203048732U (en) * | 2012-12-14 | 2013-07-10 | 蓝星环境工程有限公司 | Sewage treatment device |
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| CN202152290U (en) * | 2011-07-08 | 2012-02-29 | 蓝星环境工程有限公司 | Pressurized dissolved-air floating system |
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