CN106007285A - Municipal sludge treatment method and heat pump and solar energy coupling system for implementing method - Google Patents

Municipal sludge treatment method and heat pump and solar energy coupling system for implementing method Download PDF

Info

Publication number
CN106007285A
CN106007285A CN201610547946.9A CN201610547946A CN106007285A CN 106007285 A CN106007285 A CN 106007285A CN 201610547946 A CN201610547946 A CN 201610547946A CN 106007285 A CN106007285 A CN 106007285A
Authority
CN
China
Prior art keywords
heat pump
heat
solar energy
sewage
municipal sludge
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
CN201610547946.9A
Other languages
Chinese (zh)
Inventor
王家乐
陈威
周传辉
汪辉
黄凡
黄一凡
许钰彬
王偌楠
朱莹
徐晨翱
周航
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Wuhan University of Science and Engineering WUSE
Wuhan University of Science and Technology WHUST
Original Assignee
Wuhan University of Science and Engineering WUSE
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Wuhan University of Science and Engineering WUSE filed Critical Wuhan University of Science and Engineering WUSE
Priority to CN201610547946.9A priority Critical patent/CN106007285A/en
Publication of CN106007285A publication Critical patent/CN106007285A/en
Pending legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/12Treatment of sludge; Devices therefor by de-watering, drying or thickening
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05FORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
    • C05F17/00Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05FORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
    • C05F17/00Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation
    • C05F17/90Apparatus therefor
    • CCHEMISTRY; METALLURGY
    • C05FERTILISERS; MANUFACTURE THEREOF
    • C05FORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
    • C05F7/00Fertilisers from waste water, sewage sludge, sea slime, ooze or similar masses
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F24HEATING; RANGES; VENTILATING
    • F24SSOLAR HEAT COLLECTORS; SOLAR HEAT SYSTEMS
    • F24S23/00Arrangements for concentrating solar-rays for solar heat collectors
    • F24S23/30Arrangements for concentrating solar-rays for solar heat collectors with lenses
    • F24S23/31Arrangements for concentrating solar-rays for solar heat collectors with lenses having discontinuous faces, e.g. Fresnel lenses
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F24HEATING; RANGES; VENTILATING
    • F24SSOLAR HEAT COLLECTORS; SOLAR HEAT SYSTEMS
    • F24S80/00Details, accessories or component parts of solar heat collectors not provided for in groups F24S10/00-F24S70/00
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F25REFRIGERATION OR COOLING; COMBINED HEATING AND REFRIGERATION SYSTEMS; HEAT PUMP SYSTEMS; MANUFACTURE OR STORAGE OF ICE; LIQUEFACTION SOLIDIFICATION OF GASES
    • F25BREFRIGERATION MACHINES, PLANTS OR SYSTEMS; COMBINED HEATING AND REFRIGERATION SYSTEMS; HEAT PUMP SYSTEMS
    • F25B30/00Heat pumps
    • F25B30/06Heat pumps characterised by the source of low potential heat
    • 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
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A40/00Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
    • Y02A40/10Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
    • Y02A40/20Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses
    • 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
    • Y02E10/00Energy generation through renewable energy sources
    • Y02E10/40Solar thermal energy, e.g. solar towers
    • 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
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/10Process efficiency
    • Y02P20/129Energy recovery, e.g. by cogeneration, H2recovery or pressure recovery turbines
    • 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
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/10Process efficiency
    • Y02P20/133Renewable energy sources, e.g. sunlight
    • 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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/30Wastewater or sewage treatment systems using renewable energies
    • Y02W10/37Wastewater or sewage treatment systems using renewable energies using solar energy
    • 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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/40Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse

Abstract

The invention relates to the field of municipal sludge drying, in particular to a municipal sludge treatment method and a heat pump and solar energy coupling system for implementing the method. The municipal sludge treatment method comprises the steps that municipal sludge is dried, wherein heat used for drying comes from heat, collected by a wastewater source heat pump, of wastewater, heat collected by a gas source heat pump after waste gas generated in the wastewater treatment process is heated with solar energy and heat collected by solar vacuum pipes; the sludge is dried until the water content is 68-72%, closed fermentation is carried out, and fertilizer is obtained. The invention further provides the heat pump and solar energy coupling system for implementing the method. According to the municipal sludge treatment method and the heat pump and solar energy coupling system for implementing the method, energy is generated with the resources in a wastewater plant and solar energy, dried sludge is composted and turned into wealth, the obtained fertilizer is inorganic fertilizer and can be widely applied, and remarkable economic value is achieved.

Description

A kind of municipal sludge processing method and the heat pump-solar energy coupled system of enforcement the method
Technical field
The present invention relates to municipal sludge drying field, in particular to a kind of municipal sludge process side Method and the heat pump-solar energy coupled system of enforcement the method.
Background technology
By the end of the year 2014, whole nation the planned city, county (abbreviation cities and towns) add up to build up sewage treatment plant 3717, sewage treatment capacity 1.57 billion cubic meters/day, relatively 2013 newly-increased about 800 ten thousand steres / sky.Sludge quantity as sewage disposal by-product is also sharply increasing, and according to statistics, current China produces per year Up to 40,000,000 tons (being generally more than 98% with water content), the mud of the most about 80% is without properly for amount Process.Secondary pollution can be caused to environment, wherein mud after entering environment without the appropriate mud processed Moisture content causes cost of transportation increase, stacking big, the pressing waste landfill yard storage capacity of area etc. one compared with high meeting Series of problems.
For reducing moisture percentage in sewage sludge further, current Sewage Plant mainly uses the method for sludge drying.Dirty Mud drying technique is to use artificial heat, and its operation temperature (for mud granule) is typically larger than 100 DEG C, acted on by diafiltration or evaporation etc., from mud, remove major part water content thus reach the degree of depth Dehydration (its moisture content can be controlled in less than 20%).Sludge drying is the process of a Net Energy expenditure, Energy expenditure height, therefore, how the sludge drying that carries out of environmental protection and energy saving is to have problem to be solved.
In view of this, the special proposition present invention.
Summary of the invention
The first object of the present invention is to provide a kind of municipal sludge processing method, and this technique collects dirt The heat of water, waste gas and solar energy, this heat of collection, for the mummification of mud, saves the energy; And the mud after mummification carries out compost, the fertilizer obtained is inorganic fertilizer, it is achieved that municipal sludge Recycling treatment.
The second object of the present invention is to provide a kind of heat pump implementing described municipal sludge processing method -solar energy coupled system, this device arranges simply, collects energy effective, it is easy to industrial applications.
In order to realize the above-mentioned purpose of the present invention, spy by the following technical solutions:
A kind of municipal sludge processing method, by municipal sludge drying, the heat that described mummification is used comes Coming from sewage uses the waste gas produced in the heat of sewage source heat pump collection, sewage disposal process through too The heat that sun is collected with heat and the solar energy vacuum tube of air supply heat pump collection after heating;
Sludge drying to water content is 68%-72%, and sealed fermenting obtains fertilizer.
The present invention utilizes Sewage Plant homegrown resource to carry out production capacity, specifically, extracts in waste gas, waste water Low potential energy, is converted into high level heat, is applied in sludge drying, is substantially reduced mud drying process Power consumption, reaches energy-conservation purpose.
Specifically, sewage is a kind of renewable heat resource containing abundant Lowlevel thermal energy, uses heat pump This Lowlevel thermal energy is converted into high level heat, and utilizes this heat energy that mud in factory is carried out mummification, Heat energy is utilized nearby.Not only the heat energy of sewage can utilize, the heat energy in the distributed waste gas of Sewage Plant Also can utilize.Sewage Plant is in running, and each processing unit all can produce foul smell, waste gas Processing and the most increasingly paid attention to by technical staff, the most more widespread practice is to add a cover, by air inducing Power traction is to exhaust treatment system.And the present invention before exhaust-gas treatment by collect waste gas through solar energy liter Temperature, then by heat pump techniques, this heat energy is applied to sludge drying, after the utilization of this technology also can reduce The load of continuous odor treating device, and, solar energy provides energy as supplementary energy for Sewage Plant, Safely cleaning.Additionally also setting up solar energy vacuum tube, the heat of collection is also simultaneously used for the mummification of mud. The present invention utilizes heat pump-heliotechnics to couple institute's heat production can carry out drying and other treatment to mud, and mud is aqueous Rate is substantially reduced, and whole process make use of the energy and the sun that Sewage Plant self runs off to greatest extent The heat of energy, it is achieved that the clean energy-saving of mud drying process produces.
Further, the mud being cured to certain water content is carried out compost by the present invention, turns waste into wealth, The fertilizer obtained is inorganic fertilizer, can extensively apply, and has significant economic worth.
For now, main research of technique point is to improve Solar use, and Fresnel Lenses is made It is greatly improved the focusing of sunlight for a kind of solar energy condenser lens, improves solar energy utilization ratio with this. Preferably, the thermal source heating described waste gas is mainly derived from Fresnel Lenses gathering sunlight collection Heat.
Due to sewage complicated component and instability, the sewage of employing is usually through pretreated, to the greatest extent So, owing to the internal structure of heat pump is the most complicated, not easy cleaning, therefore, the present invention is by sewage for pipe First passing through centrifugal sewage heat exchanger to process, it solves well containing bigger float, granule or thing The medium of body causes the situation that heat exchanger blocks, and avoids the cleaning taken time and effort simultaneously, and The heat making waste water middle-low grade is fully applied.Preferably, described sewage first passes through centrifugal sewage heat change Device processes, then uses sewage source heat pump to collect heat.
Compost is actual is exactly a kind of form of garbage stabilisation, need specific humidity, temperature and Aeration condition, so that probiotics produces, makes Organic substance constantly be degraded and stablize, and produces a kind of suitable It is suitable for the process of the product of Land_use change.Municipal sludge after drying and other treatment, then is carried out heap by the present invention Fertile, it is achieved the recycling of mud, this technology can not only effectively process mud, moreover it is possible to is made into tool There is the fertilizer of high added value, be truly realized the disposal of resources of garbage.
Experiment proves that, further, the temperature of fermentation is 15-25 DEG C, and the time of fermentation is 25-35 My god.After the fermentation of the certain time under this temperature conditions, the fertilizer obtained and inorganization fertilizer efficiency Fruit is consistent.
Further, the fertilizer obtained after fermentation adds in the mud after mummification as additive, mixing After ferment.
Containing probiotics in the fertilizer that fermentation obtains, add in mud, the fermentation speed of mud can be accelerated Degree, shortens the fermentation time of fertilizer.
Further, mud is stirred by sweat the most up and down and the step smashed to pieces.This mistake Journey is the process of " turning over a heap of manure or a compost heap and pile it up afresh ", by this process, fermentation can be made more abundant and uniform, and pass through Of short duration aerobic processes, and increases the amplification of probiotics, promotes the quality of the fertilizer that fermentation obtains.
Present invention also offers the heat pump-solar energy coupled systemes of municipal sludge processing method described in enforcement System, including: including: sewage source heat pump, exhaust gas source heat pump, solar energy vacuum tube, sludge drying fill Put, installation for fermenting;
Described sewage source heat pump, exhaust gas source heat pump, solar energy vacuum tube fill with described sludge drying respectively Put connection;
Described mud drying device is connected with described installation for fermenting.
Heat pump-solar energy the coupled systemes of the municipal sludge processing method described in enforcement that the present invention provides System, sets gradually each device, simple, beneficially efficiently the carrying out of sludge handling process.
Wherein, mud drying device typically uses drying baker.
Further, described heat pump-solar energy coupled system also includes gas collecting apparatus and Fresnel Lenses, The energy that described Fresnel Lenses is collected is the heating of gas in described gas collecting apparatus, and described gas collection fills Put and be connected with described exhaust gas source heat pump.
Further, described heat pump-solar energy coupled system also includes centrifugal sewage heat exchanger, described from Heart sewage heat exchanger is connected with described sewage source heat pump.I.e. sewage first passes through the process of centrifugal sewage heat exchanger, Enter back into sewage source heat pump, solve Jie containing bigger float, granule or object the most well Matter causes the situation that sewage source heat pump blocks, and avoids the cleaning taken time and effort simultaneously, and makes The heat of waste water middle-low grade is fully applied.
Further, described installation for fermenting includes the first fermentation cabin and the second fermentation cabin.
First fermentation cabin and the second fermentation cabin, will switch once by mud in two fermentation cabin, it is achieved The step stirred up and down and smash to pieces of mud.
Be furnished with on the downside of drying baker in the present invention heat pump heat distribution system, expansion valve, cold-producing medium, blower fan with And pipeline, all there is airduct to be connected between heat pump with drying baker, airduct is provided with volume damper, Being provided with air flow sensor in heat pump, air flow sensor is all connected with controller with volume damper; It is additionally provided with the Temperature Humidity Sensor to drying baker on controller, can come according to the humiture in drying baker Regulate the air quantity on each system airduct so that under conditions of drying system is in closed circulation, not with External environment is connected.
Compared with prior art, the invention have the benefit that
(1) on the basis of sewage treatment plant is existing, the coupling of heat pump-heliotechnics is applied to sewage, The thermal energy collecting of waste gas the municipal sludge producing sewage treatment plant carry out drying and other treatment, it is achieved that energy Source utilizes nearby, is to realize the effective way that integrated wastewater utilizes;After mummification, mud carries out compost again, Obtained fertilizer is similar to inorganic fertilizer, it is achieved that the disposal of resources of garbage.
(2) water outlet after the waste water i.e. second pond discharged after Sewage Plant is processed by sewage source heat pump carries Take its low temperature heat energy, by sewage source heat pump unit, be promoted to high temperature heat and be used for sludge drying, The secondary being achieved in sewage utilizes, and turns waste into wealth, and improves the utilization rate of resource.
(3) each stage of sewage treatment plant can produce substantial amounts of waste gas, and waste gas can distribute stench, Can have undesirable effect the resident of staff and surrounding, whole sewage disposal is produced by the present invention Gas sampling gets up, and utilizes Fresnel Lenses more effectively direct light and the scattered light of sunlight to be filled Divide and utilize, improve capacity usage ratio, gas is heated, then gas is utilized air source heat as thermal source Its low level heat energy collected by pump, by waste gas Appropriate application, and reduces the load of follow-up odor removal, Reach the purpose of pretreatment.
(4) on the one hand by tradition greenhouse dry technology, in conjunction with the development of automatic technology in the present age, Use this clean energy resource of solar energy as the portion of energy source of sludge drying.
(5) sludge composting technology is constantly to be degraded by the Organic substance of mud and stablize, the fertilizer prepared Material is similar to inorganic fertilizer, can extensively apply, it is achieved that the recycling treatment of mud.
Accompanying drawing explanation
In order to be illustrated more clearly that the embodiment of the present invention or technical scheme of the prior art, below by right In embodiment or description of the prior art, the required accompanying drawing used is briefly described.
The schematic diagram of the municipal sludge processing method that Fig. 1 provides for the present invention.
Detailed description of the invention
Below in conjunction with embodiment, embodiment of the present invention are described in detail, but this area skill Art personnel are it will be appreciated that the following example is merely to illustrate the present invention, and are not construed as limiting the present invention Scope.Unreceipted actual conditions person in embodiment, the condition advised according to normal condition or manufacturer Carry out.Agents useful for same or instrument unreceipted production firm person, being can be by commercially available purchase acquisition Conventional products.
A kind of municipal sludge processing method, by municipal sludge drying, the heat that described mummification is used comes Coming from sewage uses the waste gas produced in the heat of sewage source heat pump collection, sewage disposal process through too The heat that sun is collected with heat and the solar energy vacuum tube of air supply heat pump collection after heating;
Sludge drying to water content is 68%-72%, and sealed fermenting obtains fertilizer.
1, the heat that sewage source heat pump is collected
The main operational principle of sewage source heat pump is as follows:
By sewage source heat pump compressor assembly, consume a small amount of electric energy, in the winter time being stored in water Lowlevel thermal energy " extracts " out, for user's heat supply, then indoor heat " is extracted " summer Come, be discharged in water, thus reduce room temperature, reach the effect of refrigeration.Its energy Flow is to utilize Whole heat energy (i.e. the heat energy of electric energy+absorption) one that source pump institute consumed energy (electric energy) draws Play row and transport to high temperature heat source, and play institute's consumed energy effect is to make media collapse to High Temperature High Pressure shape State, thus reach to absorb the effect of heat energy in low-temperature heat source.
The present invention use sewage be generally the trade effluent after two stage treatment.While it is true, Trade effluent composition is the most complicated and unstable, and owing to the internal structure of heat pump is the most complicated, is difficult to clear Washing, therefore, sewage first passes through centrifugal sewage heat exchanger and processes, and it solves well containing the most outstanding The medium of float, granule or object causes the situation that sewage source heat pump blocks, and avoids time-consuming consumption simultaneously The cleaning of power, and make the heat of waste water middle-low grade fully apply.Therefore, in the present invention Use first passes through the process of centrifugal sewage heat exchanger through pretreated trade effluent, then uses sewage Heat collected by source heat pump.
Sewage water heat pump AOF calculation:
Heating energy coefficient 1.33, heating energy coefficient 0, cooling energy coefficient 0.66, refrigerated energy-saving system Several 0.If unit sewage quantity is with 105m3Meter, utilizing the sensible heat temperature difference is 5 DEG C, then may utilize cold and hot amount and be 2.1×109KJ.Can be calculated by above-mentioned data and formula: during heating, primary energy (coal-fired) can be saved, Be equivalent to 71.3 tons (22800 yuan) coal-fired.Primary energy (combustion gas) can be saved, be equivalent to 40.7 tons (48800 yuan) combustion gas.During refrigeration, primary energy (coal-fired) can be saved, be equivalent to 19 ton (6100 Unit) coal-fired.Primary energy (combustion gas) can be saved, be equivalent to 10.5 tons of (12600 yuan) combustion gas.
With 1000m3/ h sewage calculates, and when the sewage temperature difference is 5 DEG C, extractible heat is 5800kw, If carrying out heat production by combustion standard coal about to need to consume 5000kg.The sewage of 100,000 tons is processed by this calculating Day, production capacity was up to 580000000kw.
2, waste gas uses air supply heat pump to collect heat
Sewage Plant is in running, and each processing unit all can produce foul smell, and the process of waste gas the most more comes More being paid attention to by technical staff, the most more widespread practice is to add a cover, air-introduced machine cause waste gas Processing system.And the present invention before exhaust-gas treatment by collect waste gas through solar temperature rising, specifically, Fresnel Lenses is used to be collected solar energy, with Fresnel Lenses as a kind of solar energy condenser lens It is greatly improved the focusing of sunlight, improves solar energy utilization ratio with this, the temperature of the waste gas after heating About 40 DEG C.The energy of collection is not directly used in the mummification of mud but first adds by Fresnel Lenses Hot waste gas, then by heat pump techniques, this heat energy is applied to sludge drying, the purpose of do so is to improve The stable supply of the sludge drying energy.It addition, the utilization of this technology also can reduce follow-up Odor control dress The load put, and, solar energy provides energy, safely cleaning as supplementary energy for Sewage Plant.
Being computed, the waste gas of the Fresnel Lenses heating of 10m × 10m can be collected through air supply heat pump Heat is 3870kwh.
3, the heat that solar energy vacuum tube is collected
Also setting up solar energy vacuum tube, the heat of collection is also simultaneously used for the mummification of mud, the most The clean energy resource utilizing solar energy.
Solar energy uses vacuum tube heat absorbing, and air thermally contacts with vacuum tube as heat-carrying agent, band Walk the sun heat wave that vacuum tube absorbs.Calculating according to the medium regional areas of China's solar energy resources, year is too Sun radiation amount is 5850~6680MJ/m2, it is contemplated that with day amount of radiation 4.5~5.1kW h/m2, vacuum tube Area is according to 144m2Calculating, every day can produce the heat of about 740kwh.According to standard fire coal Energy balane, the heat that standard coal burning produces is 7000 kilocalories/kilogram be converted into joule i.e. 29260J/kg, 740kwh are converted into joule 740 × 103× 3600J obtains the tonnage of coal: 740 × 103× 3600/ (29260 × 1000)=91.0458 ton.
It addition, Fresnel Lenses and solar energy vacuum tube can select suitable size according to demand.
In summary, sewage is a kind of renewable heat resource containing abundant Lowlevel thermal energy, uses heat This Lowlevel thermal energy is converted into high level heat by pump, and utilizes this heat energy that mud in factory is carried out mummification, Heat energy is utilized nearby.Not only the heat energy of sewage can utilize, the heat energy in the distributed waste gas of Sewage Plant Also can utilize.Sewage Plant is in running, and each processing unit all can produce foul smell, waste gas Processing and the most increasingly paid attention to by technical staff, the most more widespread practice is to add a cover, by air inducing Power traction is to exhaust treatment system.And the present invention is special through solar energy by the waste gas of collection before exhaust-gas treatment It not that the energy that Fresnel Lenses is collected heats up, then by heat pump techniques, this heat energy is applied to dirt Mud mummification, the utilization of this technology also can reduce the load of follow-up emission-control equipment, and, solar energy Energy, safely cleaning is provided for Sewage Plant as supplementary energy.Additionally also set up solar energy vacuum tube, The heat collected also is simultaneously used for the mummification of mud.
As can be seen here, the present invention utilizes the heat production of heat pump-heliotechnics coupling institute can do mud Change processes, and draws materials nearby, comprehensively extracts the low potential energy in waste gas, waste water, be converted into high level heat, And use solar energy, and it being applied in sludge drying, whole process make use of Sewage Plant certainly to greatest extent The energy of body loss and the heat of solar energy, be substantially reduced the power consumption of mud drying process, reaches joint The purpose of energy, it is achieved that the clean energy-saving of mud drying process produces;And also reduce follow-up waste gas The load of processing means.
Further, the mud after mummification is carried out compost by the present invention, and compost is actual is exactly that garbage is steady A kind of form of fixedization, needs specific humidity, temperature and aeration condition so that probiotics produces, Make Organic substance constantly be degraded and stablize, and produce the process of a kind of product being suitable for Land_use change. Municipal sludge after drying and other treatment, then is carried out compost by the present invention, it is achieved the recycling of mud, should Technology can not only effectively process mud, moreover it is possible to is made into the fertilizer with high added value, really realizes The disposal of resources of garbage.So sludge composting is one not only will not damage environment but also can resource return Economical treatment technology.
Embodiment 1
A kind of municipal sludge processing method, comprises the following steps:
Take municipal sludge, be put in drying baker;
Sewage uses the waste gas produced in the heat of sewage source heat pump collection, sewage disposal process through luxuriant and rich with fragrance alunite Heat and solar energy that your lens are collected with air supply heat pump after assembling the heat of sunlight collection are true The heat that blank pipe is collected imports drying baker, for sludge dehydrating and drying;
Sludge drying to water content is 68%, and airtight normal temperature fermentation obtains fertilizer in 35 days.
Embodiment 2
A kind of municipal sludge processing method, comprises the following steps:
Take municipal sludge, be put in drying baker;
Sewage sewage heat exchanger by centrifugation uses sewage source heat pump to collect heat, the heat of collection after processing It is passed through drying baker by heat pipe;
Fresnel Lenses assembles the waste gas that the heat gas collecting apparatus of sunlight collection is collected, after heating Waste gas air supply heat pump collect heat be passed through drying baker by heat pipe;
The heat that solar energy vacuum tube is collected imports drying baker by heat pipe;
Drying baker is by controlling the heat sludge dehydrating and drying in the inner of separate sources;
Sludge drying to water content is 70%, adds the fertilizer that embodiment 1 prepares, and addition is mud The 1% of weight, after mixing, airtight normal temperature fermentation obtains fertilizer in 28 days.
Embodiment 3
A kind of municipal sludge processing method, comprises the following steps:
Take municipal sludge, be put in drying baker;
Sewage sewage heat exchanger by centrifugation uses sewage source heat pump to collect heat, the heat of collection after processing It is passed through drying baker;
Fresnel Lenses assembles the waste gas that the heat gas collecting apparatus of sunlight collection is collected, after heating Waste gas air supply heat pump collect heat be passed through drying baker;
The heat that solar energy vacuum tube is collected imports drying baker;
Control the heat of separate sources for sludge dehydrating and drying;
Sludge drying to water content is 72%, adds the fertilizer that embodiment 1 prepares, and addition is mud The 1% of weight, puts into the first airtight normal temperature fermentation of fermentation cabin 15 days after mixing, then ferment first Mud in storehouse stirs and smashs to pieces and be transferred to the second fermentation cabin up and down, then ferments 10 days and obtain fertilizer.
The fertilizer that embodiment 1-3 prepares is verified, the same inorganic fertilizer of fertilizer performance obtained, should Fertilizer is used for farmland, can increase organic matter, improve Soil structure, reduces the use of existing fertilizer Amount, and the potential erosion of soil can be alleviated, it is achieved that the resource application of mud.
The present invention directly utilizes the sewage after Sewage Plant two stage treatment and the produced waste gas low temperature as heat pump Thermal source, so near heat user, saves the energy consumption of conveying heat, thus improves the economy of its system. Solar collecting device as auxiliary energy supply is taked, with Fresnel Lenses and solar energy vacuum tube, to promote The utilization rate of the sun.In current this energy crisis, under conditions of ecological deterioration, sludge composting is because of it There is no secondary pollution, turn waste into wealth, because its biochemistry again realizing resource will become a new generation's mud Newly warding off for the treatment of technology, can realize reducing discharging and can producing economic benefit, kill two birds with one stone.
Although illustrate and describing the present invention with specific embodiment, but it will be appreciated that and do not carrying on the back May be made that in the case of the spirit and scope of the present invention many other change and amendment.Therefore, This means all these changes including belonging in the scope of the invention in the following claims and repair Change.

Claims (10)

1. a municipal sludge processing method, it is characterised in that by municipal sludge drying, described dry Change heat, sewage disposal process that the origin of heat used uses sewage source heat pump to collect in sewage The waste gas of middle generation after solar energy heating with air supply heat pump collect heat and solar energy vacuum tube The heat collected;
Sludge drying to water content is 68%-72%, and sealed fermenting obtains fertilizer.
Municipal sludge processing method the most according to claim 1, it is characterised in that heating is described The thermal source of waste gas is mainly derived from Fresnel Lenses and assembles the heat of sunlight collection.
Municipal sludge processing method the most according to claim 1, it is characterised in that described sewage First pass through centrifugal sewage heat exchanger to process, then use sewage source heat pump to collect heat.
4. according to the municipal sludge processing method described in any one of claim 1-3, it is characterised in that The temperature of fermentation is 15-25 DEG C, and the time of fermentation is 25-35 days.
5. according to the municipal sludge processing method described in any one of claim 1-3, it is characterised in that The fertilizer obtained after fermentation adds in the mud after mummification as additive, ferments after mixing.
6. according to the municipal sludge processing method described in any one of claim 1-3, it is characterised in that The step in sweat, mud stirred the most up and down and smash to pieces.
7. heat pump-the solar energy of enforcement municipal sludge processing method described in any one of claim 1-6 Coupled system, it is characterised in that including: sewage source heat pump, exhaust gas source heat pump, solar energy vacuum tube, Mud drying device, installation for fermenting;
Described sewage source heat pump, exhaust gas source heat pump, solar energy vacuum tube fill with described sludge drying respectively Put connection;
Described mud drying device is connected with described installation for fermenting.
Heat pump the most according to claim 7-solar energy coupled system, it is characterised in that described Heat pump-solar energy coupled system also includes gas collecting apparatus and Fresnel Lenses, and described Fresnel Lenses is collected Energy heating of gas in the described gas collecting apparatus, described gas collecting apparatus and described exhaust gas source heat pump Connect.
Heat pump the most according to claim 7-solar energy coupled system, it is characterised in that described Heat pump-solar energy coupled system also includes centrifugal sewage heat exchanger, and described centrifugal sewage heat exchanger is with described Sewage source heat pump connects.
10., according to the heat pump described in any one of claim 7-9-solar energy coupled system, its feature exists In, described installation for fermenting includes the first fermentation cabin and the second fermentation cabin.
CN201610547946.9A 2016-07-13 2016-07-13 Municipal sludge treatment method and heat pump and solar energy coupling system for implementing method Pending CN106007285A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201610547946.9A CN106007285A (en) 2016-07-13 2016-07-13 Municipal sludge treatment method and heat pump and solar energy coupling system for implementing method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201610547946.9A CN106007285A (en) 2016-07-13 2016-07-13 Municipal sludge treatment method and heat pump and solar energy coupling system for implementing method

Publications (1)

Publication Number Publication Date
CN106007285A true CN106007285A (en) 2016-10-12

Family

ID=57108733

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201610547946.9A Pending CN106007285A (en) 2016-07-13 2016-07-13 Municipal sludge treatment method and heat pump and solar energy coupling system for implementing method

Country Status (1)

Country Link
CN (1) CN106007285A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107056005A (en) * 2016-12-30 2017-08-18 武汉芳笛环保股份有限公司 A kind of efficient low-consume mud drying device
CN113526824A (en) * 2021-07-06 2021-10-22 绍兴市上虞区供水有限公司 Heat energy and solar energy linkage drying sludge treatment equipment and process
WO2021253659A1 (en) * 2020-06-17 2021-12-23 石文政 Solar sludge drying and sludge composting combined treatment method and device

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103359904A (en) * 2012-09-28 2013-10-23 山东华城城建设计工程有限公司 Sludge drying system combining sewage source heat pump with solar energy

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103359904A (en) * 2012-09-28 2013-10-23 山东华城城建设计工程有限公司 Sludge drying system combining sewage source heat pump with solar energy

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
杨柳燕 等主编: "《环境微生物技术》", 31 August 2003, 科学出版社 *
董永胜 著: "《有机固体废弃物的处理及应用技术研究》", 30 September 2015, 中国水利水电出版社 *

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107056005A (en) * 2016-12-30 2017-08-18 武汉芳笛环保股份有限公司 A kind of efficient low-consume mud drying device
WO2021253659A1 (en) * 2020-06-17 2021-12-23 石文政 Solar sludge drying and sludge composting combined treatment method and device
CN113526824A (en) * 2021-07-06 2021-10-22 绍兴市上虞区供水有限公司 Heat energy and solar energy linkage drying sludge treatment equipment and process

Similar Documents

Publication Publication Date Title
CN101239773B (en) Heat pump and sludge drying integration method and system
Gaballah et al. Enhancement of biogas production by integrated solar heating system: A pilot study using tubular digester
CN102500604B (en) Household solid garbage recycling and renewable biological carbon circulating technology
CN101844859B (en) Complete steam low-temperature thermally tempering and drying device and method for sludge
CN201186893Y (en) Heat pump and sludge dewatering integrated system
CN103359904A (en) Sludge drying system combining sewage source heat pump with solar energy
CN203768195U (en) Bio-drying and dehumidification heat pump coupled flap tower type sludge drying system
CN104150732B (en) A kind of mud two-stage anhydration system
CN101239771A (en) Water source heat pump and sludge anaerobic assimilation integration method and system
CN106007285A (en) Municipal sludge treatment method and heat pump and solar energy coupling system for implementing method
CN105948454A (en) Treatment method for industrial sludge and heat pump-solar coupling system implementing method
CN201186892Y (en) Water source heat pump and sludge anaerobic digestion integrated system
CN109264954A (en) A kind of solar energy heat conducting oil desiccation domestic sludge is the preparation method of fuel
CN108007107A (en) A kind of solar energy desiccation factory concurrent heating system and application method
CN201753303U (en) Steam low-temperature quenching and tempering complete sludge drying device
CN102992570A (en) Electric-regenerative solar energy assisted sludge biodrying system
CN101007743A (en) Garbage methane processing and resource utilization machine set
CN202188770U (en) Smoke and waste heat comprehensive utilization device of annular kiln
CN204174056U (en) A kind of mud two-stage anhydration system
WO2021253659A1 (en) Solar sludge drying and sludge composting combined treatment method and device
CN203653407U (en) Energy-saving sludge drying device using solar energy and afterheat
CN207451916U (en) A kind of new energy recycling sludge system
CN218115266U (en) Heat pump-solar energy coupling system for treating industrial sludge
CN207313414U (en) Utilize the sludge anhydration burning device of solar energy
CN107522382A (en) A kind of sludge drying-incineration integrated system using solar source

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
RJ01 Rejection of invention patent application after publication

Application publication date: 20161012

RJ01 Rejection of invention patent application after publication