CN102807282A - Wet type raw material feeding device and method for feeding multiple raw materials - Google Patents

Wet type raw material feeding device and method for feeding multiple raw materials Download PDF

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Publication number
CN102807282A
CN102807282A CN2012102945533A CN201210294553A CN102807282A CN 102807282 A CN102807282 A CN 102807282A CN 2012102945533 A CN2012102945533 A CN 2012102945533A CN 201210294553 A CN201210294553 A CN 201210294553A CN 102807282 A CN102807282 A CN 102807282A
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pipe
tank body
water
raw material
activated carbon
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CN102807282B (en
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史玉乾
曾敬
高启全
蒋磊
崔腾军
王芳
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YINGUANG CHEMICAL INDUSTRY GROUP Co Ltd GANSU
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YINGUANG CHEMICAL INDUSTRY GROUP Co Ltd GANSU
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Abstract

The invention relates a wet type raw material feeding device and a method for feeding multiple raw materials. The wet type raw material feeding device comprises a tank body (1), a pore plate (2), baffles (3), a water pump (4) and a corresponding mated pipeline. The wet type raw material feeding device is characterized in that the pore plate (2) is rectangular, through holes are uniformly distributed, the two sides of the pore plate (2) are vertically welded on the inner wall of the tank body (1); the cylindrical tank body (1) is divided into a large part and a small part, wherein the large part is a mixing area and the small part is a discharge area; the inner wall of the mixing area of the tank body (1) is vertically provided with the three baffles (3), the bottom of the mixing area of the tank body (1) is connected with a pipe C, a pipe A is connected in the middle of the mixing area of the tank body (1) in the tangential direction, a pipe B is connected to the bottom of the discharge area of the tank body (1), the pipe B is connected with an inlet pipe of the water pipe (4), and the pipe A and the pipe C are connected with an outlet pipe of the water tank (4). The invention provides the device for comprehensively feeding various raw materials including powdered activated carbon, flour, glucose, nitrogenous fertilizer, monopotassium phosphate, trisodium phosphate, nitrobacterium culture promoter and strains, thereby greatly improving the operation environment and reducing labor intensity.

Description

The addition method of a kind of raw material wet type throwing device and plurality of raw materials
Technical field
The invention belongs to environmental technology field, be specifically related to a kind of Powdered Activated Carbon, nutritive salt and microbial strains throwing device.
Background technology
At present, for advanced treatment of industrial waste water, can adopt the method that Powdered Activated Carbon adsorbs stink, colourity, organic pollutant etc. in the water that adds.Country's pay attention to day by day environmental protection work, the environmental emission standard improves constantly, and Powdered Activated Carbon is used also more and more widely in dirt, wastewater treatment.Powdered Activated Carbon wet type adding equipment generally all has some mixing drums; Mixing drum generally has whipping appts; After Powdered Activated Carbon and water mixed in mixing drum, it was about 8% slurries that Powdered Activated Carbon is configured to concentration, through volume pump mixed solution is dropped in the former water again.Powdered Activated Carbon automatic wet-type adding equipment generally all has a feed bin, and this feed bin is positioned at the upper reaches of whole plant, and its purposes is the storage powder gac.The top of feed bin is typically provided with the opening that communicates with ambient atmosphere, so that the feed bin internal pressure keeps constant, guarantees that Powdered Activated Carbon can successfully join in the feed bin and successfully from feed bin, provides.Because the Powdered Activated Carbon fineness of selecting for use is 150~200 orders; Powdered Activated Carbon can produce a large amount of airborne dusts in the process that adds feed bin; This opening just because of the feed bin top; Make airborne dust run out of feed bin, this not only causes serious dust pollution to surrounding environment, has also caused the waste of Powdered Activated Carbon.So have the dealer to install sack cleaner,, increased complicacy, input cost and the running cost of equipment but effect is not good enough to reduce dust pollution at this pneumostome place.The Powdered Activated Carbon wet type adds two shortcomings: the pollution problem of (1) dust from flying.Powdered Activated Carbon all is packed, and unpacking it feeds intake when pouring the charcoal stock tank into, and entrained air the black powder gac and flown upward, and the chemical feed room dust is filled the air, and causes work under bad environment, and the operator works in this environment for a long time and is prone to suffer from occupational illness.Dust pollution is to restrict its key in application problem for a long time.(2) powdered carbon blockage problem.Domestic Powdered Activated Carbon quality is uneven, and is impure many, in each big water factory application process, the stuck situation of accurate feeding machine taken place repeatedly, serious threat water factory operating safety.
Trade effluent generally will add biochemistry pool in 1: 1 ratio with sewage when carrying out biochemical treatment, and adds nutritive salt.For guaranteeing the mikrobe eubolism; The ratio of carbon in the waste water (C), nitrogen (N), phosphorus (P) generally was controlled at 100: 5: 1; Situation out of proportion according to the complexity of the concrete pollutent biochemical treatment of waste water and carbon (C), nitrogen (N), phosphorus (P) needs in time to replenish the necessary nutrition agent of bacterium, like flour, glucose, microcosmic salt etc.Trade effluent hard to manage BOD often occurs at anaerobism, aerobic system 5Anaerobism, aerobic system must be returned in a large number with settling tank mud in/COD<0.1, strengthen the amount of adding nutrition agent simultaneously, guarantee BOD 5The activity of anaerobism, aerobic bacteria is recovered in/COD>0.1, and then recovers the ability of microbiological deterioration pollutent.Most of domestic sewage work becomes bag to pour the sewage pond into nutrition agent with artificial; Nutrition agent is dissolved in the sewage; Squeeze into biochemistry pool with pump; Become organic carbon or waste material at the bottom of having part flour, glucose, potassium primary phosphate, tsp etc. to be deposited to the sewage pond, need to cause very big waste at the bottom of the manual regular cleaning pond.Also have and directly pour nutrition agent into biochemistry pool.There is part nutrition agent sedimentation becoming organic carbon to cause biochemical sludge rotten and then cause biochemical treatment system disorderly.
Ammonia nitrogen is the bigger pollution factor of harm in the water body, and it can cause the eutrophication in river, lake, and water body self-purification ability is weakened.The ammonia nitrogen of polluted-water is often referred to the nitrogen that exists with the ammonia form, and the difficulty of ammonia nitrogen removal is much bigger in the contaminated water body of other organic pollutant relatively.In the prior art, the removal method of ammonia nitrogen mainly contains physics, chemistry and biological method in the contaminated water body.Physics or chemical method comprise air stripping method, break point chlorination, ion exchange adsorption, flocculent precipitation, electroosmose process, catalytic wet air oxidation, liquid-film method etc.These methods generally are used for the pre-treatment of high-concentration ammonia nitrogenous wastewater, and processing cost is very high.It is the effect through certain micro-organisms that biological process is removed ammonia nitrogen, thereby makes the ammonia nitrogen in the contaminated water body finally form the purpose that nitrogen effusion water body reaches purifying treatment.The biological process cost is much lower, and its applicable surface is also wider, like removal of ammonia nitrogen in ammonia nitrogen purifying treatment, sanitary wastewater or the trade effluent of fishery cultivating water body etc.Biological process is removed ammonia nitrogen and is mainly comprised nitrification process and denitrification process.In the nitrification process, ammonia nitrogen is oxidized to nitrate salt or nitrite nitrogen under the aerobic condition under the effect of nitrifier; Denitrification is meant that nitrate salt and nitrite are reduced to the process of gaseous nitrogen.Under anoxia condition, utilize organism as electron donor, denitrifying bacterium is reduced to nitrogen with nitrate salt and nitrite.In these two processes, it is generally acknowledged that the nitrification process is even more important, it is the key that biological process is removed ammonia nitrogen, the difficulty of its completion is also higher relatively.Because most of nitrifiers are chemosynthetic autotroph mikrobes, and compare with the heterotroph mikrobe, the autotrophic microorganism proliferative speed is slow, growing environment is harsh, can't in the growth competition, get the mastery with the heterotroph mikrobe under a lot of conditions.Therefore; When nitrifier content in the water body is low; The environment such as oxygen supply and pH value of only regulating sewage still can't make the breeding of nitrifier self-sow in the short period of time; In way common in the industry is directly in sewage, to throw in the nitrated bacterial classification of cultured high density, contains the active sludge of high density nitrifier like input.The nitrated bacterial classification of these high densitys is to cultivate through special operation to obtain, and has all introduced the cultural method of the nitrated bacterial classification of high density that is used for removing the sewage ammonia nitrogen like Chinese patent ZL02156977.0 and one Chinese patent application 00808700.8.Introduce nitrated bacterial classification by the external world and can guarantee that really the nitrification process successfully carries out in the short period of time; But operational management is very inconvenient; Cost is also higher relatively, and the suitability of this method is not wide in range, just as handling very not suitable for the bigger industrial sewage of quantity discharged.Chinese invention patent application number 200610025171.5 provides a kind of method that adopts sequencing batch active sludge to remove sewage ammonia nitrogen; Means such as oxygen supply through adding a kind of nitrobacteria culture promoter and fit adjustment sewage to sewage and pH value can be built in water body and are fit to nitrobacteria growth breeding environment; Nitrifier is growth and breeding at short notice, removes in the ammonia nitrogen nitrification process need and introduces this technical problem of nitrated bacterial classification by the external world thereby can solve biological process.
Chinese invention patent application number 200910196310.4 " automatic adding system of powdered activated carbon " is made up of one-level pneumatic conveyer 1, accurate powder feeding machine 2, liquid powder mixer 3, first storage bin 4 and level gage 6; The material sucking port of one-level pneumatic conveyer 1 connects gac ton bag 7; Discharge port connects first storage bin 4 through feeding tube 5; First storage bin, 4 bottoms connect level gage 6, and level gage 6 connects liquid powder mixer 3, and liquid powder mixer 3 is positioned at accurate powder feeding machine 2 outlets.
China utility model patent CN202161928U " a kind of gac moistening device " comprises water tank (1); Top one side of water tank (1) has gac and drops into hole (2), the external cleaning apparatus of opposite side (3), the outer vacuum valve (4) that also is provided with of cleaning apparatus (3); The interior reserved part water of said water tank (1); The top of water tank (1) also is provided with row's shower nozzle (5), the external filtration unit of the lower wall of said water tank (1) (6) and the pump housing (7), and the described pump housing (7) is connected with reaction kettle (10) through first pipeline (9).Said first pipeline (9) joins through external second pipeline (8) and shower nozzle (5), and first variable valve (12) and second variable valve (11) are set respectively on described first pipeline (9) and second pipeline (8).Described cleaning apparatus (3) is a bag-type dust collector.
China utility model patent CN201914516U " a kind of Powdered Activated Carbon intelligence dosing system " comprises feed bin (3), worm conveyor (2) and jet mixer (17); It is characterized in that: be provided with bale broken system casing (8) in described feed bin (3) top; Be provided with screen drum (7) and drive unit thereof in described bale broken system's casing (8); Described bale broken system's casing (8) is provided with the guide case (9) that docks with the import of described screen drum (7); What described bale broken system's casing (8) was provided with the material bag that acts on the described guide case (9) revolves doctor blade assembly (10); Described guide case (9) is to being connected to rotary conveyor (12), and described bale broken system's casing (8) is provided with the residue surge drum (6) that docks with the outlet of described screen drum (7).
Chinese invention patent application number 201110007316.X " a kind of novel many technology synergies catalysis microbubble ozone high grade oxidation tower "; It is characterized in that: Powdered Activated Carbon (PAC) wet type dosing system is set on the mechanically mixing air dissolved pump suction culvert; The activated carbon of certain particle size (particle diameter is 10~50 μ m) is added the ozone oxidation tower, have adsorption on the one hand; Cause free chain reaction at aqueous phase on the other hand, thereby can realize the concerted catalysis of Powdered Activated Carbon (PAC), improve ozone oxidation efficient the ozone oxidation effect.
Chinese invention patent application number 201010235865.8 " biological on-line automatic dosing system " includes: frame, sequence controller, cultivation bucket, substratum are provided unit, water inlet unit, self-circulation and water and are provided unit, oxygenation unit, temperature conditioning unit.Compared with prior art; The biological on-line automatic dosing system that the present invention proposes has through substratum provides unit, water inlet unit, self-circulation and water granting unit, oxygenation unit, temperature conditioning unit; For the activation of synergic bacteria provide various suitable conditions, and growth and breeding essential nutrition is provided; The input of guaranteeing activation bio-synergistic bacterium is able to implement, thereby has guaranteed wastewater biological synergic continuous and effective; A product also capable of using simultaneously can be adjusted the dosage of synergic bacteria liquid automatically according to the variation of water outlet COD, reduces the production run cost greatly.
Chinese invention patent application number 200610025171.5 " a kind of method that adopts activated sludge process to remove sewage ammonia nitrogen " comprising: 1) sewage gets into the aeration tank after preliminary sedimentation is removed solid impurity; The active sludge that has domestication in the aeration tank; Drop into nitrobacteria culture promoter in the sewage; Its component comprises molasses, metal-salt and sorbent material, proportioning: molasses 100 weight parts; Metal-salt 0.2~2.5 weight part; Sorbent material 1~8 weight part.Metal-salt comprises A and B, and wherein A is MnSO 4Or MnCL 2, B is MgSO 4Or CaCL 2Or both mixtures, the mol ratio of A and B is 10: (0.5~5), above-mentioned sorbent material are one or more mixtures in zeolite powder, zeyssatite, Powdered Activated Carbon or the flyash; 2) sewage gets into first settling tank and carries out sludge settling; 3) the first settling tank supernatant gets into agitated pool, has the active sludge of domestication in the agitated pool; 4) sewage gets into second settling tank and carries out sludge settling, the supernatant discharging.The preferably first water of nitrobacteria culture promoter drops in the sewage after being mixed with diluent again, can make promotor more even with mixing of sewage like this.In technique scheme, sewage at first carries out preliminary precipitation process, to remove the bigger solid impurity of volume.Get into then in the aeration tank, under aerobic condition, carry out nitration reaction, the release position of nitrobacteria culture promoter generally is positioned at water inlet place of sewage.As everyone knows, nitrifier is relatively responsive to outside atmosphere, and growth and breeding is very high to environment requirement, except that aerobic and suitable potential of hydrogen of needs and temperature, also needs suitable nitrifier and cultivates and promote the material existence.Existing result of study shows that dissolved organic carbon (DOC), molecular state organism (POM), this three types of materials cultivation to nitrifier under low consistency conditions of each biostearin have obvious facilitation.Chinese invention patent application number 200510111870 " a kind of method that adopts sequencing batch active sludge to remove sewage ammonia nitrogen " comprising: 1) sewage gets into reaction tank after preliminary sedimentation is removed solid impurity; The active sludge that has domestication in the reaction tank; Drop into nitrobacteria culture promoter to reaction tank in the time of water inlet; This nitrobacteria culture promoter is a kind of compsn, and component comprises molasses, manganese salt and sorbent material, and its proportioning is: molasses: 100 weight parts; Manganese salt: 0.2~3.0 weight part; Sorbent material: 1~8 weight part.Above-mentioned manganese salt is vitriol or hydrochloride, and sorbent material is one or more the mixture in zeolite powder, zeyssatite, Powdered Activated Carbon or the flyash.Sludge loading is controlled to be 0.05~0.3kgBOD 5/ kg.MLVSS, nitrobacteria culture promoter dosage are 5~20mg/l.
Chinese invention patent application number 201110379817.0 " the mixed treatment process of a kind of nitramine class, nitrobenzene and phenyl amines wastewater from chemical industry " disclosed for the 7th step: the anaerobic mud bed UASB/AF of up-flow that promotes composite waste entering band filler in the water collecting basin with pump; Low in and high out; Mikrobe will contain aromatic hydrocarbons structure pollution substance through hydrolysis and acidifying and change straight chain or short chain solubility small organic molecule into; Or with not being adsorbed the aminocompound that nitrobenzene or nitramine class material convert readily biodegradable in the waste water; Remove partial organic substances simultaneously, with the most of activated sludge tank that flows into of the anaerobism water outlet after mud separates, few part is introduced the UASB/AF bottom cycle with pump; Add life water and nutrition agent simultaneously, must in water inlet pipe, feed steam winter and keep the Sludge Bed temperature at 20~25 ℃; The 8th step: the anaerobism water outlet flows into three grades of activated sludge tanks and has carried out oxygen metabolism, and low in and high out adds life water and nutrition agent simultaneously; Wastewater flow rate and sewage amount should add in 1: 1 ratio, so that the COD concentration of extra-nutrition and reduction water inlet is removed most of organism; The core aeration head is equipped with in Aerobic Pond inside, is stirred by the air blast aeration, and the aeration rate of three grades of activated sludge tanks is high, medium and low three kinds of states; Guarantee that first step Aerobic Pond is to a large amount of oxygenations of waste water; Be the large scale cultivating aerobic bacteria, utilize aeration fully to stir nutritive substance again, guarantee that nutritive substance can sedimentation not become organic carbon by the aerobic bacteria metabolism; Outputted aerobic water partly flows into second pond, and part is recycled to aerobic import with pump; The 9th step: outputted aerobic water flows into second pond, low in and high out, and Xiang Chizhong adds PAM or PAC, realizes mud-water separation, and regularly arranging active sludge returns activated sludge tank or UASB/AF, goes out the water management suspended substance less than 100mg/l; In the 8th step in three grades of activated sludge tanks the active sludge rate of descent greater than 15%, dissolved oxygen 2~4mg/l, BOD 5/ COD>0.1.Composite waste adds biochemistry pool with sewage in 1: 1 ratio in 55~70 tons/hour, and adds nutrition agent.Is no lack of carbon (C), nitrogen (N) in the composite waste, so need to replenish the necessary carbamate additives for low phosphorus of bacterium (P).In the anaerobic system residence time is 40 hours, like BOD 5Anaerobic system must be returned in a large number with second pond mud in/COD<0.1, strengthens the amount of adding nutrition agent simultaneously, and 20~25 ℃ of waste water temperature controls recover the activity of anaerobic bacterium, guarantee BOD 5/ COD>0.1; The anaerobism recycle pump was opened weekly four hours, excessively drove the anaerobism recycle pump and can cause the broken anaerobic grain sludge of waste water internal circulating load favourable opposition, and water outlet COD is high.The aerobic residence time is 22 hours, like BOD 5Aerobic system must be returned in a large number with second pond mud in/COD<0.1, strengthens the amount of adding nutrition agent simultaneously, and 20~25 ℃ of waste water temperature controls recover the activity of aerobic bacteria, guarantee BOD 5/ COD>0.1; Aerobic recycle pump must often be opened, otherwise too much active sludge gets into all sedimentations of second pond.Second pond is opened mud scraper, and adjustment reaction tank coagulant aids PAM dosage needs to guarantee that pollutent and PAM fully react the bigger alumen ustum of formation; And can in second pond, effectively precipitate removal, when second pond mud black in color is also smelly, be that the dead or a large amount of organic carbons of a large amount of demouldings of mikrobe cause; Must change coagulant aids PAM into flocculation agent PAC temporarily; Let charge discharge in the water body, normal activity mud is field gray, only adds coagulant aids PAM under the standard state.
The present invention is further describing and further improving of centering state invention number of patent application 201110379817.0 " the mixed treatment process of a kind of nitramine class, nitrobenzene and phenyl amines wastewater from chemical industry " detail.The objective of the invention is to overcome the deficiency of above-mentioned technology; And a kind of comprehensive device that various raw materials comprise Powdered Activated Carbon, flour, glucose, potassium primary phosphate, tsp, nitrobacteria culture promoter, microbial strains that adds is provided; Not only can alleviate operative employee's labour intensity; Can also effectively control various raw materials particularly Powdered Activated Carbon to the pollution of environment; And guarantee various raw materials particularly Powdered Activated Carbon add precision, have higher job stability and safety.
Summary of the invention
The present invention adopts following technical scheme for realizing above-mentioned purpose:
A kind of raw material wet type throwing device comprises tank body 1, orifice plate 2, traverse baffle 3, water pump 4 and corresponding supporting pipelines, and it is characterized in that: orifice plate 2 is rectangle; The through hole that evenly gathers, orifice plate 2 both sides be vertically welded in tank body 1 inwall vertical on, cylindrical tank 1 is divided into large and small two portions; Major part is named the mixing zone, and small portion is discharge zone, and tank body 1 mixing zone inwall vertically is uniformly distributed with 3 three of traverse baffles; Bottom, tank body 1 mixing zone connects the C pipe, and middle part, tank body 1 mixing zone tangential direction connects the A pipe, and tank body 1 discharge zone bottom connects the B pipe; B pipe water pump 4 inlet pipes, A pipe, C pipe water pump 4 outlet pipes.
Described raw material wet type throwing device is installed a side of biochemistry pool water inlet water pump; Wherein water pump 4 inlet pipes are delivered a child and are produced water reservoir or sewage water reservoir, water pump 4 outlet pipe bifurcations, and one is removed biochemistry pool; One connects A pipe, C pipe and valve 13, B pipe water pump 4 inlet pipes.Through-hole spacing 30mm on its aperture plate 2, aperture φ 10~20mm.The raw material that wherein adds is any one or a few in Powdered Activated Carbon, flour, glucose, microcosmic salt, nitrobacteria culture promoter, the microbial strains.
When the raw material that adds was Powdered Activated Carbon, (4) outlet pipe that switches off the pump removed biochemical anaerobic pond valve, guaranteed that Powdered Activated Carbon goes in the biochemical Aerobic Pond.A kind of dust-trap 5 that adds is installed in the present invention additional when adding Powdered Activated Carbon; Comprise water inlet 6, diversion box 7, water curtain spout 8, mix mouth 10, support 11, inverted L shape runner 12, valve 13; Diversion box 7 is located at the top of said inverted L shape runner 12, the bottom that water curtain spout 8 is located at said diversion box 7; Water inlet 6 is positioned at the top of diversion box 7, the sidewall that mixing mouth 10 is positioned at inverted L shape runner 12, and a chord position 11 is positioned at the bottom of L type runner 12.Water curtain spout 8 is the finedraw of width 2~4mm, totally three roads, and spacing is uniformly distributed with.Water inlet 6 is connected with water pump 4 outlet pipes, and is provided with valve 13, by the emitted dose and the intensity of spray irrigation of valve 13 control water curtain spouts 8.The structure of inverted L shape runner 12 adopts the steel plate welding production of 3.5mm, and its outside surface is coated with the red lead paint twice, and mixing mouthfuls 10 is width 30mm, and the rectangle of length 300mm is divided into three sides of dust-trap 5 ends of falling L.
Utilize the method that adds plurality of raw materials like above-mentioned raw material wet type throwing device, it is characterized in that:
A) the first step is to open water pump 4 import and export valves, opens A pipe, C manage inlet valve, unlatching water pump 4; Sewage has in few part sewage shunting suction tank body 1 from sewage pond suction biochemistry pool, and water flows into from tank body 1 bottom in the C pipe; Water flows into from tangential, tank body 1 middle part in the A pipe; When sewage is filled with tank body 1 soon, drive B pipe outlet valve, water outlet pump 4 inlet pipes that anhydrate are regulated the import and export valve and are guaranteed tank body 1 water-in and water-out balance;
B) second step was evenly to pour raw material into tank body 1 mixing zone from container or in the packing bag; A pipe current tangential drives raw material and in water, forms eddy flow and dispersion; Drive raw material in welter and dispersion on the C pipe current direction, the collision of raw material and current is uniformly dispersed on three traverse baffles 3 in the tank body 1;
C) the 3rd step was that finely dispersed raw material passes orifice plate 2 through holes with current, was sent to biochemistry pool through the B pipe by water pump 4 at discharge zone.
When the raw material that adds was Powdered Activated Carbon, step was following:
A) the first step adds dust-trap 5 with Powdered Activated Carbon and connects with throwing device by Fig. 4, regulates tank body 1 water level earlier, makes the mixing mouth 10 of dust-trap 5 be submerged in 50~100mm under tank body 1 liquid level; Again the powder gac bag 9 of opening is put into inverted L shape runner 12; Open valve 13; And through valve 13 adjusting water curtain spouts 8 intensity of spray irrigation; And movable gac bag 9 makes the powder gac evenly pour tank body 1 into through inverted L shape runner 12, and mixes mixing mouthfuls 10, and burgy has fallen fully in will wrapping;
B) second step was that finely dispersed Powdered Activated Carbon passes orifice plate 2 through holes with current, was sent to biochemistry pool through the B pipe by water pump 4 at discharge zone;
C) the 3rd step was successively the Powdered Activated Carbon bag to be put into inverted L shape runner 12, repeated above step, after the Powdered Activated Carbon of capacity is squeezed into biochemistry pool, stopped.
Nutrition agent adds groove and has carried out the traverse baffle design; Have three and cell body welding, the side direction traverse baffle is processed as spination in the groove, adds in flour, the glucose process as delivery medium with sewage; When improving mixing dynamics, uniformity coefficient, increased the utilization ratio of various nutrition medicaments.
Description of drawings
Fig. 1 is a raw material wet type throwing device synoptic diagram of the present invention.
Fig. 2 is tank body 1 front view in the raw material wet type throwing device.
Fig. 3 is tank body 1 vertical view in the raw material wet type throwing device.
Fig. 4 is that raw material wet type throwing device installs dust-trap 5 synoptic diagram additional.
Code name explanation among the figure: 1-tank body; The 2-orifice plate; The 3-traverse baffle; The 4-water pump; The 5-dust-trap; The 6-water inlet; The 7-diversion box; 8-water curtain spout; 9-gac bag; 10-mixes mouth; The 11-support; 12-inverted L shape runner; The 13-valve.
Embodiment
Further set forth the present invention's wet type in wastewater treatment process below in conjunction with specific embodiment and add Powdered Activated Carbon, flour, glucose, microcosmic salt, nitrobacteria culture promoter, microbial strains.The top the spirit and scope of the present invention that disclose do not receive the restriction of embodiment.
Embodiment 1
Like Fig. 1, Fig. 2, shown in Figure 3, a kind of raw material wet type throwing device comprises tank body 1, orifice plate 2, traverse baffle 3, water pump 4 and corresponding supporting pipelines; It is characterized in that: orifice plate 2 is rectangle, the through hole that evenly gathers, orifice plate 2 both sides be vertically welded in tank body 1 inwall vertical on; Cylindrical tank 1 is divided into large and small two portions, and major part is named the mixing zone, and small portion is discharge zone; Tank body 1 mixing zone inwall vertically is uniformly distributed with 3 three of traverse baffles, and bottom, tank body 1 mixing zone connects the C pipe, and middle part, tank body 1 mixing zone tangential direction connects the A pipe; Tank body 1 discharge zone bottom connects the B pipe, B pipe water pump 4 inlet pipes, A pipe, C pipe water pump 4 outlet pipes.
Described raw material wet type throwing device is installed a side of biochemistry pool water inlet water pump; Wherein water pump 4 inlet pipes are delivered a child and are produced water reservoir or sewage water reservoir, water pump 4 outlet pipe bifurcations, and one is removed biochemistry pool; One connects A pipe, C pipe and valve 13, B pipe water pump 4 inlet pipes.Through-hole spacing 30mm on its aperture plate 2, aperture φ 10~20mm.The raw material that wherein adds is any one or a few in Powdered Activated Carbon, flour, glucose, microcosmic salt, nitrobacteria culture promoter, the microbial strains, selects to go biochemical anaerobic pond or Aerobic Pond according to the production needs.
When the raw material that adds is in flour, glucose, microcosmic salt, nitrobacteria culture promoter, the microbial strains any one or a few; Raw material wet type throwing device is appointed a side that so is installed in biochemistry pool water inlet water pump; Device has made full use of the power of water pump; Medicament stirs through fluid in groove automatically, and the spination traverse baffle enhancing mixed of groove inwall capable of using, and is easy to operate.
Concrete operations are following:
1. start water pump to the biochemistry pool normal water supply.
2. the inlet valve of opening dosing tank is to 1 moisturizing of dosing tank tank body.
3. open dosing tank tank body 1 outlet valve, and regulate the terminal valve of dosing tank tank body 1, make the liquid level in the groove keep balance.
4. in dosing tank tank body 1, add nutrition medicaments such as flour, glucose.
5. raw material washes away mixing in the stirring of dosing tank tank body 1 water inlet and is inhaled into pump entrance by dosing tank tank body 1 outlet pipe after through orifice plate, thereby is added into biochemistry pool uniformly.
6. medicament cleans dosing tank after adding completion, and completion is closed the dosing tank inlet valve earlier after cleaning, and closes outlet valve again.
Embodiment 2
Utilize like above-mentioned raw material wet type throwing device and add the method that comprises flour, glucose, microcosmic salt, nitrobacteria culture promoter, microbial strains, it is characterized in that:
A) the first step is to open water pump 4 import and export valves, opens A pipe, C manage inlet valve, unlatching water pump 4; Sewage has in few part sewage shunting suction tank body 1 from sewage pond suction biochemistry pool, and water flows into from tank body 1 bottom in the C pipe; Water flows into from tangential, tank body 1 middle part in the A pipe; When sewage is filled with tank body 1 soon, drive B pipe outlet valve, water outlet pump 4 inlet pipes that anhydrate are regulated the import and export valve and are guaranteed tank body 1 water-in and water-out balance;
B) second step was evenly to pour raw material into tank body 1 mixing zone from container or in the packing bag; A pipe current tangential drives raw material and in water, forms eddy flow and dispersion; Drive raw material in welter and dispersion on the C pipe current direction, the collision of raw material and current is uniformly dispersed on three traverse baffles 3 in the tank body 1;
C) the 3rd step was that finely dispersed raw material passes orifice plate 2 through holes with current, was sent to biochemistry pool through the B pipe by water pump 4 at discharge zone.
When needs add a large amount of Powdered Activated Carbon within a short period of time, raise suddenly such as water factory's water inlet pollutent, in the time of need per hour adding 2 tons of Powdered Activated Carbons, step is following:
A) the first step is poured the powder gac bag of many bags mouths opens into tank body 1 continuously;
B) second step was to open water pump 4 import and export valves, opened water pump 4, and sewage is from sewage pond suction biochemistry pool; Drive B pipe outlet valve; The life water tube hose that disappears is inserted with in few part sewage shunting suction tank body 1 discharge zone, and water flow drives powder gac gets into the B pipe from tank body 1 discharge zone, opens when the motionless powder gac of current band that A manages, C manages inlet valve; Have in few part sewage shunting suction tank body 1; Water flows into from tank body 1 bottom in the C pipe, and water flows into from tangential, tank body 1 middle part in the A pipe, when current drive the powder gac again, closes the A pipe, C manages inlet valve;
C) the 3rd step was successively the Powdered Activated Carbon bag to be put into, and repeated above step, after the Powdered Activated Carbon of capacity is squeezed into biochemistry pool, stopped.
Embodiment 3
A) the first step is to open water pump 4 import and export valves, opens A pipe, C manage inlet valve, unlatching water pump 4; The most of suction biochemistry pool of sewage, small portion suction tank body 1, C pipe current enter tank body 1 bottom; Tank body 1 middle part is entered in A pipe current tangential; Drive B pipe outlet valve when sewage is filled with tank body 1 soon, water outlet pump 4 inlet pipes that anhydrate are regulated the import and export valve and are guaranteed tank body 1 water-in and water-out balance;
B) second step was evenly to pour starting material nitrobacteria culture promoter or mikrobe into tank body 1 mixing zone; A pipe current tangential drives nitrogenous fertilizer and in water, forms eddy flow and dispersing and dissolving; Drive nitrobacteria culture promoter at welter and dispersing and dissolving on the C pipe current direction, nitrobacteria culture promoter and current bump homodisperse dissolving on three traverse baffles 3 in the tank body 1;
C) the 3rd step was that homodisperse dissolved nitrobacteria culture promoter passes orifice plate 2 through holes with current, was sent to biochemistry pool through the B pipe by water pump 4 at discharge zone.
The utility model installs a kind of dust-trap 5 that adds additional when transporting Powdered Activated Carbon; Comprise water inlet 6, diversion box 7, water curtain spout 8, mix mouth 10, support 11, inverted L shape runner 12; Diversion box 7 is located at the top of said inverted L shape runner 12, the bottom that water curtain spout 8 is located at said diversion box 7; Water inlet 6 be positioned at diversion box 7 the top, mix mouthfuls 10 and be positioned at and the sidewall of inverted L shape runner 12, a chord position 11 is positioned at the bottom of L type runner 12.Water curtain spout 8 is the finedraw of width 2~4mm, totally three roads, and spacing is uniformly distributed with.Water inlet 6 is connected with water pump 4 outlet pipes, and is provided with valve 13, by the emitted dose and the intensity of spray irrigation of valve 13 control water curtain spouts 8.The structure of inverted L shape runner 12 adopts the steel plate welding production of 3.5mm, and its outside surface is coated with the red lead paint twice, and mixing mouthfuls 10 is width 30mm, and the rectangle of length 300mm is divided into three sides of dust-trap 5 ends of falling L.When needs per tour normally added Powdered Activated Carbon, when per hour adding the 200kg Powdered Activated Carbon, step was following:
A) the first step adds dust-trap 5 with Powdered Activated Carbon and connects with throwing device by Fig. 4, regulates tank body 1 water level earlier, makes the mixing mouth 10 of dust-trap 5 be submerged in 50~100mm under tank body 1 liquid level; Again the powder gac bag 9 of opening is put into inverted L shape runner 12; Open valve 13; And through valve 13 adjusting water curtain spouts 8 intensity of spray irrigation; And movable gac bag 9 makes the powder gac evenly pour tank body 1 into through inverted L shape runner 12, and mixes mixing mouthfuls 10, and burgy has fallen fully in will wrapping.
B) second step was that finely dispersed Powdered Activated Carbon passes orifice plate 2 through holes with current, was sent to the biochemistry pool pond through the B pipe by water pump 4 at discharge zone.
C) the 3rd step was successively the Powdered Activated Carbon bag to be put into L type runner 12, repeated above step, after the Powdered Activated Carbon of capacity is squeezed into biochemistry pool, stopped.
A kind of dust-trap 5 that adds is installed in the present invention additional when transporting Powdered Activated Carbon; Comprise water inlet 6, diversion box 7, water curtain spout 8, mix mouth 10, support 11, inverted L shape runner 12; Diversion box 7 is located at the top of said inverted L shape runner 12, the bottom that water curtain spout 8 is located at said diversion box 7; Water inlet 6 be positioned at diversion box 7 the top, mix mouthfuls 10 and be positioned at and the sidewall of inverted L shape runner 12, a chord position 11 is positioned at the bottom of inverted L shape runner 12.Water curtain spout 8 is the finedraw of width 2~4mm, totally three roads, and spacing is uniformly distributed with.Water inlet 6 is connected with water pump 4 outlet pipes, and is provided with valve 13, by the emitted dose and the intensity of spray irrigation of valve 13 control water curtain spouts 8.The structure of inverted L shape runner 12 adopts the steel plate welding production of 3.5mm, and its outside surface is coated with the red lead paint twice, and mixing mouthfuls 10 is width 30mm, and the rectangle of length 300mm is divided into three sides of inverted L shape runner 12 bottoms.
During practical application of the present invention; Powdered Activated Carbon is added dust-trap 5 to be connected with throwing device by Fig. 4; According to the packing measurement of 25Kg packing (pouch) gac bag, the size of corresponding definite dust-trap, and guarantee that the mixing mouth 10 of dust-trap 5 is submerged in 50~100mm under tank body 1 liquid level.
As shown in Figure 4, when the present invention starts, regulate tank body 1 water level earlier, make the mixing mouth 10 of dust-trap 5 be submerged in 50~100mm under tank body 1 liquid level; Again the powder gac bag 9 of opening is put into inverted L shape runner 12; Open valve 13; And through valve 13 adjusting water curtain spouts 8 intensity of spray irrigation; And movable gac bag 9 makes the powder gac evenly pour tank body 1 into through inverted L shape runner 12, and mixes mixing mouthfuls 10, and burgy has fallen fully in will wrapping.
Although in above illustrating, describe the present invention in detail, should be understood that described details only is used to illustrate, those skilled in the art can make change to it in not deviating from spirit that claim of the present invention limits and scope.The reorganization of any simple transformation, step and increase and decrease all belong in protection scope of the present invention.

Claims (8)

1. a raw material wet type throwing device comprises tank body (1), orifice plate (2), traverse baffle (3), water pump (4) and corresponding supporting pipelines, and it is characterized in that: orifice plate (2) is rectangle; The through hole that evenly gathers, orifice plate (2) both sides be vertically welded in tank body (1) inwall vertical on, cylindrical tank (1) is divided into large and small two portions; Major part is named the mixing zone, and small portion is discharge zone, and tank body (1) mixing zone inwall vertically is uniformly distributed with (3) three of traverse baffles; Bottom, tank body (1) mixing zone connects the C pipe, and middle part, tank body (1) mixing zone tangential direction connects the A pipe, and tank body (1) discharge zone bottom connects the B pipe; B pipe water pump (4) inlet pipe, A pipe, C pipe water pump (4) outlet pipe.
2. raw material wet type throwing device according to claim 1; It is characterized in that: described raw material wet type throwing device is installed in a side of biochemistry pool water inlet water pump; Wherein water pump (4) inlet pipe is delivered a child and is produced water reservoir or sewage water reservoir, water pump (4) outlet pipe bifurcation, and one is removed biochemistry pool; One connects A pipe, C pipe and valve (13), B pipe water pump (4) inlet pipe.Its aperture plate (2) goes up through-hole spacing 30mm, aperture φ 10~20mm.
3. raw material wet type throwing device according to claim 1 is characterized in that: the raw material that wherein adds is any one or a few in Powdered Activated Carbon, flour, glucose, microcosmic salt, nitrobacteria culture promoter, the microbial strains.
4. according to the said raw material wet type of claim 1 throwing device, it is characterized in that: (4) outlet pipe that when the raw material that adds is Powdered Activated Carbon, switches off the pump removes biochemical anaerobic pond valve, guarantees that Powdered Activated Carbon goes in the biochemical Aerobic Pond.
5. according to the said raw material wet type of claim 1 throwing device; It is characterized in that: when the raw material that adds is in flour, glucose, microcosmic salt, nitrobacteria culture promoter, the microbial strains any one or a few, select to go biochemical anaerobic pond or Aerobic Pond according to the production needs.
6. according to the said raw material wet type of claim 1 throwing device, it is characterized in that: when the raw material that adds is Powdered Activated Carbon, installs a kind of Powdered Activated Carbon simultaneously additional and add dust-trap (5); It is characterized in that comprise water inlet (6), diversion box (7), water curtain spout (8), mix mouthful (10), a support (11), inverted L shape runner (12), valve (13), diversion box (7) is located at the top of said inverted L shape runner (12), the bottom that water curtain spout (8) is located at said diversion box (7); Water inlet (6) is positioned at the top of diversion box (7); Support (11) is positioned at the bottom of L type runner (12), and water curtain spout (8) is the finedraw of width 2~4mm, totally three roads; Spacing is uniformly distributed with; Water inlet (6) is connected with water pump (4) outlet pipe, is provided with valve (13) therebetween, by the emitted dose and the intensity of spray irrigation of valve (13) control water curtain spout (8); The structure of inverted L shape runner (12) adopts the steel plate welding production of 3.5mm; Its outside surface is coated with the red lead paint twice, and mixing mouthful (10) is the rectangle of width 30mm, length 300mm, is divided into three sides of inverted L shape runner (12) bottom.
7. utilize raw material wet type throwing device according to claim 1 to add the method for plurality of raw materials, it is characterized in that:
A) the first step is to open water pump (4) import and export valve, opens A pipe, C manage inlet valve, unlatching water pump (4); Sewage has in few part sewage shunting suction tank body (1) from sewage pond suction biochemistry pool, and water flows into from tank body (1) bottom in the C pipe; Water flows into from tangential, tank body (1) middle part in the A pipe; When sewage is filled with tank body (1) soon, drive B pipe outlet valve, water outlet pump (4) inlet pipe that anhydrates is regulated the import and export valve and is guaranteed tank body (1) water-in and water-out balance;
B) second step was evenly to pour raw material into tank body (1) mixing zone from container or in the packing bag; A pipe current tangential drives raw material and in water, forms eddy flow and dispersion; Drive raw material in welter and dispersion on the C pipe current direction, interior raw material of tank body (1) and current collision are uniformly dispersed on three traverse baffles (3);
C) the 3rd step was that finely dispersed raw material passes orifice plate (2) through hole with current, was sent to biochemistry pool through the B pipe by water pump (4) at discharge zone.
8. the method that adds plurality of raw materials according to claim 7 is characterized in that when the raw material that adds is Powdered Activated Carbon, installs additional and uses dust-trap (5), and step is following:
A) the first step adds dust-trap (5) with the connection of raw material wet type throwing device with Powdered Activated Carbon, regulates tank body (1) water level earlier, makes the mixing mouth (10) of dust-trap (5) be submerged in 50~100mm under tank body (1) liquid level; Again the powder gac bag (9) of opening is put into inverted L shape runner (12); Open valve (13); And through valve (13) adjusting water curtain spout (8) intensity of spray irrigation; And movable gac bag (9) makes the powder gac evenly pour tank body (1) into through inverted L shape runner (12), and mixes mixing mouthful (10), and burgy has fallen fully in will wrapping;
B) second step was that finely dispersed Powdered Activated Carbon passes orifice plate (2) through hole with current, was sent to biochemistry pool through the B pipe by water pump (4) at discharge zone;
C) the 3rd step was successively the Powdered Activated Carbon bag to be put into L type runner (12), repeated above step, after the Powdered Activated Carbon of capacity is squeezed into biochemistry pool, stopped.
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CN110002586A (en) * 2019-04-19 2019-07-12 中国人民大学 A kind of active carbon addition method and system for municipal sewage plant
CN112566715A (en) * 2019-07-25 2021-03-26 环保视野株式会社 Wastewater treatment apparatus and wastewater treatment method
RU2782590C1 (en) * 2022-06-27 2022-10-31 Владимир Владимирович Володин Plant for the production of liquid fertilizer

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CN110002586A (en) * 2019-04-19 2019-07-12 中国人民大学 A kind of active carbon addition method and system for municipal sewage plant
CN112566715A (en) * 2019-07-25 2021-03-26 环保视野株式会社 Wastewater treatment apparatus and wastewater treatment method
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RU2782590C1 (en) * 2022-06-27 2022-10-31 Владимир Владимирович Володин Plant for the production of liquid fertilizer

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