CN104249074A - Washing kitchen waste disposal system - Google Patents

Washing kitchen waste disposal system Download PDF

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Publication number
CN104249074A
CN104249074A CN201310265471.0A CN201310265471A CN104249074A CN 104249074 A CN104249074 A CN 104249074A CN 201310265471 A CN201310265471 A CN 201310265471A CN 104249074 A CN104249074 A CN 104249074A
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treatment
treatment system
aerobic process
outlet side
restaurant garbage
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CN104249074B (en
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维林加·索德·哈伯斯·约瑟夫
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PAQUES ENVIRONMENTAL TECHNOLOGY (SHANGHAI) Co Ltd
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PAQUES ENVIRONMENTAL TECHNOLOGY (SHANGHAI) Co Ltd
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Abstract

The washing kitchen waste disposal system solves the technical problems of large water content, various impurities and bad disposal effect of kitchen waste mainly being residues after meals due to the unique food culture of China in the prior art. The invention relates to a washing kitchen waste disposal system which comprises a pre-disposal system, an anaerobic treatment system, an aerobic treatment system, a deep treatment system, a biogas treatment system, a sludge treatment system, an exhaust-gas treatment system and a chemical dispensing system for processing, and the washing kitchen waste disposal system has good treatment effect.

Description

Washing restaurant garbage treating system
Technical field
The present invention relates to a kind of restaurant garbage treating system, particularly relate to a kind of washing restaurant garbage treating system.
Background technology
Changing food waste process is an emerging environmental protection proposition in China's Mainland, and after the waste oil major case detection transprovincially in the shock whole nation in 2011, country starts management and the disposal of paying much attention to changing food waste.
On August 2nd, 2011, National Development and Reform Committee, the Ministry of Finance, the firmly portion of building announce, recycling economy development special fund 6.3 hundred million yuan will be arranged, support that 33 pilot cities (district) in the whole nation carry out kitchen castoff recycling and harmless treatment, " outlet " of exploring changing food waste for various places provides experience and reference.
Should, within 2011, be the memorable milestone of Chinese meal kitchen garbage disposal, bugle is blowed at this.And within 2012, will be an open arena, the participation of global various state-of-the-art technology the garbage disposal of Chinese meal kitchen will advance a new height.
Before this, the garbage disposal of Chinese meal kitchen is in under-capitalization, communal participation is not enough, cause the immature state that level is low, problem is many, and the dining and drinking culture of China's uniqueness creates the distinct changing food waste character with west, this Chinese changing food waste water content based on residue is after the meal large, impurity is various, and also not external maturation and successful experience can directly be used.
Only with pretreatment, dirty, unrest, difference are that Present Domestic is at the basal conditions of the changing food waste factory run, this technique based on dry-type separation not only site environment very severe, stench fills the air, disgusting, and there is the huge potential safety hazard such as hydrogen explosion, hydrogen sulfide poisoning.Under this working environment, it is also deeply influenced that artificial separation quality of workers is difficult to raising, and the result caused is that sharpness of separation is poor: Organic Matter Loss is many, also impure many in follow-up slurry, chain reaction causes scum silica frost sand setting in subsequent anaerobic digestion tank many, has a strong impact on lasting operation.
Summary of the invention
The invention discloses a kind of washing restaurant garbage treating system, in order to solve Chinese unique cooking culture in prior art based on the changing food waste water content of residue after the meal greatly, impurity is various, the technical problem that treatment effect is very undesirable.
Above-mentioned purpose of the present invention is achieved through the following technical solutions:
A kind of washing restaurant garbage treating system, comprising:
One pretreatment system, in order to remove the organic matter in changing food waste, described pretreatment system specifically comprises an impurity removing unit, an oil removing unit and a pulverizing unit, wherein, also comprises and setting gradually:
One system for anaerobic treatment;
One Aerobic Process for Treatment system, in order to remove biodegradable organic pollution further; Described Aerobic Process for Treatment system specifically comprises: a dephosphorizing reactor, in order to remove phosphorus and to reduce the situation occurring guanite in follow-up system; One short-cut denitrification reactor, in order to carry out denitrogenation processing to waste water;
One exhaust treatment system, described exhaust treatment system specifically comprises: an activated sludge scrubbing tower, in order to remove residual activity pollutant; One advanced treatment system, in order to remove COD and TSS of part difficult for biological degradation further.
Restaurant garbage treating system as above, wherein, the waste material outlet side of described advanced treatment system is connected with treatment system with described.
Restaurant garbage treating system as above, wherein, the charging aperture of described Aerobic Process for Treatment system is connected with the waste water outlet side of described system for anaerobic treatment, and described Aerobic Process for Treatment system has a water side.
Restaurant garbage treating system as above, wherein, described Aerobic Process for Treatment system also has a waste gas outlet side, and described exhaust treatment system is connected with the waste gas outlet side of described Aerobic Process for Treatment system.
Restaurant garbage treating system as above, wherein, described pretreatment system has a changing food waste feed end and a changing food waste discharge end, the changing food waste discharge end of described pretreatment system is connected with the charging aperture of described system for anaerobic treatment, and described system for anaerobic treatment has a biogas outlet side and a waste water outlet side.
Restaurant garbage treating system as above, wherein, also comprises: a sludge treating system, and described system for anaerobic treatment is provided with described Aerobic Process for Treatment system the mud outlet side be connected with described sludge treating system.
Restaurant garbage treating system as above, wherein, also comprise a chemical administration system, described chemical administration system has multiple being connected with described system for anaerobic treatment, described Aerobic Process for Treatment system, described sludge treating system respectively, in order to add chemicals respectively in described system for anaerobic treatment, described Aerobic Process for Treatment system, described sludge treating system.
Washing restaurant garbage treating system as above, wherein, also comprises: a marsh gas treating system, and the air inlet of described marsh gas treating system is connected with the biogas outlet side of described system for anaerobic treatment.
Washing restaurant garbage treating system as above, wherein, the water inlet end of described advanced treatment system is connected with the water side of described Aerobic Process for Treatment system, and described advanced treatment system has a water side.
In sum, owing to have employed technique scheme, the present invention washes restaurant garbage treating system, and to solve Chinese unique cooking culture in prior art large based on the changing food waste water content of residue after the meal, impurity is various, the technical problem that treatment effect is very undesirable, respectively by pretreatment system, system for anaerobic treatment, Aerobic Process for Treatment system, advanced treatment system, marsh gas treating system, sludge treating system, the process of exhaust treatment system and chemical administration system, play good treatment effect, there is following advantage: 1, healthy: namely changing food waste discharging produces namely clear, in utilization, water sieve is washed rubbish and is removed peculiar smell, create cleaning ambient, forgo manual sorting, realize high-efficient automatic, whole system closed operation simultaneously, stench is avoided to spread, and be combined with aerobic water treatment and build special emission-control equipment, 2, safety: the i.e. product of changing food waste discharging is namely clear, creates the environment of a neat and tidy, avoids piling up generation hydrogen and other damps, fully demonstrates the respect to life and health, 3, environmental protection: by sieving and washing the waterpower of changing food waste, can extract organic matter (pollution) to greatest extent, realize minimizing and resource, the discarded object simultaneously sieved and washed cleans innoxious, 4, energy-conservation: to avoid selecting the high-power pulverizing of high rotating speed and centrifugal separation equipment, fully realize energy-conservation, the compact stirring power required for high efficiency anaerobic reactor greatly reduces simultaneously, 5, automation: abandon manual sorting, integrated pre-processing device.
Accompanying drawing explanation
Fig. 1 is the structural representation that the present invention washes restaurant garbage treating system;
Fig. 2 is the structured flowchart schematic diagram that the present invention washes restaurant garbage treating system;
Fig. 3 is the structured flowchart schematic diagram that the present invention washes an embodiment of restaurant garbage treating system.
Detailed description of the invention
According to the content disclosed in claim of the present invention and summary of the invention, described in technical scheme of the present invention is specific as follows:
Fig. 1 is the structural representation that the present invention washes restaurant garbage treating system, Fig. 2 is the structured flowchart schematic diagram that the present invention washes restaurant garbage treating system, Fig. 3 is the structured flowchart schematic diagram that the present invention washes an embodiment of restaurant garbage treating system, refer to Fig. 1, Fig. 2, Fig. 3: the invention discloses a kind of washing restaurant garbage treating system, wherein, comprising:
One pretreatment system 101, in order to remove the organic matter in changing food waste; Before Anaerobic Treatment; material needs through pretreatment, and except rejecting the impurity protection follow-up equipment in changing food waste, larger object is the organic matter extracted as far as possible in rubbish; and anaerobic reaction is convenient in organic materials making beating, lay the first stone for more producing natural pond.
Described pretreatment system 101 in the present invention comprises the material-receiving device, a knot screen, a separating device for water with dregs, a degreasing unit and the pulverizing beating apparatus that set gradually, described material-receiving device has a feed end, described material-receiving device, described knot screen, described separating device for water with dregs, described degreasing unit, described pulverizing beating apparatus are connected by pipeline successively, and described pulverizing beating apparatus has a discharge end.
Splicing workshop in the present invention, primarily of hopper and helix transporting device composition, according to the principle of " namely producing namely clear " " operational support ", is designed to double wire system.Changing food waste, after receiving fortune vehicle transport and arriving disposal field, first arrives at the high-rise material discharging platform of pretreatment workshop, pours in hopper, then leave the theatre.Changing food waste in hopper is transported to rapidly follow-up rotary drum sieve through shaftless screw conveying device and carries out waterpower cleaning and initial gross separation.
The concrete technique effect except hetero moiety in the present invention in pretreatment system 101 is for extract organic matter to greatest extent; the coarse impurities such as removing waste tableware, metal implements, sandstone, glass or plastic containers, polybag, paper handkerchief, protect the safety of the equipment such as follow-up pulverizer, squeezer.
Pulp water in the present invention is separated can be called as street cleaner, specifically comprise: rotary drum washing and sieving machine and grit water separator, rotary drum washing and sieving machine specifically act as: changing food waste is transported to rotary drum sieve equably by shaftless screw, water in the circulation of usual employing 2 ~ 3 times, namely biochemical treatment output water temperature (35 DEG C) is heated to the hot water of (45 ~ 50 DEG C), after sieving and washing, wash out organic pollution while hogwash taste removal and most economical limit can be realized.Rotary drum washing and sieving machine is a kind of horizontally-mounted waterpower rinsing device, automatically can isolate by rinsed residue at end simultaneously.The rubbish that helical feed is come falls in rotary drum washing and sieving machine continuously, relies on the rotation of rotary drum washing and sieving machine that rubbish is stirred in rinsing liquid, reaches the object of washing.
Further, the rubbish of the large scale of construction that rotary drum filters out and sewage directly fall into the grit water separator of bottom, at this, rely on the impact of gravity, by the dynamics viscosity (magma has up to thousands of mPas) sieving and washing hot water in a large number and greatly reduce fluid, light flotation of material is to the upper strata of separator, and the heavy substance of proportion more than 1.5 is then precipitated to the bottom of separator, the relative homogeneous material in portion is mainly organic food residue in the separator, be then transferred next step process.
Further, also have one and overlap the rotary sieve of spacing 1mm separation accuracy with street cleaner supporting 2, the fluid of often overlapping the maximum 50m3/h that process street cleaner discharges and the oversize less than 7 tons/h wherein contained, target is as far as possible by organic solidity thing wherein and fluid separation applications, is convenient to oily-water seperating equipment oil removing.Rotary sieve is made up of the rotary drum filter that is rotated, in rotary drum filter, have spiral, conveying oversize.Rotary sieve diameter 1.5m, long 3m are the characteristics design of changing food waste specially.Slag-water slurry, first enters from one end of rotary sieve.Water falls into collecting pipe by the filter screen of spacing 1mm and collects, and goes out water pump by filter screen and squeeze into oil removing pot, carries out next step oil removal treatment.Slag is then slowly taken to the other end of rotary sieve by auger conveyor, fall into making beating tank there.
Oil removing part in the present invention in pretreatment system 101 is specially: the grease in changing food waste needs to extract as much as possible, this is not only only and obtains grease income, and the suppression reduced because LCFA reacts anaerobic organism, improve the task performance of anaerobic reactor.Be separated through previous step pulp water, the most of oil in changing food waste is along with the liquid inflow oil removing pot after filtration, and the oil be adsorbed in solid hogwash then enters making beating tank, because in hogwash, the content of oil is less, is can be born by AFR anaerobic reactor and be easy to digestion.Therefore mainly for the abundant Extraction and separation of bulky grain grease, and deliberately in separation means, do not employ too high energy consumption and lose more than gain.This process must be easier to realize in water-oil phase process, even if in the state of normal temperature, therefore, Gravity Separation and normal temperature oil removing are the advantages of this oil removing process process energy conservation.
Also comprise a gun barrel, in order to normal temperature separation can not carried out in special oil removing pot by the profit of screenings interference.Be equipped with slow stirrer in oil removing pot, prevent the solidity thing in profit from floating and disturb oil removing, go up cloth aluminum strip simultaneously and float to realize after particle diameter of growing up being separated for adsorbing little oil droplet.Liquid after oil removing is partly refluxed to making beating tank, and remainder branch enters system for anaerobic treatment 102(AFR water inlet tank).The tubular type oil extracting machine that gun barrel top layout is special, be for low oil-containing water form effective separate mode of oil sheet.
Pulverizing making beating in the present invention in pretreatment system 101 is specially, comparatively large through the isolated screenings volume of rotary sieve, directly enters air-flotation type anaerobic reactor (AFR) not easily digested, before Anaerobic Treatment, needs further to pulverize.Screenings first will with the liquid mixing that refluxes in oil removing pot, the material mixed will be sheared machine and grinder and pulverize, and the material after pulverizing enters system for anaerobic treatment 102(AFR and to intake tank).
The present invention also comprises cutter, and concrete technique effect is: the material through preliminary cutting enters twin shaft cutter, and cutter shears rear mixed material by < 2cm, enters grinder subsequently, to prepare more tiny material.
Further, the present invention also comprises grinder, and after leaving cutter, before entering AFR anaerobism water inlet tank, cutting accuracy is that the hogwash sheared grinds, to improve the feed conditions of anaerobic digestion by the single shaft grinder of 1mm further.
Described pretreatment system 101 has a changing food waste feed end and a changing food waste discharge end, the changing food waste discharge end of described pretreatment system 101 is connected with the charging aperture of a system for anaerobic treatment 102, and described system for anaerobic treatment 102 has a biogas outlet side and a waste water outlet side; There is in system for anaerobic treatment 102 an air-flotation type anaerobic reactor (AFR), material after grinding enters AFR water inlet tank through making beating tank elevator pump, mix with the direct liquid entered into water tank from oil removing pot, in order to reach better mixed effect and prevent solid content from precipitating, in AFR water inlet tank, mixer is housed.In pond, the pH value of material is monitored continuously, and adds the pH value of NaOH to material when needed and regulate.Regulating reservoir is equipped with liquid level gauge to monitor its liquid level continuously.The water outlet of AFR water inlet tank pumps into AFR reactor by AFR reactor intake pump.For providing a stable charging operating mode to subsequent bio reaction, the fluctuation that balance pretreatment split run runs, the AFR of design tank of intaking is very large, plays the effect regulating buffering simultaneously.AFR anaerobic reactor, in AFR reactor, in waste water, most COD is degraded, is converted into biogas.The biogas that AFR reactor produces drains into bionethanation system from reactor head, and can carry out biogas desulfurization purification as required.
One Aerobic Process for Treatment system 103, in order to remove biodegradable organic pollution further, the charging aperture of described Aerobic Process for Treatment system 103 is connected with the waste water outlet side of described system for anaerobic treatment 102, and described Aerobic Process for Treatment system 103 has a water side.Described Aerobic Process for Treatment system 103 in the present invention specifically comprises: a dephosphorizing reactor (PHOSPAQ reactor), and in order to remove phosphorus and to reduce the situation occurring guanite in follow-up system, described dephosphorizing reactor has a water side; One short-cut denitrification reactor (ANAMMOX reactor), being connected with the water side of described dephosphorizing reactor of described short-cut denitrification reactor, in order to carry out denitrogenation processing to waste water; One activated sludge process aeration tank, described activated sludge process aeration tank is connected with the water side of described short-cut denitrification reactor, in order to carry out aerobic aeration process to waste water.Waste water removes biodegradable organic pollution further through the process of aerobic activated sludge system again after high temperature anaerobic process.But due to the total N in waste water and total P content higher, also denitrogenation dephosphorizing process can be carried out as required, especially in hogwash, a large amount of protein is broken down into high ammonia nitrogen, easily causes ammonia poisoning, adopts reflux dilution after ANAMMOX short-cut denitrification to be solve the poisoning effective way of high ammonia nitrogen.
Aerobic Process for Treatment system 103 in the present invention also has a waste gas outlet side, one exhaust treatment system 104 is connected with the waste gas outlet side of described Aerobic Process for Treatment system 103, because changing food waste treatment plant is very easy to produce stench, for ensureing good working environment, the extraction waste gas of necessary Wind Volume in time.
Further, also comprise in the present invention:
The present invention also comprises: a marsh gas treating system 107, and the air inlet of described marsh gas treating system 107 is connected with the biogas outlet side of described system for anaerobic treatment 102.Described marsh gas treating system 107 specifically comprises the biogas flow detector, a methane voltage-stabilizing cabinet, a biogas burner, a condensation water tank and the methane bio-desulfurization system that connect successively.Described methane bio-desulfurization system specifically comprises: a biological scrubbing tower, a bioreactor and a sulphur settling vessel.
The present invention also comprises an advanced treatment system 108, in order to remove COD and TSS of part difficult for biological degradation further, the water inlet end of described advanced treatment system 108 is connected with the water side of described Aerobic Process for Treatment system 103, and described advanced treatment system 108 has a water side.
Further, the described advanced treatment system 108 in the present invention specifically comprises:
One Fenton reaction tank, in order to remove the organic pollution of difficult for biological degradation in waste water by chemical Strong oxdiative;
One tilted plate separator, the water inlet end of described tilted plate separator is connected with the water side of described Fenton reaction tank, in order to the waste water flowed in described tilted plate separator is carried out Separation of Solid and Liquid.
One sludge treating system 105, the excess sludge that this sewage treatment plant discharges needs to collect, utilize and process.Because the dry solids content of these mud is lower, for increasing the dry solids content of mud, mud must dewater further with mechanical sludge dewatering equipment.Described system for anaerobic treatment 102 and described Aerobic Process for Treatment system 103 are provided with the mud outlet side be connected with described sludge treating system 105;
Further, sludge treating system 105 is also connected with the discharge end of the Fenton reaction tank of advanced treatment system 108.
The mud that native system design need process mainly comprises the residue anaerobic sludge of AFR air supporting reactor assembly, PHOPAQ mud and FETON excess sludge, and we can be referred to as " grog ", is the very good raw material manufacturing fertilizer.
Described sludge treating system 105 in the present invention specifically comprises:
One mud mixing pit, mixes in order to the mud of described system for anaerobic treatment 102 and described Aerobic Process for Treatment system 103 being discharged;
One horizontal spiral centrifuge system, described horizontal spiral centrifuge system is connected with the discharge end of described mud mixing pit, carries out processed in order to the mud of discharging described mud mixing pit.
One chemical administration system 106, described chemical administration system 106 has multiple being connected with described system for anaerobic treatment 102, described Aerobic Process for Treatment system 103, described sludge treating system 105 respectively, in order to add chemicals respectively in described system for anaerobic treatment 102, described Aerobic Process for Treatment system 103, described sludge treating system 105.
Described chemical administration system 106 in the present invention specifically comprises:
One alkali dosing system, described alkali dosing system is connected with described Fenton reaction tank, in order to add alkali lye in Fenton reaction tank;
One MgO adds unit, and described MgO adds unit and is connected with described dephosphorizing reactor;
One sulfuric acid adds unit, and described sulfuric acid adds unit and is connected with described Fenton reaction tank, in order to add H2SO4 to described Fenton reaction tank;
One H2O2 adds unit, and described H2O2 adds unit and is connected with described Fenton reaction tank;
One FeSO4 adds unit, and described FeSO4 adds unit and is connected with described Fenton reaction tank;
One PAM adds unit, and described PAM adds unit and is connected with described system for anaerobic treatment 102, described Fenton reaction tank respectively;
Described PAM add unit also described sludge treating system 105 be connected, in order to provide dewatering performance of sludge when mechanical sludge dewatering.
In one embodiment of the invention, chemical administration system 106 can adopt following technical scheme:
This partial design establishes 6 covers chemistry administration systems 106 altogether for adding alkali, MgO, sulfuric acid, H2O2, FeSO4 and PAM(two cover).
1, alkali dosing system
NaOH alkali lye (30%) is supplied to NaOH storage tank by alkali discharging pump.
NaOH storage tank is furnished with liquid level gauge and monitors its liquid level continuously, and control NaOH discharging pump and NaOH add the start and stop of pump, produces two position and reports to the police.Add pump to add in alkali lye and FENTON reaction tank add alkali lye respectively to regulating reservoir, scrubbing tower unit.NaOH storage tank has evacuated tube.
2, MgO adds unit (PHOSPAQ uses)
MgO is added by dosing pump by storage tank in PHOSPAQ.
MgO storage tank is furnished with liquid level gauge and monitors its liquid level continuously, and the start and stop of control MgO dosing pump, produce two position and report to the police.This tank has evacuated tube.
3, sulfuric acid adds unit (FENTON uses)
Sulfuric acid (98%) is supplied to sulfuric acid storage tank by sulfuric acid discharging pump.
H2SO4 storage tank is furnished with liquid level gauge and monitors its liquid level continuously, and control H2SO4 discharging pump and H2SO4 add the start and stop of pump, produces two position and reports to the police.This tank has evacuated tube.
Two H2SO4 add pump (the using and the reserved) for adding H2SO4 to Fenton reaction tank.
4, H2O2 adds unit (FENTON uses)
A H2O2 storage tank is for storing H2O2, H2O2(27.5%) squeeze into H2O2 storage tank by discharging pump from tank car.Two H2O2 dosing pumps (the using and the reserved) are for adding hydrogen peroxide to Fenton reaction tank.H2O2 storage tank is furnished with liquid level gauge and monitors its liquid level continuously, and the start and stop of control H2O2 discharging pump and H2O2 dosing pump.This tank has evacuated tube.
5, FeSO4 adds unit (FENTON uses)
FeSO4.7H2O is transported to scene in solid form, and in two FeSO4 dissolving tanks, be mixed with the FeSO4 solution of 30%.The FeSO4 solution dissolved is added to Fenton reaction tank by two FeSO4 dosing pumps (the using and the reserved).
FeSO4 dissolving tank can produce high and low liquid level warning.
6, PAM adds unit (for AFR air supporting and FENTON)
Need to add flocculant to improve settling property before AFR air supporting and in FENTON flocculation tank.
A set of automatic flocculant is prepared unit and is added for the PAM of AFR air-flotation system, FENTON unit.Flocculant consumption is estimated as 2ppm.
7, PAM adds unit (for sludge dewatering)
Need during mechanical sludge dewatering to add flocculant to provide dewatering performance of sludge.
A set of automatic flocculant is prepared unit and is added for the PAM of sludge dewatering system.Flocculant needs first water-soluble before the use, and flocculant consumption is estimated as dewatered sludge 4kg per ton.The solution prepared mixes in the pipeline being pumped to dewaterer front portion with flocculant concentration pump.
In sum, owing to have employed technique scheme, the present invention washes restaurant garbage treating system, and to solve Chinese unique cooking culture in prior art large based on the changing food waste water content of residue after the meal, impurity is various, the technical problem that treatment effect is very undesirable, respectively by the process of pretreatment system, system for anaerobic treatment, Aerobic Process for Treatment system, advanced treatment system, marsh gas treating system, sludge treating system, exhaust treatment system and chemical administration system, play good treatment effect, there is following advantage:
1, healthy: namely changing food waste discharging produces namely clear, in utilization, water sieve is washed rubbish and is removed peculiar smell, creates cleaning ambient, forgo manual sorting, realizes high-efficient automatic, simultaneously whole system closed operation, avoid stench to spread, and be combined with aerobic water treatment and build special emission-control equipment;
2, safety: the i.e. product of changing food waste discharging is namely clear, creates the environment of a neat and tidy, avoids piling up generation hydrogen and other damps, fully demonstrates the respect to life and health;
3, environmental protection: by sieving and washing the waterpower of changing food waste, can extract organic matter (pollution) to greatest extent, realize minimizing and resource, the discarded object simultaneously sieved and washed cleans innoxious;
4, energy-conservation: to avoid selecting the high-power pulverizing of high rotating speed and centrifugal separation equipment, fully realize energy-conservation, the compact stirring power required for high efficiency anaerobic reactor greatly reduces simultaneously;
5, automation: abandon manual sorting, integrated pre-processing device.
Above preferred embodiment of the present invention is described.It is to be appreciated that the present invention is not limited to above-mentioned particular implementation, the equipment wherein do not described in detail to the greatest extent and structure are construed as to be implemented with the common mode in this area; Any those of ordinary skill in the art, do not departing under technical solution of the present invention ambit, the Method and Technology content of above-mentioned announcement all can be utilized to make many possible variations and modification to technical solution of the present invention, or being revised as the Equivalent embodiments of equivalent variations, this does not affect flesh and blood of the present invention.Therefore, every content not departing from technical solution of the present invention, according to technical spirit of the present invention to any simple modification made for any of the above embodiments, equivalent variations and modification, all still belongs in the scope of technical solution of the present invention protection.

Claims (9)

1. wash a restaurant garbage treating system, comprising:
One pretreatment system, in order to remove the organic matter in changing food waste, described pretreatment system specifically comprises an impurity removing unit, an oil removing unit and a pulverizing unit, it is characterized in that, also comprises setting gradually:
One system for anaerobic treatment;
One Aerobic Process for Treatment system, in order to remove biodegradable organic pollution further; Described Aerobic Process for Treatment system specifically comprises: a dephosphorizing reactor, in order to remove phosphorus and to reduce the situation occurring guanite in follow-up system; One short-cut denitrification reactor, in order to carry out denitrogenation processing to waste water;
One exhaust treatment system, described exhaust treatment system specifically comprises: an activated sludge scrubbing tower, in order to remove residual activity pollutant;
One advanced treatment system, in order to remove COD and TSS of part difficult for biological degradation further.
2. restaurant garbage treating system according to claim 1, is characterized in that, the waste material outlet side of described advanced treatment system is connected with treatment system with described.
3. restaurant garbage treating system according to claim 1, is characterized in that, the charging aperture of described Aerobic Process for Treatment system is connected with the waste water outlet side of described system for anaerobic treatment, and described Aerobic Process for Treatment system has a water side.
4. restaurant garbage treating system according to claim 1, is characterized in that, described Aerobic Process for Treatment system also has a waste gas outlet side, and described exhaust treatment system is connected with the waste gas outlet side of described Aerobic Process for Treatment system.
5. restaurant garbage treating system according to claim 3, it is characterized in that, described pretreatment system has a changing food waste feed end and a changing food waste discharge end, the changing food waste discharge end of described pretreatment system is connected with the charging aperture of described system for anaerobic treatment, and described system for anaerobic treatment has a biogas outlet side and a waste water outlet side.
6. restaurant garbage treating system according to claim 1, is characterized in that, also comprises: a sludge treating system, and described system for anaerobic treatment is provided with described Aerobic Process for Treatment system the mud outlet side be connected with described sludge treating system.
7. restaurant garbage treating system according to claim 6, it is characterized in that, also comprise a chemical administration system, described chemical administration system has multiple being connected with described system for anaerobic treatment, described Aerobic Process for Treatment system, described sludge treating system respectively, in order to add chemicals respectively in described system for anaerobic treatment, described Aerobic Process for Treatment system, described sludge treating system.
8. washing restaurant garbage treating system according to claim 1, is characterized in that, also comprise: a marsh gas treating system, the air inlet of described marsh gas treating system is connected with the biogas outlet side of described system for anaerobic treatment.
9. washing restaurant garbage treating system according to claim 1, is characterized in that, the water inlet end of described advanced treatment system is connected with the water side of described Aerobic Process for Treatment system, and described advanced treatment system has a water side.
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Cited By (2)

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Publication number Priority date Publication date Assignee Title
CN106244429A (en) * 2016-08-31 2016-12-21 宜兴市欧亚华都环境工程有限公司 A kind of synergic fermentation system being applied to changing food waste process
CN106399064A (en) * 2016-08-31 2017-02-15 宜兴市欧亚华都环境工程有限公司 System for kitchen waste disposal

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