CN107008730B - Refuse disposal system and waste disposal method - Google Patents

Refuse disposal system and waste disposal method Download PDF

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Publication number
CN107008730B
CN107008730B CN201710262387.1A CN201710262387A CN107008730B CN 107008730 B CN107008730 B CN 107008730B CN 201710262387 A CN201710262387 A CN 201710262387A CN 107008730 B CN107008730 B CN 107008730B
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China
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sewage
methane
generating pit
water
rubbish
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CN201710262387.1A
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CN107008730A (en
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许国志
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Zhengzhou Hepeng Precision Mechanical Equipment Co ltd
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Individual
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE
    • B09B3/00Destroying solid waste or transforming solid waste into something useful or harmless
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE
    • B09B5/00Operations not covered by a single other subclass or by a single other group in this subclass
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F9/00Multistage treatment of water, waste water or sewage
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2301/00General aspects of water treatment
    • C02F2301/08Multistage treatments, e.g. repetition of the same process step under different conditions
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2303/00Specific treatment goals
    • C02F2303/04Disinfection
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/28Anaerobic digestion processes
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel

Abstract

The present invention relates to a kind of refuse disposal systems and waste disposal method to solve the problems, such as to be difficult to effective, progress garbage disposal at low cost in the prior art.When handling rubbish using the waste disposal method of the present invention, it is directly discharged into municipal sewage pipe network after the rubbish of citizen's manufacture is pulverized, and constantly being washed away through interval siphon erosion and deposition device prevents pipeline to silt up.The rubbish that crushed is mixed in former municipal sewage and is transported to distribution reservoir through municipal sewage pipe network, coordinate the market of farm produce rubbish collected COD contents, acid-base value is made suitable for the sewage of growth methanotrophic bacterial strain requirement, the partial organic substances therein after quick methane-generating pit are rapidly decomposed into biogas to sewage again, the biogas slurry not being decomposed in quick methane-generating pit is sent to again in methane-generating pit at a slow speed, is adequately broken in methane-generating pit at a slow speed together with the food garbage being collected into and is generated a large amount of biogas.So the present invention can not only be recycled municipal refuse and sewage to the maximum extent, moreover it is possible to avoid the blockage problem of urban sewage pipeline.

Description

Refuse disposal system and waste disposal method
Technical field
The present invention relates to a kind of refuse disposal system and waste disposal methods.
Background technology
With the development of economy with the process of urbanization, the quantity of domestic waste and food garbage increasingly increases.Together When market kitchen waste treater also tend to popularize, be largely crushed the height with substances such as floating material, suspended matter and greasy dirts Concentration sewage enters sewage network, so that script is silted serious sewage network up and more can't bear the heavy load, it is therefore desirable to can effectively prevent The measure that sewage network silts up.A large amount of domestic waste and food garbage cause people's living environment and urban development How huge pressure and harm realize that the processing of innoxious domestic waste, minimizing and recycling has become research Focus.
At present countries in the world processing domestic waste method usually have the methods of composting method, landfill method and burning method into Row processing, and for food garbage without good processing method.And most of implementation landfill in the house refuse in China, It is handled with composting method at least partially through burning, the part in food garbage can be admitted to fermentation vat for producing methane, also Part food garbage can be poured into directly in sewer pipe.
It fills out that logos treating capacity is big, convenient and easy, small investment, is a kind of main method that China handles municipal refuse at present. But this method disadvantage has four, first, landfill will occupy large amount of land resources, second is that fermentation will produce methane to the rubbish being landfilled for a long time Imflammable gas easily causes explosion, third, environmental protection be not easy it is up to standard, it is desirable that Landfill condition is very stringent, and input cost is inevitable Increase;Fourth, the heavy metal and chemical toxicant in rubbish permeate the ground after polluted underground water.Harmful components can be right in rubbish simultaneously Air, soil and water source cause seriously to pollute.Both ecological environment is destroyed, health is also seriously endangered.
Burning method has the disadvantages that:First, capital consumption is huge, processing quantity of refuse is few;Second is that serious waste rubbish includes Resource;Third, causing serious environmental pollution.
Compost treatment needs to sort rubbish, the organic content for rubbish of classifying, require wants high.Country's rubbish point at present The technological levels such as class screening, hot fermentation, the control of malodorous discharge object are high not enough, and gained fertilizer quality is with municipal refuse plastics The object ingredient that is stale-proof rises and declines, and processing quantity of refuse is big, and labor intensity is big, not dominant compared with chemical fertilizer, comprehensively relatively Market becomes smaller and smaller afterwards.
Be used alone food garbage producing methane when, food garbage protein content is excessively high, easily cause it is acidified Sheng and no longer Production acid inhibits methane backeria activity, gas production is caused to decline, can solution to this problem so needs are a kind of.
After food garbage is poured into sewer, the food garbage containing a large amount of oils is more easy to block sewer.
From the point of view of the above garbage disposal method pros and cons, the garbage disposal rate in China is reached by existing method and technology at present 58.2%, but harmless treatment only accounts for 5% or so, and 58.2% handling rate is also that costly investment and consumption are huge Energy consumption and consuming large amount of land resources are cost, so the processing of domestic waste is to shoulder heavy responsibilities.
Invention content
The purpose of the present invention is to provide a kind of refuse disposal system with solve to be difficult in the prior art it is simple and effective, low at Local the problem of carrying out garbage disposal;It is a kind of using above-mentioned refuse disposal system progress rubbish the present invention also aims to provide The waste disposal method of processing.
To achieve the above object, refuse disposal system of the invention adopts the following technical scheme that:
Refuse disposal system, including rubbish crush module, rubbish conveyor module and garbage disposal module;Rubbish conveyor module It sets including family's sewer pipe, cell blowdown manifold, the sewage network of municipal arterial highway sewage pipe composition and along sewage network distribution The interval siphon erosion and deposition device set;Garbage disposal module include for by the rubbish conveyed by sewage network be configured to COD contents, The distribution reservoir for the sewage that acid-base value requires suitable for growth methanotrophic bacterial strain, further include in fast decoupled distribution reservoir organic matter it is quick Methane-generating pit and methane-generating pit at a slow speed for fully decomposing residual organic substances in quick methane-generating pit, garbage disposal module further includes being used for It handles and collects quick methane-generating pit and make the Marsh gas treatment equipment of biogas in methane-generating pit at a slow speed.
Garbage disposal module includes for storing sewage to carry out the horizontal flow basin of layered shaping to sewage and for hydrolyzing drift The floating material hydrolytic tank of float and bulky grain suspended matter, the water inlet of horizontal flow basin, which is set gradually, to be useful for stopping lump Trash rack, the coarse rack with crushing function and for by sewage floating material and bulky grain suspended matter be sent into the floating material Rotary drum fine fack in hydrolytic tank;Garbage disposal module further includes buffer pool, and buffer pool passes through with horizontal flow basin inlet passage bottom Bend pipe is connected to, and the spilling water absolute altitude of bend pipe is flushed with water inlet setting water level and is provided in buffer pool for taking out its interior sewage Enter the water pump of the water inlet, the setting of buffer pool is advantageously ensured that into the waterflow stabilization in the stream of flat pond.
Garbage disposal module further includes the agricultural trade rubbish hydrolytic tank for hydrolyzing agricultural trade rubbish, agricultural trade rubbish hydrolytic tank with match Pond connection passes through company so that the hydrolyzate containing large amount of organic after the hydrolysis of agricultural trade rubbish to be sent into distribution reservoir in the middle part of horizontal flow basin Siphunculus is connected to agricultural trade rubbish hydrolytic tank and provides water environment with the hydrolysis for agricultural trade rubbish.
Garbage disposal module includes anaerobic pond for being handled the waste water behind natural pond processed, biochemistry pool, sedimentation basin and disappears Malicious pond, garbage disposal module further include the bioactivation pond for being handled the biogas residue behind natural pond processed;The anaerobic pond and heavy The bottom of pond in shallow lake pond is both provided with to be connected to distribution reservoir and/or quick methane-generating pit largely to be had to gather anaerobic pond and sedimentation basin bottom The bottom muddy water of machine object is sent to the distribution reservoir and/or quick methane-generating pit and it is made to participate in the connecting pipe for recycling natural pond processed.
The junction of interval siphon erosion and deposition device and cell blowdown manifold and municipal arterial highway sewage pipe are provided with anti-return dress It sets, the back-flow preventer includes the inclined tube for tilting down setting along sewage;Interval siphon erosion and deposition device further includes Place is washed away for being connected to the distal end at the easy blocking of neighbouring pipeline.
The waste disposal method of the present invention uses following technical scheme
Waste disposal method includes the following steps:The rubbish that family generates is crushed and is directly discharged by the first step, each user In family's sewer pipe;Second step, by interval siphon erosion and deposition device successively by the rubbish in family's sewer pipe with flow It is sent into the distribution reservoir in garbage disposal area through cell blowdown manifold and municipal arterial highway sewage pipe;Third walks, and is added into distribution reservoir The market of farm produce rubbish being collected into distribution reservoir to prepare COD contents, acid-base value suitable for the sewage of growth methanotrophic bacterial strain requirement;The Four steps the sewage in distribution reservoir are added in quick methane-generating pit, in the fermentative microorganism fast decoupled sewage in quick methane-generating pit Partial organic substances generate biogas;Biogas slurry after quick methane-generating pit is transported in methane-generating pit at a slow speed by the 5th step, while to slow The food garbage being collected into is added in fast methane-generating pit, the fermentative microorganism in methane-generating pit fully decomposes organic produce in it at a slow speed Raw biogas;6th step, the biogas that purified treatment methane-generating pit generates.
The sewage that the garbage disposal area is flowed by municipal arterial highway sewage pipe will appear the feelings that a large amount of drosses swim in upper layer Condition specifically includes following steps in the second step, step 201, collects in the sewage flowed by municipal arterial highway sewage pipe Dross and bulky grain suspended matter;Collect the lower water that is flowed by municipal arterial highway sewage pipe, it is largely organic in the lower water being collected into Object accumulates in lower layer and forms bottom sludge;It collects the mid-water in the sewage flowed by municipal arterial highway sewage pipe and detects middle level Concentration of suspension in water carries out Anaerobic Treatment, when concentration of suspension is more than when concentration of suspension is less than setting value to mid-water When setting value, first mid-water is sent into when quick methane-generating pit is handled to concentration of suspension less than setting value, it is carried out at anaerobism again Reason;
Step 202, the bottom sludge in lower water is sent into the distribution reservoir;The upper layer dross and bulky grain that will be collected into Suspended matter is hydrolyzed under water environment, and large amount of organic is deposited on lower layer after hydrolysis, described in the lower water feeding after hydrolysis In quick methane-generating pit;Upper layer is difficult to the object hydrolyzed and is sent into recovery and processing system;
Step 203, collect described in being sent into supernatant of the sewage in methane-generating pit behind natural pond tentatively processed at a slow speed, to supernatant into The lower water for being populated with large amount of organic is sent into the distribution reservoir after row biochemical treatment, precipitation.
In second step, the sewage to flowing into garbage disposal area by municipal arterial highway sewage pipe is also needed to before step 201 Buffered is carried out with the water supply flow of equalization stable municipal sewage pipe network horizontal flow basin into garbage disposal area.
In third step, market of farm produce rubbish is first sorted, crush after be hydrolyzed under water environment, contain after hydrolysis There is the hydrolyzate of large amount of organic to be sent in the distribution reservoir, by the water that the mid-water in step 201 is market of farm produce rubbish Solution provides water environment.
The methane-generating pit at a slow speed includes medium temperature methane-generating pit and high temperature methane tank, the sludge in the quick methane-generating pit and food and drink Rubbish, which is transported in medium temperature methane-generating pit, participates in natural pond processed, and the biogas slurry after a natural pond end cycle processed in the medium temperature methane-generating pit is sent To natural pond processed is participated in the high temperature methane tank, medium temperature methane-generating pit is sent with supernatant of high temperature methane tank after natural pond processed in it Biochemical treatment is carried out toward biochemistry pool, the biogas of generation is sent to Marsh gas treatment equipment to carry out the biogas treatment described in the 6th step.
Beneficial effects of the present invention are as follows:When handling rubbish using the waste disposal method of the present invention, the rubbish of citizen's manufacture It is directly discharged into municipal sewage pipe network after rubbish is pulverized, and constantly being washed away through interval siphon erosion and deposition device prevents pipeline to silt up.It will The rubbish that crushed is mixed in former municipal sewage and is transported to distribution reservoir through municipal sewage pipe network, coordinates the market of farm produce rubbish of collection COD contents, acid-base value is made suitable for the sewage of growth methanotrophic bacterial strain requirement, the sewage part therein after quick methane-generating pit again Organic matter is rapidly decomposed into biogas, and the biogas slurry not being decomposed in quick methane-generating pit is sent to again in methane-generating pit at a slow speed, with receipts The food garbage collected is adequately broken in methane-generating pit at a slow speed together generates a large amount of biogas.So using the present invention quickly processing The preliminary treatment to sewage is also achieved while various municipal refuses, is fully recycled the recyclable part in it, is subtracted significantly The water quality of small discharge garbage bulk and sewage effluent.The setting in interval siphon erosion and deposition pond is more that of avoiding urban sewage pipeline Blockage problem, and the setting of distribution reservoir enables the sewage into quick methane-generating pit to meet natural pond condition processed always and can continue to participate in Natural pond processed is conducive to the rate of recovery for improving municipal refuse.
Description of the drawings
Fig. 1 crushes the knot of module and rubbish conveyor module for rubbish in one embodiment of the refuse disposal system of the present invention Structure schematic diagram.
Specific implementation mode
The embodiment of the refuse disposal system of the present invention:
The refuse disposal system of the present invention is as described in Figure 1, includes that rubbish for crushing rubbish crushes module, for defeated Send the rubbish conveyor module of rubbish and for recycling the garbage disposal module that can use part in rubbish.
Rubbish crush module include be arranged kitchen food waste powder millstone 1, toilet rubbish in toilet is set Grinder 2 and the garbage disposer 12 being arranged on street.Rubbish conveyor module includes family's sewer pipe, cell blowdown manifold And the sewage network of municipal arterial highway sewage pipe composition, further include blocking the interval siphon of sewage network for washing away rubbish to prevent it Erosion and deposition device.Interval siphon erosion and deposition device includes interval siphon erosion and deposition pond 3, for extracting supernatant in sewage network and being sent into institute It states the water pump 10 in interval siphon erosion and deposition pond and washes away place for being connected to the distal end at its easy blocking of arbitrary sewage network nearby 5.Distal end is washed away to be connected between place 5 and interval siphon erosion and deposition pond 3 washes away the solenoid valve 4 whether place 5 washes by water for controlling distal end, It only needs opening solenoid valve 4 that distal end can be used to wash away place 5 to wash away at the easy blocking in sewage network.Under usual state, sewage It is the turning of pipeline at easy blocking in pipe network.Use small pump to interval siphon erosion and deposition pond in interval siphon erosion and deposition device Internal pump water, with mass-flow erosion and deposition.
To prevent interval erosion and deposition device from destroying the pipeline in sewage network, the company of interval siphon erosion and deposition device and sewage network The place of connecing is provided with along the pipeline for tilting down setting of sewage and forms and wash away pipette tips 8.Washing away pipette tips 8 can also play It prevents the effect of sewage backflow and constitutes back-flow preventer.
Interval siphon erosion and deposition device can during new building is built the same period be implemented at the working lining in new building, also may be used With by being transformed to Lao Lou drainages.When improving Lao Lou drainages, may because in building without installation space, this When need Lao Lou sewer pipe between interval siphon erosion and deposition pond 3 be arranged septic tank 9 fallen to prevent the flow in sewage network It fills.Septic tank 9 or rubbish, which crush, is connected with expansion pond 6 on the sewage network between module and interval siphon erosion and deposition device, prevent Sewage is flow backwards when mass-flow erosion and deposition, expands the air bleeding valve 7 that supplied gas discharge is provided on pond 6.
Household garbage is discharged by food waste powder millstone 1 and toilet garbage grinder 2 in family's sewer pipe, interval The collector nozzle of siphon erosion and deposition device washes away family's sewer pipe and makes it through septic tank and flow into cell blowdown manifold.In cell Family's sewer pipe merge into and be provided at the position of cell blowdown manifold for washing away the rubbish that deposits at the total mouth of a river of cell Interval siphon erosion and deposition device, interval siphon erosion and deposition device savings wash away water source by water pump 10 from the supernatant of septic tank 9 Extraction.The rubbish that cleaner collects crushes by garbage disposer 12 and is directly discharged into the arterial highways cell blowdown manifold or municipal In sewage pipe.Due to needing water environment when garbage disposer 12 handles rubbish, so water source and rubbish in interval siphon erosion and deposition pond 3 The electrically operated valve 11 of control flow break-make is connected to and is connected on pipeline between rubbish processor 12 by pipeline.Along the dirt of municipal arterial highway Water pipe is additionally provided with the interval siphon flushing device for washing away in municipal arterial highway sewage pipe the rubbish that deposits, due in the device Interval siphon washes away that 3 reserves of pond are very big, so the stream in flow comes direction and washes away pond 3 and municipal arterial highway sewage in interval siphon The junction of pipe is provided with anti-overflow device of water 13, and anti-overflow device of water 13 prevents the dirt caused by front-end pipelines silt up when mass-flow erosion and deposition Water overflows ground, the solenoid valve 4 in the corresponding interval siphon erosion and deposition device of joint control.It is also associated with moisture storage capacity on municipal arterial highway sewage pipe Larger collecting-tank 16 is provided with for the supernatant in it to be pumped to the water pump for washing away pond 3 into interval siphon in collecting-tank 16 10。
It is dirty to be sent into municipal arterial highway by above method for cell 14 and the rubbish manufactured in Biohazard Waste Disposal 15 on the way on the way In water pipe, and as municipal arterial highway sewage pipe is admitted to garbage disposal module to carry out subsequent processing.
Garbage disposal module includes the horizontal flow basin 21 for being flowed into for the sewage in municipal arterial highway sewage pipe, and sewage is through advection Pond 21 is divided into upper, middle and lower-ranking naturally, and upper layer contains the larger suspended matter of a large amount of particles and is sent to floating material hydrolytic tank 22 In, lower layer's sludge for containing large amount of organic and be admitted in distribution reservoir 24, middle level is sent in anaerobic pond 32 and carries out at anaerobism Reason.When sewage in municipal arterial highway sewage pipe is flowed into through water inlet 211 in horizontal flow basin 21, it is provided in the front end of water inlet 211 The trash rack 191 of the larger rubbish in sewage can be filtered out.The powder for further grinding up the refuse is additionally provided with after trash rack 191 Broken grid 192 is crushed and is provided with for that will enter floating material, particulate matter in the sewage before horizontal flow basin 21 after grid 192 The rotary drum fine fack 193 being sent in floating material hydrolytic tank 22.
To ensure that municipal arterial highway sewage pipe is stablized to the water supply flow of horizontal flow basin 21, garbage disposal module further includes buffer pool 20.Buffer pool 20 is connected to the inlet passage bottom of horizontal flow basin 21 by bend pipe, the spilling water absolute altitude of bend pipe and setting for water inlet Determine water level to flush.Inlet passage refers to the corresponding pipeline section that municipal arterial highway sewage pipe flows into garbage disposal area.It is provided in buffer pool 20 Water pump for its interior sewage suction to be fed to horizontal flow basin water inlet.When the flow in municipal arterial highway sewage pipe is higher than setting water level When, the part water level exceeded flows into buffer pool 20 underwater until in the sewage pipe of municipal arterial highway under the action of linker Until dropping to setting water level.It, will be in buffer pool 20 by water pump when the water level in municipal arterial highway sewage pipe is less than setting water level Sewage back suction enter water inlet, and can wash away crush grid 192.
Floating material in floating material hydrolytic tank 22 after being hydrolyzed, wherein the impurity that cannot be hydrolyzed is by rotary drum fine fack 221 It pulls out and is sent to process in plastics recovery system, large amount of organic is gathered in the bottom of pond of floating material hydrolytic tank 22 after hydrolysis, by floating material Sewage in hydrolytic tank 22, which is sent into the ponds USR 25, carries out quickly natural pond processed.The ponds USR 25 can rapidly decompose partial organic substances, but its It is difficult to fully decompose organic matter.So after one period of the ponds USR natural pond, while producing part biogas, lower layer according to So have the bed mud comprising large amount of organic.By in collecting methane to biogas treatment collecting device 31, by the upper layer in the ponds USR 25 Water is sent into heavy pond 26, and part bed mud is sent into medium temperature methane-generating pit 28 and is fully decomposed.Surface layer suspended matter passes through water distributor 251 Cycle in carrying out is sent into the ponds USR 25.
Into the sewage in heavy pond 26, its upper strata aqueous phase is admitted in anaerobic pond 32 and detests to relatively clean after precipitation Oxygen is handled, and is admitted to containing large amount of organic in distribution reservoir 24 in lower water.
The sewage that distribution reservoir 24 is used to prepare COD contents, acid-base value suitable for growth methanotrophic bacterial strain requirement.To stablize the ponds UASB 27 With the Sludge Bed nutrient demand in the ponds USR 25, and various municipal refuses can be fully recycled, garbage disposal module further includes agricultural trade rubbish Hydrolytic tank 23.After the agricultural trade rubbish being collected into is poured by hopper 231, and communicated band 232 is transported to the crushing of 233 upper end of feed inlet It is sent in agricultural trade rubbish hydrolytic tank 23.The part of horizontal flow basin 21 being sent in the mid-water of anaerobic pond 32 is sent to agricultural trade rubbish In hydrolytic tank 23 water environment is provided with the hydrolysis for agricultural trade rubbish.Hydrolyzate after the hydrolysis of agricultural trade rubbish is sent to distribution reservoir 24 It is interior.
The foul water fraction made in distribution reservoir 24 is sent in the ponds USR 25 to adjust the organic matter of sewage in the ponds USR 25 Content.The sewage made in distribution reservoir 24 simultaneously be also sent to in ponds UASB 27 that sewage quality requirement is more stringent with into Row fast decoupled natural pond, the sewage containing organic matter are sent by water distributor 271 in the ponds UASB 27.The ponds UASB 27 also can rapidly be divided Partial organic substances are solved, but are also difficult to fully decompose organic matter.So after one period of the ponds UASB natural pond, part natural pond is being produced While gas, lower layer still has the bed mud comprising large amount of organic.By in collecting methane to biogas treatment collecting device 31, Upper water in the ponds UASB 27 is sent into anaerobic pond 32 and carries out Anaerobic Treatment, lower layer's bed mud is sent into medium temperature methane-generating pit 28 and is carried out Fully decompose.
After one natural pond end cycle processed of medium temperature methane-generating pit 28, the supernatant of medium temperature methane-generating pit 28 is sent in anaerobic pond 32 Anaerobic Treatment is carried out, most of biogas slurry is sent in high temperature methane tank 29 and carries out further pyrohydrolysis, by small part lower layer Biogas residue is sent to activating tank 37 and carries out activation process.It is enough organic fully to recycle municipal refuse, providing medium temperature methane-generating pit 28 Object, garbage disposal module further include food-beverage rubbish treating equipment 30, through treated the organic matter quilt of food-beverage rubbish treating equipment 30 It is sent in medium temperature methane-generating pit 28 to recycle the organic matter in food garbage.
Further include biochemistry pool 33, sedimentation basin 34 and sterilization pool 35, sewage other than anaerobic pond 32 when handling sewage Being decomposed by macromolecular mass organic matter therein after anaerobic pond 32 has subset organic matter, is exposed into biochemistry pool 33 Gas biochemical treatment, then sewage is sent in sedimentation basin 34, the lower layer's water section for being populated with large amount of organic is sent to after precipitation In distribution reservoir 24, another part is sent into final deposition pool 36 and is finally precipitated.Supernatant after final deposition pool 36 precipitates is sent again Final process is carried out toward anaerobic pond 32, amount of activated sludge is sent in the ponds UASB 27 and is decomposed again.When in final deposition pool 24 Sewage after a cycle, the base sludge in final deposition pool 36 is sent in activating tank 37 and carries out activation process.
In the other embodiment of the refuse disposal system of the present invention, buffer pool can also save, and only feed horizontal flow basin The discharge of sewage is unstable;Water environment can be provided with the hydrolysis for agricultural trade rubbish with external water source, can only cause water source in this way Waste;The refuse disposal system of the present invention can not also include the anaerobic pond, biochemistry pool, precipitation for being handled waste water Pond and sterilization pool, but waste water is routed directly to the subsequent processing that sewage plant carries out sewage.
The embodiment of the waste disposal method of the present invention:
The method that rubbish is handled using the refuse disposal system of the present invention is as follows:
The rubbish that family generates is crushed and is directly discharged into family's sewer pipe by the first step, each user;
Second step, by interval siphon erosion and deposition device successively by the rubbish in family's sewer pipe as water flows through cell row Dirty manifold and municipal arterial highway sewage pipe are sent into the distribution reservoir in garbage disposal area;
Second step specifically again include:Step 201, the dross in the sewage flowed by municipal arterial highway sewage pipe and big are collected Grain suspended matter;The lower water flowed by municipal arterial highway sewage pipe is collected, large amount of organic accumulates in down in the lower water being collected into Layer and form bottom sludge;It collects the mid-water in the sewage flowed by municipal arterial highway sewage pipe and detects suspended matter in mid-water Concentration carries out Anaerobic Treatment when concentration of suspension is less than setting value to mid-water, when concentration of suspension is greater than the set value, First mid-water is sent into when quick methane-generating pit is handled to concentration of suspension less than setting value, Anaerobic Treatment is carried out to it again;
Step 202, the bottom sludge in lower water is sent into the distribution reservoir;The upper layer dross and bulky grain that will be collected into Suspended matter is hydrolyzed under water environment, and large amount of organic is deposited on lower layer after hydrolysis, described in the lower water feeding after hydrolysis In quick methane-generating pit;Upper layer is difficult to the object hydrolyzed and is sent into recovery and processing system;
Step 203, collect described in being sent into supernatant of the sewage in methane-generating pit behind natural pond tentatively processed at a slow speed, to supernatant into The lower water for being populated with large amount of organic is sent into the distribution reservoir after row biochemical treatment, precipitation.
Third walks, and the market of farm produce rubbish being collected into is added into distribution reservoir to prepare COD contents, soda acid in distribution reservoir The sewage that degree requires suitable for growth methanotrophic bacterial strain;
In this step, market of farm produce rubbish is first sorted, crush after be hydrolyzed under water environment, containing big after hydrolysis The hydrolyzate of amount organic matter is sent in the distribution reservoir, is carried by the hydrolysis that the mid-water in step 201 is market of farm produce rubbish For water environment.
Sewage in distribution reservoir is added in quick methane-generating pit 4th step, and the fermentative microorganism in quick methane-generating pit is quick The partial organic substances decomposed in sewage generate biogas;
Quick methane-generating pit includes the ponds USR 25 and the ponds UASB 27, and the organic matter source in the ponds USR 25 includes floating material hydrolytic tank Interior 22 upper layer floating material, the bottom sludge in floating material hydrolytic tank 22 and the sewage in distribution reservoir 24, the ponds USR 25 can quickly by Partial organic substances therein resolve into biogas.The organic matter source in the ponds USAB 27 is in sewage and final deposition pool 36 in distribution reservoir 24 Lower layer's sludge after precipitation.
Biogas slurry after natural pond processed in quick methane-generating pit is transported in methane-generating pit at a slow speed by the 5th step, while to natural pond at a slow speed The food garbage being collected into is added in gas pond, the fermentative microorganism in methane-generating pit fully decomposes the organic matter in it and generates natural pond at a slow speed Gas;
Methane-generating pit includes medium temperature methane-generating pit 28 and high temperature methane tank 29 at a slow speed, the bed mud in the quick methane-generating pit and food and drink Rubbish, which is transported in medium temperature methane-generating pit 28, participates in natural pond processed, the middle level after a natural pond end cycle processed in the medium temperature methane-generating pit 28 Water, which is sent in the high temperature methane tank 29, participates in high temperature natural pond, and medium temperature methane-generating pit 28 is with high temperature methane tank 29 after natural pond processed Supernatant in it is sent to biochemistry pool and carries out biochemical treatment, and the biogas of generation is sent to Marsh gas treatment equipment to carry out the 6th step The biogas treatment.
6th step, the biogas that purified treatment methane-generating pit generates.
In the other embodiment of the waste disposal method of the present invention, directly the sewage in sewage network can also be discharged into In distribution reservoir, then agricultural trade rubbish and other drugs are added to make the sewage met the requirements into distribution reservoir.Only at this time not Only production efficiency is slow, even more needs continually to clear up distribution reservoir.

Claims (8)

1. refuse disposal system, it is characterised in that:Module, rubbish conveyor module and garbage disposal module are crushed including rubbish;Rubbish Rubbish conveyor module includes family's sewer pipe, cell blowdown manifold, the sewage network of municipal arterial highway sewage pipe composition and along sewage The interval siphon erosion and deposition device of pipeline distribution setting;Garbage disposal module includes that the rubbish for will be conveyed by sewage network is prepared Further include for having in fast decoupled distribution reservoir at the distribution reservoir for the sewage that COD contents, acid-base value require suitable for growth methanotrophic bacterial strain The quick methane-generating pit of machine object and methane-generating pit at a slow speed for fully decomposing residual organic substances in quick methane-generating pit, garbage disposal module Further include for handling and collecting quick methane-generating pit and make the Marsh gas treatment equipment of biogas in methane-generating pit at a slow speed;Interval siphon is rushed Silt device includes interval siphon erosion and deposition pond, for extracting supernatant in sewage network and being sent into the interval siphon erosion and deposition pond Water pump and place is washed away for being connected to the distal end at its easy blocking of arbitrary sewage network nearby, distally washes away place and interval siphon punching It is connected between silt pond and washes away the solenoid valve whether place washes by water for controlling distal end, it is only necessary to opened solenoid valve and distal end can be used Place is washed away to wash away at the easy blocking in sewage network;Garbage disposal module further includes the agricultural trade rubbish water for hydrolyzing agricultural trade rubbish Xie Chi, agricultural trade rubbish hydrolytic tank are connected to distribution reservoir the hydrolyzate containing large amount of organic after the hydrolysis of agricultural trade rubbish is sent into water distribution In pond.
2. refuse disposal system according to claim 1, it is characterised in that:Garbage disposal module includes for storing sewage To carry out the horizontal flow basin of layered shaping to sewage and the floating material hydrolytic tank for hydrolyzing floating material and bulky grain suspended matter, advection The water inlet in pond, which is set gradually, is useful for stopping the trash rack of lump, the coarse rack with crushing function and for will be dirty Floating material and bulky grain suspended matter in water are sent into the rotary drum fine fack in the floating material hydrolytic tank;Garbage disposal module is also wrapped Buffer pool is included, buffer pool is connected to horizontal flow basin inlet passage bottom by bend pipe, and spilling water absolute altitude and the water inlet of bend pipe are set Water level flushes and is provided with the water pump for its interior sewage to be pumped into the water inlet in buffer pool, and being provided with for buffer pool is conducive to Ensure to enter the waterflow stabilization in the stream of flat pond.
3. refuse disposal system according to claim 1 or 2, it is characterised in that:Garbage disposal module includes for system Anaerobic pond, biochemistry pool, sedimentation basin and the sterilization pool that waste water behind natural pond is handled, garbage disposal module further include for natural pond processed The bioactivation pond that biogas residue afterwards is handled;The bottom of pond of the anaerobic pond and sedimentation basin is both provided with and distribution reservoir and/or fast The connection of fast methane-generating pit with anaerobic pond and sedimentation basin bottom are gathered the bottom muddy water of large amount of organic be sent to the distribution reservoir and/or Quick methane-generating pit simultaneously makes it participate in the connecting pipe for recycling natural pond processed.
4. refuse disposal system according to claim 1 or 2, it is characterised in that:Interval siphon erosion and deposition device is arranged with cell The junction of dirty manifold and municipal arterial highway sewage pipe is provided with back-flow preventer, and the back-flow preventer includes the stream along sewage To the inclined tube for tilting down setting;Interval siphon erosion and deposition device further includes the distal end punching for being connected at the easy blocking of neighbouring pipeline At brush.
5. waste disposal method, which is characterized in that include the following steps:The first step, the rubbish that each user generates family crush And it is directly discharged into family's sewer pipe;Second step, by interval siphon erosion and deposition device successively by the rubbish in family's sewer pipe Rubbish flows through cell blowdown manifold and municipal arterial highway sewage pipe is sent into the distribution reservoir in garbage disposal area, interval siphon erosion and deposition with water Device includes interval siphon erosion and deposition pond, for extracting supernatant and the water being sent into the interval siphon erosion and deposition pond in sewage network It pumps and washes away place for being connected to the distal end at its easy blocking of arbitrary sewage network nearby, distally wash away place and interval siphon erosion and deposition It is connected between pond and washes away the solenoid valve whether place washes by water for controlling distal end, it is only necessary to opened solenoid valve and distal end can be used to rush It is washed away at brush at the easy blocking in sewage network;Third walks, be added into distribution reservoir the market of farm produce rubbish that is collected into with COD contents are prepared in pond, the sewage that acid-base value requires suitable for growth methanotrophic bacterial strain, market of farm produce rubbish is first sorted, after crushing It is hydrolyzed under water environment, the hydrolyzate containing large amount of organic is sent in the distribution reservoir after hydrolysis;4th step will match Sewage in pond is added in quick methane-generating pit, and the part in fermentative microorganism fast decoupled sewage in quick methane-generating pit is organic Object generates biogas;Biogas slurry after quick methane-generating pit is transported in methane-generating pit at a slow speed by the 5th step, while into methane-generating pit at a slow speed The food garbage being collected into is added, the fermentative microorganism in methane-generating pit fully decomposes the organic matter in it and generates biogas at a slow speed;The Six steps, the biogas that purified treatment methane-generating pit generates.
6. waste disposal method according to claim 5, it is characterised in that:The rubbish is flowed by municipal arterial highway sewage pipe The sewage for the treatment of region will appear the case where a large amount of drosses swim in upper layer, in the second step, specifically include following steps, step Rapid 201, collect the dross and bulky grain suspended matter in the sewage flowed by municipal arterial highway sewage pipe;It collects by municipal arterial highway sewage The lower water that pipe flows into, large amount of organic accumulates in lower layer and forms bottom sludge in the lower water being collected into;It collects by municipal administration Mid-water in the sewage that arterial highway sewage pipe flows into simultaneously detects concentration of suspension in mid-water, when concentration of suspension is less than setting value When, Anaerobic Treatment is carried out to mid-water, when concentration of suspension is greater than the set value, mid-water is first sent into quick methane-generating pit and is handled Anaerobic Treatment is carried out to it again when being less than setting value to concentration of suspension;
Step 202, the bottom sludge in lower water is sent into the distribution reservoir;The upper layer dross and bulky grain that are collected into are suspended Object is hydrolyzed under water environment, and large amount of organic is deposited on lower layer after hydrolysis, the lower water after hydrolysis is sent into described quick In methane-generating pit;Upper layer is difficult to the object hydrolyzed and is sent into recovery and processing system;
Step 203, supernatant of the sewage in methane-generating pit behind natural pond tentatively processed at a slow speed is collected described in being sent into, supernatant is given birth to The lower water for being populated with large amount of organic is sent into the distribution reservoir after change processing, precipitation.
7. waste disposal method according to claim 6, it is characterised in that:In second step, also needed before step 201 The sewage that garbage disposal area is flowed into from municipal arterial highway sewage pipe is carried out buffered with equalization stable municipal sewage pipe network to The water supply flow of horizontal flow basin in garbage disposal area.
8. waste disposal method according to any one of claims 5 to 7, it is characterised in that:The methane-generating pit packet at a slow speed Medium temperature methane-generating pit and high temperature methane tank are included, the sludge and food garbage in the quick methane-generating pit are transported in medium temperature methane-generating pit Participation natural pond, the biogas slurry after a natural pond end cycle processed in the medium temperature methane-generating pit are sent in the high temperature methane tank system that participates in Natural pond, medium temperature methane-generating pit are sent to biochemistry pool with supernatant of high temperature methane tank after natural pond processed in it and carry out biochemical treatment, production Raw biogas is sent to Marsh gas treatment equipment to carry out the biogas treatment described in the 6th step.
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CN107671104B (en) * 2017-09-15 2021-03-16 佛山科学技术学院 Garbage sorting and resource utilization method
CN109592995A (en) * 2018-12-12 2019-04-09 青岛理工大学 A kind of system and method by residential kitchen waste water and household garbage collaboration processing

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1302699A (en) * 2001-02-28 2001-07-11 王平 Method and facilities for comprehensively treating life garbage, excrement, urine and sewage in urban area to make them become useful resources
EP1136449A1 (en) * 2000-03-21 2001-09-26 SANYO ELECTRIC Co., Ltd. Waste water processing system
US7306731B1 (en) * 2003-08-12 2007-12-11 Daritech, Inc. Manure separation for digester method and apparatus
CN101618926A (en) * 2009-06-24 2010-01-06 杨欣 Urban environment comprehensive treatment scheme

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP1136449A1 (en) * 2000-03-21 2001-09-26 SANYO ELECTRIC Co., Ltd. Waste water processing system
CN1302699A (en) * 2001-02-28 2001-07-11 王平 Method and facilities for comprehensively treating life garbage, excrement, urine and sewage in urban area to make them become useful resources
US7306731B1 (en) * 2003-08-12 2007-12-11 Daritech, Inc. Manure separation for digester method and apparatus
CN101618926A (en) * 2009-06-24 2010-01-06 杨欣 Urban environment comprehensive treatment scheme

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