CN107311395A - A kind of intelligent environment protection toilet MBR film water casees - Google Patents
A kind of intelligent environment protection toilet MBR film water casees Download PDFInfo
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- CN107311395A CN107311395A CN201710598395.3A CN201710598395A CN107311395A CN 107311395 A CN107311395 A CN 107311395A CN 201710598395 A CN201710598395 A CN 201710598395A CN 107311395 A CN107311395 A CN 107311395A
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- slag
- mbp
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- water
- scrape
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F9/00—Multistage treatment of water, waste water or sewage
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/001—Processes for the treatment of water whereby the filtration technique is of importance
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/46—Treatment of water, waste water, or sewage by electrochemical methods
- C02F1/461—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F2001/007—Processes including a sedimentation step
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/005—Black water originating from toilets
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/02—Aerobic processes
- C02F3/12—Activated sludge processes
- C02F3/1236—Particular type of activated sludge installations
- C02F3/1268—Membrane bioreactor systems
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F7/00—Aeration of stretches of water
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- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Separation Using Semi-Permeable Membranes (AREA)
Abstract
A kind of intelligent environment protection toilet disclosed by the invention MBR film water casees, including casing, ramp type slag-scraper, water leg and MBP film devices.Electrolyte after electrolysis enters ramp type slag-scraper, ramp type slag-scraper scrapes off the scum silica frost floated on the surface, the scum silica frost that ramp type slag-scraper is scraped out is delivered in collecting box via scum silica frost discharge end and pipeline and re-starts processing, scrapes treated water in slag bath and enters and is precipitated in sedimentation basin.Water in sedimentation basin, which reaches, enters water leg after certain liquid level, and obtains clear water into progress biomembrane purification filtration treatment in MBP membrane cisternas via water leg.Aeration pump is opened, Air Exposure can be carried out to the water in membrane cisterna.Clear water after the processing of MBP film devices is connected by the clear water reserviors of a pump and casing, and the clear water that processing is obtained is delivered to the clear water reserviors memory storage of casing.The intelligent environment protection toilet MBR film water case automatic runnings of the present invention, without operating personnel's operation, without chemical reagent, you can by electrolyte purify obtaining clear water.
Description
Technical field
The present invention relates to stool detection technical field, more particularly to a kind of intelligent environment protection toilet MBR film water casees.
Background technology
Population increase and high concentration is so that the yield of urban night soil is continuously increased, these excrement are in past most conduct
Fertilizer directly transports rural area to, and at present in the case where that can bring the impact of chemical fertilizer of distinct economic, excrement makes rural area
Consumption increasingly atrophy.Thus, excrement is managed and handled using suitable technology, not only has great to environmental protection
Meaning, and to ensureing that the health of the people also has profound significance.
Excrement and urine water mainly has high suspended particulate substance (SS), ammonia nitrogen (NH3-N) concentration height, organic matter (COD) concentration is high, feel
The features such as official's degree is poor, biodegradability is good.Have at present for the main treatment technology of excrement and urine water：It is anaerobic fermentation facture, aerobic
Facture, high temperature high pressure process method, septic tank facture, materialization treatment process, During High-Temperature Composting method etc., but the country is in reality at present
The stool detection technology being most widely used in engineering is broadly divided into two classes：
One class：Septic tank processing:In small and medium-sized cities and rural area due to the processing of sanitary sewage, collecting dung, processing are complete
Pipelineization is relatively difficult, and small-sized septic tank just turns into the facility that apartment is most universal and must configure.The function of septic tank is
Receive, store family domestic sewage.It is divided into floating layer, mud and middle 3 region of clear water layer in pond.Clear water can use sewage
The mode of irrigation makees final process.Current widely using due to chemical products, the composition of family domestic sewage is increasingly sophisticated, dirty
Harmful substance contents increase in water, the direct discharge of septic tank " clear water layer " just turns into the pollution sources in sewage irrigation region.To this
The control for planting pollution is only to decompose to precipitate harmful substance using a large amount of chemicalses in septic tank, but is filled expanding sewage
Region is irrigate, increase soil treatment is functionally to be difficult to effectively.While septic tank processing is also easy to, appearance is blocked, spoil disposal is difficult,
Handle the problems such as thorough, mosquitos and flies does not grow.
Two classes：Materializing strategy:It is 200710079587 in China Patent No..X, publication date are September in 2007 19 days, title
A kind of method of materializing strategy excrement disclosed in patent document for " dejecta treatment method and system ".This method is to pass through solid-liquid
Excrement is carried out separation of solid and liquid by separation equipment, and the residue isolated carries out landfill disposal, and the liquid manure isolated adds appropriate chemistry
Medicament, makes liquid manure occur by dehydration equipment progress dewater treatment after flocculation, wherein dry clay as fertile obtained by dehydration
Material, liquid deliver to sewage treatment plant and carry out terminal processes.The dejecta treatment method of above pattern has the following disadvantages：For highly concentrated
Spend being received for organic fecal sewage, it is desirable to which the condition such as designed capacity, operating mode of sewage treatment plant meets by receiving the standard of sewage, and
Fecal sewage is that randomness is discharged into sewage network, and the construction plan to sewage treatment plant brings very big inconvenience；Fecal sewage is defeated
Dense stink can be given out and be difficult to handle stink by being sent in the way of sewage treatment plant, be unfavorable for environmental sanitation.
In order to solve the not enough above of above type of dejecta treatment method, it have devised to liquid dung produced after dehydration
It is further processed to reach the stool detection method discharged again after discharge mark.It is in Chinese Patent Application No.
201210251613.3rd, publication date is on October 24th, 2012, entitled " a kind of decontamination of human excreta recycling processing method "
Switched in patent document it is a kind of can be by the method for the liquid waste processing in excrement to qualified discharge.This method is gained after being dehydrated
Waste liquid carry out gathering chelation treatment and oxygen processing successively and one-level/bis- grade Aerobic Process for Treatment is discharged afterwards to up to standard.The type
Processing method have the following disadvantages：Directly waste liquid is carried out successively to gather chelation treatment and oxygen processing and one-level/bis- grade are aerobic
Handle it is up to standard after discharged, the processing method causes the organic matter for making nutrient in liquid dung to be decomposed into can not be as nutrient
Organic matter, it is impossible to realize abundant recycling to the organic matter in excrement and nitrogen treatment not thoroughly, COD removal efficiency
It is low；The dewater treatment of sludge and excrement is carried out together by same centrifuge, the reasonable utilization for the nutrient being not easy in excrement, because
For excrement be dehydrated obtained by dry mud nutrient it is high, can be used as fertilizer and be used, and the dry mud obtained by sludge dewatering does not almost have
What nutrient is improper as fertilizer utilization.
For the deficiency of above-mentioned technology, Chinese patent Authorization Notice No. CN103073149B discloses a kind of decontamination of human excreta
Processing method, it is handled excrement in accordance with the following steps：
1st step, by solid-liquid separating machine to excrement carry out separation of solid and liquid；
It is dehydrated after 2nd step, the liquid flocculation for isolating the 1st step by centrifuge；
3rd step, by the liquid isolated in the 2nd step in anaerobic digester by the effect of anaerobe, make waste water
In organic matter decomposition and inversion turn into after methane and carbon dioxide mud-water separation carried out by the method for precipitation；
4th step, by the liquid isolated in the 3rd step carry out denitrogenation processing；
Denitrogenation processing comprises the following steps：
4-1 is walked, is adjusted the pH value for the liquid isolated in the 3rd step to 9.5~12；
4-2 is walked, the method that the liquid produced in 4-1 steps is taken off by air-blowing is made into the free ammonia volatilization in liquid, so
The ammonia volatilized is absorbed with acid solution afterwards and ammonium salt is generated；
4-3 is walked, the liquid after walking denitrogenation through 4-2 is carried out into neutralisation treatment, by pH value regulation to 7.5~8.5；
5th step, the liquid after the 4th step denitrogenation processing is subjected to degraded COD, BOD and ammonia nitrogen；
5-1 step, by the liquid after the 4th step denitrogenation be transported in one-level anoxic pond handle after be transported to one-level Aerobic Pond again
It is middle to be handled；Anaerobic bacteria in one-level anoxic pond makes the larger molecular organicses in liquid be degraded to small organic molecule, anti-
Nitrobacteria is carried out instead using the organic matter in liquid for the mixed liquor containing nitrate nitrogen flowed back in carbon source and one-level Aerobic Pond
Nitration reaction, nitrogen is converted into by the nitrate nitrogen in water；Aerobic bacteria in one-level Aerobic Pond is under Effect of Dissolved Oxygen by liquid
Middle organic matter, which absorbs, to be decomposed, and is converted into CO2 and itself organic matter, and Simultaneous Nitrification bacterium is also by the ammonium oxidation in water into nitre state
Nitrogen；
5-2 steps, the liquid after the processing of one-level Aerobic Pond are transported to after being handled in two grades of anoxic ponds is transported to two grades again
Handled in Aerobic Pond；It is organic that anaerobic bacteria in two grades of anoxic ponds makes the larger molecular organicses in liquid be degraded to small molecule
Thing, denitrifying bacteria are entered using the organic matter in liquid for the mixed liquor containing nitrate nitrogen flowed back in carbon source and two grades of Aerobic Ponds
Row anti-nitration reaction, nitrogen is converted into by the nitrate nitrogen in water；Aerobic bacteria in two grades of Aerobic Ponds will under Effect of Dissolved Oxygen
Organic matter, which absorbs, in liquid decomposes, and is converted into CO2 and itself organic matter, Simultaneous Nitrification bacterium also by the ammonium oxidation in water into
Nitrate nitrogen；Liquid after two grades of Aerobic Pond processing, which is transported in the 6th step, to be handled.
6th step, the method progress mud-water separation that the liquid after being handled through the 5th step is passed through into precipitation；
7th step, the liquid for isolating the 6th step carry out disinfection processing after discharge.
8th step, the sludge dewatering in dewater treatment, the 8th step and the 2nd step are carried out by the sludge produced in the 3rd step and the 6th step
In the dehydrate liquids for isolating the 1st step separately carry out.
The core of the patent and be to carry out denitrogenation processing to ammonia nitrogen by stripping method a little, denitrogenation processing efficiency high enters
Enter to carry out degraded COD, BOD and ammonia nitrogen so that CODCr≤450mg/L in the waste water of discharge, SS≤350mg/L, BOD5≤
250mg/L, NH3-N≤28mg/L；Discharge before disinfected, make pathogen therein, parasitic ovum and fly maggot go out extremely,
Reach harmless in health；Methane and ammonium salt will be isolated in excrement in processing, the utilization to the organic matter in excrement is abundant.But
The shortcoming for being the patent is that the operation of whole system needs operating personnel's control, additionally needs and delivers some chemical reagent, once
Chemical reagent is delivered excessively, is made troubles to subsequent treatment.
For many technical problems present in above-mentioned stool detection, the applicant is by beneficial exploration and grinds
Study carefully, have developed a kind of automatic operating, the intelligent environment protection toilet of chemical reagent need not be delivered without emissions and recycled certainly
Dynamicization processing system, the automated programming system carries out separation of solid and liquid, the liquid that will be obtained after separation to excrement solid-liquid mixture
Mixture is electrolysed, then obtains clear water to electrolyte progress purified treatment.It is how right in the case where not delivering chemical reagent
Electrolyte carries out purified treatment and obtains the technical barrier that clear water is this area urgent need to resolve, and the present invention is to produce under this background
Raw.
The content of the invention
It is an object of the invention to provide a kind of MBR film water casees of intelligent environment protection toilet, the MBR film waters case is without throwing
Purified treatment is carried out to electrolyte in the case of putting chemical reagent and obtains clear water.
The technical problems to be solved by the invention can be realized by following technical solution：
A kind of intelligent environment protection toilet MBR film water casees, including：
One first demarcation strip and the second demarcation strip, described are arranged at intervals with one casing, the casing along its length
The box house is separated into first chamber, second chamber and the 3rd chamber by one demarcation strip and the second demarcation strip, in the case
One the 3rd demarcation strip is additionally provided with 3rd chamber of body, the 3rd chamber of the casing is separated into by the 3rd demarcation strip
Four chambers and the 5th chamber, the first chamber is scrapes slag bath, and the second chamber is sedimentation basin, and the 4th chamber is MBP
Membrane cisterna, the 5th chamber is clear water reserviors；Offer leak in the bottom of first demarcation strip, offered on the casing one with
The electrolyte inlet and one for scraping slag bath connection scrapes the scum silica frost discharging opening that slag bath is connected with described；
One be arranged on the casing scrape in slag bath be used for by the electrolyte upper strata scum silica frost after electrolysis strike off it is oblique
Board-like slag-scraper, the ramp type slag-scraper has an electrolyte liquid feeding end and a scum silica frost discharge end, and the ramp type is scraped
The electrolyte liquid feeding end of slag device is connected with the electrolyte inlet on the casing, on its scum silica frost discharge end and the casing
Scum silica frost discharging opening is connected；
One is horizontally set on the water leg on the top of the sedimentation basin of the casing, and one end of the water leg is connected to described
The top of first demarcation strip, its other end is connected to the top of second demarcation strip and connected with the MBP membrane cisternas；With
And
One is arranged on being used for the electrolyte progress biomembrane purification mistake after precipitation in the MBP membrane cisternas of the casing
Filter obtains the MBP film devices of clear water, and the MBP film devices have a clear water flow export, the clear water flow export of the MBP film devices
It is connected by a pump with the clear water reserviors of the casing, the clear water that processing is obtained is delivered to the clear water reserviors memory storage of the casing.
In a preferred embodiment of the invention, the ramp type slag-scraper includes：
One scrapes slag cylinder, and the sidepiece for scraping slag cylinder offers one and scrapes slag leak；
One, which is arranged on the arc scraped in slag cylinder, scrapes slag bushing, the arc scrape slag bushing with one scrape slag import and
One scrapes slag outlet, and the slag outlet of scraping that the arc scrapes slag bushing is connected with the slag leak of scraping for scraping slag cylinder；
One is arranged on the feed liquor funnel scraped in slag cylinder, and the upper surface periphery of the feed liquor funnel does not scrape slag with described
The inner cylinder face contact of cylinder, the lower end outlet of the feed liquor funnel is connected with a feed liquor connecting tube, and the feed liquor connecting tube is entered
Mouthful as the ramp type slag-scraper electrolyte liquid feeding end；
One is arranged on described scrape scrapes slag cover plate on the top surface of slag cylinder；
One be arranged on it is described scrape on slag cover plate scrape slag motor, the output end for scraping slag motor scrapes slag cover plate through described
After extend into described scrape in slag cylinder；
One, which is located at described scrape in slag cylinder, scrapes slag piece, and the center for scraping slag piece is extended into the slag motor of scraping
The output end connection scraped in slag cylinder；And
One be fixedly mounted on it is described scrape on slag cylinder scrape slag swash plate, the feed end for scraping slag swash plate, which is located at, described scrapes slag
The lower section for scraping slag leak of cylinder, its discharge end is extended obliquely downward and discharged as the scum silica frost of the ramp type slag-scraper
End.
In a preferred embodiment of the invention, the MBP film devices include：
The first, second MBP film installation side plates that relative spacing is set, the first MBP films installation side plate is towards described the
Some the first vertically extending plugboard troughs are arranged at intervals with the plate face of two MBP film installation side plates, the 2nd MBP films are installed
Side plate is some vertically extending and with described some first towards being arranged at intervals with the plate face of the first MBP film installation side plates
Plugboard trough is in the second plugboard trough of one-to-one relationship；
Some MBP diaphragm plates being arranged between the first, second MBP film installation side plates, the both sides point of the MBP diaphragm plates
There is a filtering in first, second plugboard trough for not being inserted into the first, second MBP film installation side plates, on the MBP diaphragm plates
Liquid is exported；
It is separately positioned on first, second collector pipe in the first, second MBP installation side plates, first, second collection
Filtrate outlet of the inlet of water pipe accordingly with the MBP diaphragm plates is connected, and the delivery port of first, second collector pipe converges
The clear water flow export of the MBP film devices is used as after collection；
The aeration tube of some bottoms for being disposed on the first, second MBP film installation side plates, the one of the aeration tube
Hold as inlet end, the closing of its other end；And
One aeration pump, the inlet end of the outlet side of the aeration pump by pipeline respectively with each aeration tube is connected.
In a preferred embodiment of the invention, be located on the casing bottom for scraping slag bath offer one with
First sewage draining exit for scraping slag bath connection, the bottom positioned at the sedimentation basin on the casing offers one and the precipitation
Second sewage draining exit of pond connection, the bottom positioned at the MBP membrane cisternas on the casing offers one and connected with the MBP membrane cisternas
The 3rd sewage draining exit.
In a preferred embodiment of the invention, the bottom for scraping slag bath is located in the casing and is provided with one the
It is axially spaced in one flush pipe, first flush pipe to offer some first flushing holes, the water inlet of first flush pipe
Mouth is connected by the first connecting tube with outside water supply installation.
In a preferred embodiment of the invention, the bottom of the sedimentation basin is provided with one the in the casing
It is axially spaced in two flush pipes, second flush pipe to offer some second flushing holes, the water inlet of second flush pipe
Mouth is connected by the second connecting tube with outside water supply installation.
As a result of technical scheme as above, intelligent environment protection toilet MBR film water case automatic runnings of the invention, without
Operating personnel operate, without chemical reagent, you can by electrolyte purify obtaining clear water.
Brief description of the drawings
Fig. 1 is the structural representation of intelligent environment protection toilet of the present invention MBR film water casees.
Fig. 2 is the structural representation of the ramp type slag-scraper of the present invention.
Fig. 3 is the structural representation of the MBP film devices of the present invention.
Embodiment
Referring to Fig. 1, what is provided in figure is a kind of intelligent environment protection toilet MBR film water casees, including casing 100, ramp type are scraped
Slag device 200, water leg 300 and MBP film devices 400.
One first demarcation strip 110 and the second demarcation strip 120 are arranged at intervals with casing 100 along its length, first separates
The demarcation strip 120 of plate 110 and second will be separated into first chamber, second chamber and the 3rd chamber inside casing 100, in casing 100
The 3rd chamber in be additionally provided with one the 3rd demarcation strip 130, the 3rd chamber of casing 100 is separated into by the 3rd demarcation strip 130
Four chambers and the 5th chamber, wherein, first chamber is scrapes slag bath 101, and second chamber is sedimentation basin 102, and the 4th chamber is MBP films
Pond 103, the 5th chamber is clear water reserviors 104.Leak 111 is offered in the bottom of the first demarcation strip 110, is opened up on casing 100
Have one with scraping electrolyte inlet 140 and one that slag bath 101 connects with scraping the scum silica frost discharging opening 150 that slag bath 101 is connected.
What ramp type slag-scraper 200 was arranged on casing 100 scrapes being used for the electrolyte after electrolysis in slag bath 101
Upper strata scum silica frost strikes off.Referring to Fig. 2 and Fig. 1 is combined, ramp type slag-scraper 200, which includes scraping slag cylinder 210, arc, scrapes slag bushing
220th, feed liquor funnel 230, scrape slag cover plate 240, scrape slag motor 250, scrape slag piece 260, scrape slag swash plate 270.
Scrape slag cylinder 210 scraping in slag bath 101 installed in casing 100, the sidepiece for scraping slag cylinder 210 offers one and scrapes slag leakage
Mouth 211.Arc, which is scraped slag bushing 220 and is arranged on, to be scraped in slag cylinder 210, and arc scrapes slag bushing 220 and scrapes slag import 221 and one with one
Slag outlet 222 is scraped, the slag outlet 222 of scraping that arc scrapes slag bushing 220 is connected with scraping the slag leak 211 of scraping of slag cylinder 210.Feed liquor leaks
Bucket 230, which is arranged on, to be scraped in slag cylinder 210, and the upper surface periphery of feed liquor funnel 230 is not contacted with scraping the inner cylinder face of slag cylinder 210,
The lower end outlet of feed liquor funnel 230 is connected with a feed liquor connecting tube 280, and the import of feed liquor connecting tube 280 scrapes slag as ramp type
The electrolyte liquid feeding end 201 of device 200, it is connected with the electrolyte inlet 140 on casing 100.Slag cover plate 240 is scraped to be arranged on
On the top surface for scraping slag cylinder 210.Scrape slag motor 250 and be arranged on and scrape on slag cover plate 240, scrape the output end of slag motor 250 through scraping
Extend into and scraped in slag cylinder 210 after slag cover plate 240.Slag piece 260 is scraped positioned at scraping in slag cylinder 210, the center of slag piece 260 is scraped
Extend into scraping slag motor 250 and scrape the output end in slag cylinder 210 and be connected.Scrape slag swash plate 270 and be fixedly mounted on and scrape slag cylinder 210
On, the feed end for scraping slag swash plate 270 is located at the lower section for scraping slag leak 211 for scraping slag cylinder 210, and its discharge end is extended obliquely downward
And as the scum silica frost discharge end 202 of ramp type slag-scraper 200, it is connected with the scum silica frost discharging opening 150 on casing 100.
Water leg 300 is horizontally set on the water leg on the top of the sedimentation basin of the casing, and one end of the water leg connects
The top of first demarcation strip is connected on, its other end is connected to the top of second demarcation strip and connected with the MBP membrane cisternas
It is logical；And
MBP film devices 400 are arranged on being used for the electrolyte progress after precipitation in the MBP membrane cisternas 103 of casing 100
Biomembrane purification is filtrated to get clear water.Referring to Fig. 3 and Fig. 1 is combined, MBP film devices 400 include first, second MBP film installation sides
Plate 410,420, some MBP diaphragm plates 430, first, second collector pipe 440,450, some aeration tubes 460 and aeration pump are (in figure
It is not shown).
First, second MBP films installation side plate 410,420 relative spacings are arranged in the MBP membrane cisternas 103 of casing 100.First
MBP films installation side plate 410 is towards being arranged at intervals with some vertically extending in the plate face of the 2nd MBP films installation side plate 420
One plugboard trough 411, if the 2nd MBP films installation side plate 420 is towards being arranged at intervals with the plate face of the first MBP films installation side plate 410
The second plugboard trough 421 that is dry vertically extending and with some first plugboard troughs 411 being in one-to-one relationship.Some MBP films
Plate 430 is arranged between first, second MBP films installation side plate 410,420, the both sides of MBP diaphragm plates 430 are inserted into first respectively,
In first, second plugboard trough 411,421 of the 2nd MBP films installation side plate 410,420, on MBP diaphragm plates 430 there is a filtered fluid to go out
Mouth (not shown).First, second collector pipe 440,450 is separately positioned on first, second MBP films installation side plate 410,420
On, the filtrate outlet of the inlet of first, second collector pipe 440,450 accordingly with MBP diaphragm plates 430 is connected, and first, second
The delivery port of collector pipe 440,450 collect after as MBP film devices 400 clear water flow export, it passes through a pump and casing 100
Clear water reserviors 104 are connected, and the clear water that processing is obtained is delivered to the memory storage of clear water reserviors 104 of casing 100.Between some aeration tubes 460
Every the bottom for being arranged on first, second MBP films installation side plate 410,420, one end of aeration tube 460 is inlet end, its other end
Closing.Inlet end of the outlet side of aeration pump by pipeline 470 respectively with each aeration tube 460 is connected.
For the ease of intelligent environment protection toilet with MBR film water case blowdowns the need for, on casing 100 be located at scrape slag bath 101
Bottom offers one with scraping the first sewage draining exit 161 that slag bath 101 is connected, and the bottom positioned at sedimentation basin 102 on casing 100 is opened up
Have second sewage draining exit 162 connected with sedimentation basin 102, on casing 100 positioned at MBP membrane cisternas 103 bottom offer one with
The 3rd sewage draining exit 163 that MBP membrane cisternas 103 are connected.
For the ease of the cleaning of scraping slag bath 101 bottom of the intelligent environment protection toilet with MBR film water casees, it is located in casing 100
The bottom for scraping slag bath 101 is provided with and axially spaced in one first flush pipe 171, the first flush pipe 171 offers some first
Flushing hole (not shown), the water inlet of the first flush pipe 171 is connected by the first connecting tube 171a with outside water supply installation
Connect.
For the ease of cleaning of the intelligent environment protection toilet with the bottom of sedimentation basin 102 of MBR film water casees, it is located in casing 100
The bottom of sedimentation basin 102, which is provided with, axially spaced in one second flush pipe 172, the second flush pipe 172 offers some second
Flushing hole (not shown), the water inlet of the second flush pipe 172 is connected by the second connecting tube 172a with outside water supply installation
Connect.
The intelligent environment protection toilet of the present invention is as follows with the course of work of MBR film water casees：
The ramp type that electrolyte after electrolysis enters in casing from the electrolyte inlet 110 of casing 100 scrapes slag dress
200 are put, ramp type slag-scraper 200 scrapes off the scum silica frost floated on the surface, in order to avoid flow to sedimentation basin 102 and MBP membrane cisternas 103
In.The scum silica frost that ramp type slag-scraper 200 is scraped out is delivered in collecting box via scum silica frost discharge end 202 and pipeline and re-starts place
Reason.Scrape the sediment in slag bath 220 and be sent to by the first sewage draining exit 161 and pipeline in collecting box and re-start processing.Scrape slag bath
The leak that treated water in 101 is opened up by the bottom of the first demarcation strip 110 enters to be precipitated in sedimentation basin 102.
Water in sedimentation basin 102, which reaches, enters water leg 300 after certain liquid level, and enters MBP films via water leg 300
Biomembrane purification filtration treatment is carried out in pond 103 and obtains clear water.Sediment in sedimentation basin 102 passes through the row of the second sewage draining exit 162
Go out.
Aeration pump is opened, Air Exposure can be carried out to the water in MBP membrane cisternas 103.Precipitating sludge in MBP membrane cisternas 103
Discharged by the 3rd sewage draining exit 163.Clear water after the processing of MBP film devices 400 is connected by the clear water reserviors 104 of a pump and casing 100
Connect, the clear water that processing is obtained is delivered to the memory storage of clear water reserviors 104 of casing 100.
Claims (6)
1. a kind of intelligent environment protection toilet MBR film water casees, it is characterised in that including：
One first demarcation strip and the second demarcation strip, described first point are arranged at intervals with one casing, the casing along its length
The box house is separated into first chamber, second chamber and the 3rd chamber by dividing plate and the second demarcation strip, in the casing
One the 3rd demarcation strip is additionally provided with 3rd chamber, the 3rd chamber of the casing is separated into the 4th chamber by the 3rd demarcation strip
Room and the 5th chamber, the first chamber is scrapes slag bath, and the second chamber is sedimentation basin, and the 4th chamber is MBP membrane cisternas,
5th chamber is clear water reserviors；Offer leak in the bottom of first demarcation strip, offered on the casing one with it is described
The electrolyte inlet and one for scraping slag bath connection scrapes the scum silica frost discharging opening that slag bath is connected with described；
One be arranged on the casing scrape in slag bath for the ramp type that strikes off the electrolyte upper strata scum silica frost after electrolysis
Slag-scraper, the ramp type slag-scraper has an electrolyte liquid feeding end and a scum silica frost discharge end, and the ramp type scrapes slag dress
The electrolyte liquid feeding end put is connected with the electrolyte inlet on the casing, its scum silica frost discharge end and the scum silica frost on the casing
Discharging opening is connected；
One is horizontally set on the water leg on the top of the sedimentation basin of the casing, and one end of the water leg is connected to described first
The top of demarcation strip, its other end is connected to the top of second demarcation strip and connected with the MBP membrane cisternas；And
One is arranged on being filtered for carrying out biomembrane purification to the electrolyte after precipitation in the MBP membrane cisternas of the casing
To the MBP film devices of clear water, the MBP film devices have a clear water flow export, and the clear water flow export of the MBP film devices passes through
One pump is connected with the clear water reserviors of the casing, and the clear water that processing is obtained is delivered to the clear water reserviors memory storage of the casing.
2. intelligent environment protection toilet as claimed in claim 1 MBR film water casees, it is characterised in that the ramp type slag-scraper
Including：
One scrapes slag cylinder, and the sidepiece for scraping slag cylinder offers one and scrapes slag leak；
One, which is arranged on the arc scraped in slag cylinder, scrapes slag bushing, and the arc, which scrapes slag bushing and scrapes slag import and one with one, to be scraped
Slag is exported, and the slag outlet of scraping that the arc scrapes slag bushing is connected with the slag leak of scraping for scraping slag cylinder；
One is arranged on the feed liquor funnel scraped in slag cylinder, and the upper surface periphery of the feed liquor funnel does not scrape slag cylinder with described
The contact of inner cylinder face, the lower end outlet of the feed liquor funnel is connected with a feed liquor connecting tube, and the import of the feed liquor connecting tube is made
For the electrolyte liquid feeding end of the ramp type slag-scraper；
One is arranged on described scrape scrapes slag cover plate on the top surface of slag cylinder；
One be arranged on it is described scrape on slag cover plate scrape slag motor, the output end for scraping slag motor through it is described scrape slag cover plate after prolong
Stretch into described scrape in slag cylinder；
One be located at it is described scrape in slag cylinder scrape slag piece, the center for scraping slag piece with it is described scrape slag motor extend into it is described
Scrape the output end connection in slag cylinder；And
One be fixedly mounted on it is described scrape on slag cylinder scrape slag swash plate, the feed end for scraping slag swash plate, which is located at, described scrapes slag cylinder
The lower section for scraping slag leak, its discharge end extends obliquely downward and as the scum silica frost discharge end of the ramp type slag-scraper.
3. intelligent environment protection toilet as claimed in claim 1 MBR film water casees, it is characterised in that the MBP film devices include：
The first, second MBP film installation side plates that relative spacing is set, the first MBP films installation side plate is towards the 2nd MBP
Some the first vertically extending plugboard troughs, the 2nd MBP film installation side plates are arranged at intervals with the plate face of film installation side plate
Be arranged at intervals with towards the plate face of the first MBP film installation side plates it is some vertically extending and with some first plates
Groove is in the second plugboard trough of one-to-one relationship；
Some MBP diaphragm plates being arranged between the first, second MBP film installation side plates, the both sides of the MBP diaphragm plates are inserted respectively
In first, second plugboard trough of the first, second MBP film installation side plates, on the MBP diaphragm plates there is a filtered fluid to go out
Mouthful；
It is separately positioned on first, second collector pipe in the first, second MBP installation side plates, first, second collector pipe
Filtrate outlet of the inlet accordingly with the MBP diaphragm plates be connected, after the delivery port of first, second collector pipe collects
It is used as the clear water flow export of the MBP film devices；
The aeration tube of some bottoms for being disposed on the first, second MBP film installation side plates, one end of the aeration tube is
Inlet end, the closing of its other end；And
One aeration pump, the inlet end of the outlet side of the aeration pump by pipeline respectively with each aeration tube is connected.
4. intelligent environment protection toilet as claimed in claim 1 MBR film water casees, it is characterised in that be located at institute on the casing
State and scrape the bottom of slag bath and offer one and scrape the first sewage draining exit that slag bath is connected with described, the sedimentation basin is located on the casing
Bottom offer second sewage draining exit connected with the sedimentation basin, on the casing be located at the MBP membrane cisternas bottom
Offer the 3rd sewage draining exit connected with the MBP membrane cisternas.
5. intelligent environment protection toilet as claimed in claim 1 MBR film water casees, it is characterised in that be located at institute in the casing
State scrape slag bath bottom be provided with one first flush pipe, first flush pipe it is axially spaced offer it is some first bath
Hole, the water inlet of first flush pipe is connected by the first connecting tube with outside water supply installation.
6. intelligent environment protection toilet as claimed in claim 1 MBR film water casees, it is characterised in that be located at institute in the casing
State sedimentation basin bottom be provided with one second flush pipe, second flush pipe it is axially spaced offer it is some second bath
Hole, the water inlet of second flush pipe is connected by the second connecting tube with outside water supply installation.
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| Application Number | Priority Date | Filing Date | Title |
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| CN201710598395.3A CN107311395A (en) | 2017-07-21 | 2017-07-21 | A kind of intelligent environment protection toilet MBR film water casees |
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| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201710598395.3A CN107311395A (en) | 2017-07-21 | 2017-07-21 | A kind of intelligent environment protection toilet MBR film water casees |
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| Publication Number | Publication Date |
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| CN107311395A true CN107311395A (en) | 2017-11-03 |
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| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201710598395.3A Pending CN107311395A (en) | 2017-07-21 | 2017-07-21 | A kind of intelligent environment protection toilet MBR film water casees |
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| Publication number | Priority date | Publication date | Assignee | Title |
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| CN108947138A (en) * | 2018-08-08 | 2018-12-07 | 张家港市欧微自动化研发有限公司 | A kind of sewage disposal device |
| CN108975618A (en) * | 2018-08-08 | 2018-12-11 | 张家港市欧微自动化研发有限公司 | A kind of sewage water treatment method based on sewage disposal device |
| CN110255771A (en) * | 2019-07-03 | 2019-09-20 | 东莞市宇科机械科技有限公司 | A kind of urban road sewage treatment deodorizing device and its working method |
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| CN2603138Y (en) * | 2003-03-06 | 2004-02-11 | 株式会社关电制作所 | Circular flushing type environment protection closet |
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| CN104402177A (en) * | 2014-12-27 | 2015-03-11 | 温州泓呈祥科技有限公司 | Community domestic sewage treatment system |
| CN106746380A (en) * | 2017-03-16 | 2017-05-31 | 李明 | A kind of Internet of Things remote monitoring and administration bio-toilet and its changing rejected material to useful resource method |
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| Publication number | Priority date | Publication date | Assignee | Title |
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| CN2603138Y (en) * | 2003-03-06 | 2004-02-11 | 株式会社关电制作所 | Circular flushing type environment protection closet |
| CN103073149A (en) * | 2012-12-05 | 2013-05-01 | 浙江省环境工程有限公司 | Harmless processing method of night soil |
| CN104402177A (en) * | 2014-12-27 | 2015-03-11 | 温州泓呈祥科技有限公司 | Community domestic sewage treatment system |
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| Publication number | Priority date | Publication date | Assignee | Title |
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| CN108947138A (en) * | 2018-08-08 | 2018-12-07 | 张家港市欧微自动化研发有限公司 | A kind of sewage disposal device |
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| CN110255771A (en) * | 2019-07-03 | 2019-09-20 | 东莞市宇科机械科技有限公司 | A kind of urban road sewage treatment deodorizing device and its working method |
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