WO2014079135A1 - 餐厨垃圾全方位处理的集成化装备及产物制造方法 - Google Patents
餐厨垃圾全方位处理的集成化装备及产物制造方法 Download PDFInfo
- Publication number
- WO2014079135A1 WO2014079135A1 PCT/CN2013/000146 CN2013000146W WO2014079135A1 WO 2014079135 A1 WO2014079135 A1 WO 2014079135A1 CN 2013000146 W CN2013000146 W CN 2013000146W WO 2014079135 A1 WO2014079135 A1 WO 2014079135A1
- Authority
- WO
- WIPO (PCT)
- Prior art keywords
- water
- kitchen waste
- oil
- air
- treatment system
- Prior art date
Links
Images
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE
- B09B3/00—Destroying solid waste or transforming solid waste into something useful or harmless
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE
- B09B5/00—Operations not covered by a single other subclass or by a single other group in this subclass
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10L—FUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
- C10L1/00—Liquid carbonaceous fuels
- C10L1/02—Liquid carbonaceous fuels essentially based on components consisting of carbon, hydrogen, and oxygen only
- C10L1/026—Liquid carbonaceous fuels essentially based on components consisting of carbon, hydrogen, and oxygen only for compression ignition
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10L—FUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
- C10L5/00—Solid fuels
- C10L5/40—Solid fuels essentially based on materials of non-mineral origin
- C10L5/48—Solid fuels essentially based on materials of non-mineral origin on industrial residues and waste materials
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/10—Biofuels, e.g. bio-diesel
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/30—Wastewater or sewage treatment systems using renewable energies
- Y02W10/37—Wastewater or sewage treatment systems using renewable energies using solar energy
Definitions
- the invention discloses an integrated equipment for omnidirectional treatment of kitchen waste and a product manufacturing method thereof.
- the invention belongs to the technical field of comprehensive treatment of domestic garbage, and relates to an integrated device and a manufacturing method, a recipe and a process for the waste processing of a kitchen waste, and at the same time Involved in microbiology, biochemistry, equipment manufacturing, optoelectronics, ozone applications, functional plastics, plastic reversal engineering, clean coal, mineral fuel manufacturing, biomass fuel manufacturing, cleaner production, air purification, sewage treatment and many other technical fields.
- the science and technology of waste resource utilization after a long period of application, has proved that if the waste recycling technology is applied in a single application, the consequences will bring greater crisis to the human living environment, especially The serious problem of secondary pollution is difficult to control, so the comprehensive treatment of waste has become the current development trend.
- the composition of kitchen waste is extremely complicated, including sewage, plastic bags, plastic bottles, waste cloth strips, spoilage organic matter, paper, metal bottles, broken glass, broken ceramic sheets, animal fats, vegetable oils, primary bacteria and other substances. .
- the kitchen waste resource treatment technology has presented a “hundred flowers” situation in the domestic and foreign methods and processes, but basically it is a simple single item treatment, and there is no international environmental treatment that shifts from simple treatment to comprehensive treatment, utilization and disposal.
- the trend and direction may cause the inevitable attachments in the kitchen waste to be transferred and randomly filled, causing water and soil pollution, or transfer, not only blocking the city's sewer pipes, but also emitting a foul smell and causing serious secondary pollution.
- the single treatment process of kitchen waste is feasible from the perspective of resource utilization value. However, considering the comprehensive protection of the global environment, people's livability and protection of the atmospheric environment, it may still do more harm than good.
- the present invention provides a large-scale highly integrated kitchen waste comprehensive processing equipment and application mode and production The process and formula are in line with the current international development direction of the residue after the waste resource treatment.
- a comprehensive kitchen and garbage processing system the system includes a kitchen garbage bag breaking device, a kitchen garbage combined screening device, a wet advanced oxidation deodorizing inactivation cleaning salt reducing device , vertical dewatering device, material crusher and automatic control device, the kitchen waste is put into the kitchen garbage bag breaking device for bag breaking treatment, and then input into the kitchen garbage combined screening device for joint screening, and the filtered oil-water solid mixture is input.
- the wet-type advanced oxidation and deodorization inactivation cleaning and salt-reducing device is inactivated, and the kitchen waste which has been deactivated and dehydrated by wet advanced oxidation is sent to the dehydration device by the screw conveying pipeline, and dehydrated by the dehydration device.
- the material is input into the material crusher for pulverization, and the automatic control device controls the operation of other devices.
- a method for producing a transformant using the above-described kitchen waste comprehensive treatment system comprising the following steps
- the material after dehydration is pulverized by a material crusher.
- the cutting device comprises a horizontal cylindrical casing, one end of the casing is a discharge port, and the outer casing is provided with one or more cutters on one end of the discharge port, and the other end of the casing is arranged to slide along the inner cavity of the casing.
- the piston is connected with a power tool for pushing the piston, and a sipe is arranged on the piston corresponding to each tool position, and a feed port is opened at the middle of the top of the casing.
- the bottom of the piston is mounted with a pulley, and the bottom of the inner wall of the outer casing is fixedly provided with a concave sliding rail corresponding to the position of the pulley, and the pulley can slide back and forth on the concave sliding rail.
- a collecting box is arranged at the position of the feeding port, the upper part of the collecting box is funnel-shaped, the lower part is connected with the feeding port on the outer casing through the blanking pipe, and the pneumatic sliding gate valve is arranged on the discharging pipe.
- a rolling cleat is mounted on the outlet of the casing, and the motor drives the rolling cleat to rotate.
- the rolling cleat is square or polygonal and is provided with an inner cavity.
- the rolling clapper plate is provided with more than one compressed air ejection slot on each surface, and the rolling clapper plate is provided with a compressed air air guiding tube and a gas injection nozzle, and the gas injection nozzle is connected to the compressed air air guiding tube, and the jet direction of the gas injection nozzle The same direction as the discharge of the discharge port.
- the compressed air injection slots are arranged in parallel.
- the blade of the tool has a 90 degree angle to the cross section of the housing discharge opening or a 30 degree angle to the inner wall of the outer casing.
- the kitchen and kitchen garbage combined screening system comprises a casing, wherein the casing is provided with a partition plate, and the inside of the casing is divided into an air floating zone and a non-air floating zone through a partition plate, and the partition plate is provided with a material leakage outlet, the gas
- a feeding port at the floating area a heavy material discharging outlet at the lower part of the air floating area, a valve at the heavy material discharging outlet, one or more air nozzles around the heavy material discharging outlet, and a tumbler on the upper part of the air floating area
- a material output device in the non-air floating area one end of the material output device is arranged in the casing, the other end is arranged outside the casing, the material output device is provided with auger, the material output device is equipped with a motor and a transmission, and the motor is matched with The transmission drives the auger to rotate.
- the material leakage outlet is provided with a louver guide groove, the louver guide groove is connected to the pneumatic propulsion rod, the pneumatic device drives the propulsion rod movement, and the propulsion rod controls the opening and closing of the louver guide groove.
- the roller is provided with two, two rollers are arranged one above the other, and the lower roller is 1/2 The position is set in the liquid level of the air floating zone, and the upper roller is disposed above the liquid level of the air floating zone, and the two rollers are engaged with each other.
- a rolling motor is mounted on the casing, and the rolling motor simultaneously drives the two rollers to rotate.
- a transmission is mounted at the material outputter, and the motor drives the auger to rotate through the transmission.
- a liquid level automatic control device for controlling the liquid level is installed at the air floating area.
- the casing is provided with a pipe for conveying kitchen waste into the casing, and the pipe is connected to the water inlet pipe.
- the circulating water inlet of the air floating zone is connected with a hydraulic pressure pump, the water source is provided by the circulating water storage tank, and the water outlet is provided in the middle and lower part of the non-air floating zone, and the water body is input into the circulating water storage tank through the water pump for the gas
- the circulation of the water in the floating zone and the non-air-floating zone and the strengthening of the water in the air-floating zone are strongly tumbling.
- the kitchen waste oxidation, deodorization, inactivation, cleaning and salt reduction device comprises more than one reactor and a gas, water and material mixer for ozone-water-material mixing, and the mixer is connected with waterproofing.
- One-way valve, one end of the waterproof check valve is connected to the gas pipe, and then connected to the ozone generating device.
- the mixer is also connected with a high-viscosity cam rotor pump outlet.
- the outlet of the mixer extends into a reactor, and the high-viscosity cam rotor pump
- the inlet is connected to another reactor, and more than one granular activated carbon reaction sphere is arranged in the reactor, granular activated carbon is arranged in the granular activated carbon reaction sphere, and a material outlet is arranged at the bottom of the reactor.
- the total volume of the particulate activated carbon accounts for 15% to 98% of the volume of the granular activated carbon reaction sphere.
- the top of the reactor is provided with an automatic exhaust valve, and an ozone destroyer is connected to the automatic exhaust valve.
- the bottom of the reactor is provided with a semi-circular head, and the material outlet is arranged on the semi-circular head.
- the front end of the reactor is provided with a beveled ribbon conveyor, and the reactor at the rear end is provided with a water level height regulating pipe.
- a solid and liquid separator is connected to the material outlet.
- the solid-liquid separator comprises a casing and a slanted mesh barrel, wherein the inclined mesh barrel is disposed in the outer casing, and the inclined mesh barrel is rotated by the motor in cooperation with the transmission, and the front end of the inclined mesh barrel is provided with more than one row.
- the mesh hole and the inclined mesh barrel are provided with a spiral ribbon connected to the inner wall of the mesh barrel, and a water receiver is arranged at the bottom of the shell.
- the spiral ribbon occupies the entire length of the inclined mesh barrel.
- the outer casing is provided with a window.
- the side of the reactor is equipped with a manhole.
- the vertical dewatering device comprises a casing, a vertical inner leakage tower and a ribbon propulsion rod, the vertical inner leakage tower is arranged inside the outer casing, the spiral propulsion rod is arranged inside the vertical inner leakage tower, and the vertical inner leakage tower side
- the bottom of the vertical inner leakage tower is provided with a feed inlet
- the top of the vertical inner leakage tower is provided with a discharge port
- the bottom of the outer casing is provided with a power source for driving the rotation of the propeller rod
- the inside of the outer casing corresponds to
- a water tank is arranged around the bottom of the vertical inner leakage tower, and a water outlet is connected to the water tank.
- more than one water pipe is arranged around the vertical inner leakage tower, and more than one high pressure water recoil nozzle is connected to each water pipe.
- the top of the vertical inner leak tower is provided with a shaft fixing plate for mounting a screw push rod.
- the end of the ribbon on the ribbon push rod is provided with a sealing plate for adjusting the discharge speed.
- the spacing of the ribbons on the ribbon push rod is gradually narrowed from the lower portion toward the top of the tower.
- the pitch of the lower end of the ribbon on the ribbon push rod is 25 CM, and the distance between the terminals is 10 CM.
- the power source includes a motor, a transmission, and a steering conversion device that converts the horizontal axial rotation into a vertical axial rotation.
- the motor drives the transmission to rotate
- the transmission drives the steering conversion device to rotate
- the steering conversion device drives the ribbon push rod to rotate.
- a stainless steel bearing sleeve is disposed in the outer casing.
- More than one stainless steel vertical plate is arranged around the outer side of the vertical inner leakage tower, and more than one reinforcing ring sleeve is arranged around the stainless steel vertical plate, and each reinforcing circle is provided with a slope anti-backlash guiding flow.
- the vertical inner leakage tower is composed of more than one tower body, each tower body is provided with a reinforcing flange at an upper and lower circumferential position, and the connection of adjacent tower bodies is abutment between the upper and lower flanges of the tower body, and Bolted, the upper flange of the joint flange position of each tower body is equipped with a bevel anti-backlash guide.
- the biochemical fermentation device comprises an anaerobic fermentation tank and a main fermentation device
- the main fermentation device comprises two sub-fermenters and more than one main fermenter, two sub-fermenters are arranged above the main fermenter, and the secondary fermentation
- the ribbon agitator, the anaerobic fermentation tank is connected to the main fermenter, and the anaerobic fermentation tank feeds the material into the main fermenter through an automatic unloading system.
- the double-layer ribbon agitator comprises a shaft body, an inner layer ribbon and an outer ribbon, the inner layer ribbon is disposed inside the outer layer ribbon, and the inner layer ribbon and the outer layer ribbon are spirally belt-shaped, and They are fixedly mounted on the shaft body respectively, and the inner spiral belt and the outer spiral belt have opposite spiral directions, and the double-sided ribbon stirrer is provided with a braided blade around the shaft body.
- the mixing device is a main shaft in the middle, and more than one stirring blade is fixedly mounted on the central shaft.
- the material of the anaerobic fermentation tank is provided with an automatically movable material agitator.
- the automatic unloading multi-stage drying device comprises a pre-drying device and a main drying device, wherein the pre-drying device is installed above the main drying device, and the pre-drying device shell is on both sides, and the outer casing interlayer of the pre-drying device is formed between the two sides.
- the pre-drying device is provided with an automatic material turning plate, and the central drying device is a horizontal cylindrical body capable of rotating 360 degrees in the reverse direction.
- the front and rear ends of the main drying device are respectively fixed heads and horizontal cylindrical bodies.
- the combustion chamber and the burner, the heat generated by the burner passes into the interior of the main drying device, and the exhaust gas of the main drying device is input into the inner cavity of the outer casing through the hot air discharge port, and the material output port of the pre-drying device corresponds to the innermost side of the main drying device.
- Secondary cylinder setting
- the bottom of the pre-drying device is provided with a screw auger automatic discharge device, and the screw auger automatic discharge device has a cylindrical shape, and a screw auger is arranged inside.
- the top of the pre-drying device is provided with a drafting device.
- the respective sub-cylinders are set together, and the material inlet of the outer sub-cylinder is longer than the material outlet of the inner sub-cylinder.
- Airflow disturbing fins are fixedly mounted on the outer side walls of the respective sub-cylinders.
- the horizontal cylindrical body and the guide spirals inside the respective secondary cylinders are opposite in direction.
- the material selection device comprises a base, a metal rolling screen cylinder, a material carrier, an automatic conveying tool, a chain plate conveyor and a diverter shutter, the metal rolling screen cylinder is mounted on the base, and the material carrier is arranged on the metal rolling Below the screen cylinder, the automatic conveying tool is arranged under the material carrier, the front end of the metal rolling screen cylinder is provided with a mesh hole, the rear end is provided with a spiral belt, and the chain conveyor is arranged below the discharge opening of the metal rolling screen cylinder.
- the splitter shutter is placed at the end of the chain conveyor.
- the mesh hole diameter is 4 mm - 6 mm, and the interval between the hole and the hole is 2 mm.
- the metal rolling screen cylinder is inclined, and the inclination angle is 1 degree - 20 degrees.
- the diverter shutter is provided with an adjusting device for adjusting the height between the diverter shutter and the chain plate conveyor.
- a protective cover is mounted on the outer side of the metal rolling screen cylinder.
- the kitchen garbage combined screening device is provided with a plastic solid output end, and the plastic solid output end of the kitchen garbage combined screening device is connected with a waste plastic reverse engineering device.
- the waste plastic reverse engineering device mainly swings the main processing device, and the main processing device feeds the material into the pneumatic automatic feeding machine by the conveyor belt, and feeds the material into the cracking catalytic horizontal reaction kettle through the pneumatic automatic feeding machine.
- the reactor can be rotated 360 degrees and reversely.
- the reactor is equipped with an automatic random scraping device.
- the reactor is connected with a vacuum system.
- the reactor is connected to the oil wax separator through a pipeline.
- the oil wax separator is connected with a first-stage heavy oil separator through a pipeline, and the first-stage heavy oil separator is connected with a first-stage condenser through a pipeline, and the oil-bearing container is connected to the bottom of the first-stage condenser, after the first-stage condenser
- the end is connected with a negative pressure device, the back end of the negative pressure device is connected with a vertical water-sealed gas safety conveyor, and the rear end of the vertical water-sealed gas safety conveyor is connected with a secondary gas compressor, a secondary gas compressor and a gas
- the repository is connected.
- the bottom of the reaction kettle is provided with a cracking furnace, and the gas outlet pipe of the cracking furnace is connected with the tail gas environmental protection equipment system.
- the oil carrying container is connected with a carbon removal rinser and a dewaxing glue remover.
- the system further includes a coarse carbon black processing device connected to the residual slag outlet of the waste plastic reversing engineering device.
- the crude carbon black processing device comprises a crude carbon black artificial aging processor, the crude carbon black artificial aging processor is connected with the physical aging bed, and the physical aging bed is connected with the material matching device by an automatic conveying tool, and the material matching device
- the liquid and solid automatic dosing feeding device is connected to the upper part, and the back end of the material matching device is provided with a multi-layer push-pull screw, and the back end of the multi-layer push-pull screw is connected with the low-sulfur high-energy environmentally-friendly clean coal forming machine.
- the system further includes a distillation-free biodiesel production device, wherein each device separates the oil, water, and solid mixture through oil and water through a pipeline, and then feeds the distillation-free biodiesel production device.
- the distillation-free biodiesel production system comprises a horizontal spiral belt solid-liquid separation device, an oil-water separation tower, an oil storage container, a grease colloid removal device, a bio-oil normal temperature grease exchange device, a liquid separation device and a filtration device, and a lying device.
- the outlet of the spiral ribbon solid-liquid separation device is connected to the lower end of the oil-water separation tower through a pipeline, and the oil-water separation tower is provided with a heating pipeline, and the heating pipeline extends from the lower part of the oil-water separation tower to the inside of the oil-water separation tower, and then from the upper part of the oil-water separation tower
- the output is output to the outside of the oil-water separation tower, and the oil-water separation tower is provided with an oil scraper at the top of the oil-water separation tower.
- the oil-water separation tower is connected to the oil storage container through the oil-discharging pipeline, and the oil outlet pipeline inlet corresponds to the oil scraper setting, and the oil storage container passes through the pipeline and the grease colloid.
- the device for removing the device is connected, and the grease colloid removal device is internally provided with a hole impact plate fixedly disposed, and the rotary hydraulic propeller is respectively installed at the corresponding positions on both sides of the impact plate, and the propeller blade of the rotary hydraulic propulsion machine is disposed at
- the motor is arranged outside the grease gel removal device, the motor drives the propeller blade to rotate, and the grease gel removal device
- the grease outlet is connected to the bio-oil normal temperature grease exchange device through the pipeline, and more than one ultrasonic generator is arranged in the bio-oil normal temperature grease exchange device, and the bio-oil normal temperature grease exchange device has a feed port at the top, and the bio-oil normal temperature
- the bottom of the grease exchange device is connected to the liquid separation device through a pipeline, and the bottom of the liquid separation device is connected to the filtration device through an oil pipeline, and the filtration device outputs biodiesel.
- the horizontal spiral belt solid-liquid separation device comprises a horizontal cylindrical outer casing, a filter mesh is arranged in the outer casing, a conveying screw is fixed inside the filter mesh, and the spiral belt driving motor cooperates with the transmission to drive the filter mesh and the spiral belt.
- Rotating, horizontal spiral belt solid-liquid separation equipment is provided with an oil and water mixture output pipe at the bottom.
- the top of the oil-water separation tower is equipped with an infrared water body liquid level locator.
- the outer periphery of the ultrasonic generator is respectively provided with a sleeve, and an inner threaded jet hole is arranged around the sleeve, and a locking device is fixed on the sleeve, and the ultrasonic generator is installed in the bio-oil normal temperature grease exchange device through the locking device. .
- the bio-oil normal temperature grease exchange device is provided with a liquid guiding tube, one end of the liquid guiding tube is connected to the upper part of the bio-oil normal temperature grease exchange device, and the other end is connected to the bottom of the bio-oil normal temperature fat exchange device, and the liquid guiding tube is connected Pump.
- the bottom of the bio-oil normal temperature grease exchange device is provided with a gas pipe, and one end of the gas pipe is connected to the compressed air machine.
- the system further includes an oil gel removal device, and the special oil pump inputs the bio-fat from the oil storage container into the grease gel removal device and then enters the grease exchange device.
- the system also includes the manufacture of an emulsified biodiesel device, the bio-fat from the lipid exchange process being exported to an emulsified biodiesel device.
- the emulsified biodiesel manufacturing device comprises a casing, a vertical agitator is arranged in the casing, the power source drives the vertical agitator to rotate, and the vertical agitator has more than one paddle type straight mixer or paddle folding on the central shaft of the vertical agitator.
- the blade paddle and the lower part of the vertical shaft of the vertical agitator are equipped with a turbine or disc curved blade slurry, and the top of the casing is provided with more than one feeding port, and each feeding port is connected with a quantitative feeding device through a pipe, the casing
- the lower part is provided with a finished product discharge port.
- the upper part of the casing is cylindrical and the lower part is semicircular.
- More than one liquid guide vane is mounted around the cylindrical inner wall of the housing.
- a support frame for a rotating shaft supporting a vertical agitator is mounted on the bottom of the housing.
- the power source includes a motor and a shifting device, the shifting device is fixedly mounted on the top of the housing, the motor is disposed above the shifting device, and the motor drives the vertical agitator to rotate through the shifting device.
- the system also includes a rapid sewage treatment recycling device, and the sewage generated by each device is connected to the rapid sewage treatment recycling device through a pipeline.
- the rapid sewage treatment and recycling device comprises a sewage filtration tank, a sewage barrier is arranged in the sewage filtration tank, and an anti-plug recoil is arranged in the debris barrier, and the sewage filtration tank is connected with the hot felt sewage treatment device through the water inlet pipe.
- the hot felt sewage treatment equipment comprises an inner cavity and a casing, and the top of the casing is provided with a plurality of atomizing spray heads communicating with the inlet pipe, and a burning felt is arranged under the atomizing spray head, and a heat conducting oil pipe is arranged inside the burning felt.
- the bottom of the hot felt is provided with a micro-solid sedimentation zone, and the bottom of the micro-solid sedimentation zone is provided with a sewage outlet, and an anti-fouling recoil baffle is arranged above the sewage outlet, and a high-temperature cushion for supporting the hot felt is arranged under the hot felt
- the top of the casing is provided with an automatic suction and exhaust valve, and the casing is located above the hot felt with a hot steam collecting port, and the hot steam collecting port is connected to the heat exchanger through a pipe, and the rear end of the heat exchanger is connected with a collecting pool.
- the pool is connected to the advanced oxidation system through the pipe section.
- the advanced oxidation system has two inner and outer cavities, the inner cavity is a gas-water reaction cavity, the outer cavity is a gas-water circulation reaction buffer cavity, and the inner cavity inlet is introduced into the end of the pipe.
- Activated carbon reaction ball activated carbon reaction ball is filled with granular activated carbon
- the bottom of the inner cavity is provided with a sewage outlet
- the sewage outlet is connected with the sewage outlet of the outer casing
- the anti-backlash plate is also installed on the sewage outlet of the inner cavity
- the advanced oxidation reactor passes
- the circulating pipe is connected with a gas-water mixer, the gas-water mixer is a three-way connection, the circulating water is connected at both ends, and one port in the middle is connected with the waterproof one-way valve, and the other port of the waterproof one-way valve is connected to the ozone generator.
- the gas pipeline, the advanced oxidation system is connected with a transfer tank, and the transfer tank is connected with an activated carbon filter fixed bed, the activated carbon filter fixed bed is connected with a composite filter device, and the composite filter device includes more than one filter tank.
- Each filter column has a water outlet hole at half of the length of the filter column.
- the bottom of the filter column is equipped with a filter screen of 80-140 mesh.
- the top of the filter tank has a water inlet and
- the pressurized tube and the filter tank are divided into two layers, and each layer of the tank is respectively provided with a filter column tray, and the filter column holder has an orifice matched with the diameter of the filter column, and the filter column is inserted in the filter column holder.
- the upper side of the upper tank is provided with a water guiding pipe
- the inlet guiding pipe leads to the upper part of the lower tank
- the lower side of the upper tank is provided with a water guiding pipe
- the outlet guiding pipe leads to the lower layer.
- the lower part of the tank body is respectively provided with an exhaust port on the upper and lower sides of the tank body
- the water outlet of the filter tank is disposed on one side of the bottom seal head of the composite filter device, and a sediment discharge port is arranged at a center position of the bottom seal head.
- the surface of the hot felt is provided with a plurality of shallow shallow water channels.
- the top of the inner chamber is equipped with an automatic exhaust valve and a liquid level control online monitor for monitoring the liquid level.
- the upper portion of the activated carbon reaction sphere is impervious to water, and the lower part is a mesh outlet.
- the volume of activated carbon in the activated carbon reaction sphere accounts for 15% to 95% of the volume of the reaction sphere.
- the system further includes a hybrid charged adsorbent production device for treating the remaining solid sludge, and the sludge generated in each section is input to the hybrid charged adsorbent production device.
- the system further includes an exhaust gas environmental treatment device that centrally treats the flue gas, hot flue gas, dust, and the like generated in each process.
- the exhaust gas treatment system comprises a preliminary purification device, a water-solid mixer, a twin-tower rotary spray system and a flue gas discharge device, the preliminary purification device comprising an air buffer and a primary flue gas treatment pipe, and the exhaust gas is introduced into the air.
- the buffer is input into the primary flue gas treatment pipeline through the air buffer, discharged into the water-solid mixer through the primary flue gas treatment pipeline, and the water-solid mixer outlet is connected into the double-tower rotary sprinkler system.
- the tower rotary sprinkler system is processed and input into the flue gas discharge equipment, and then discharged through the flue gas discharge equipment.
- the air buffer comprises a cylindrical outer casing, and more than one water curtain ejection opening is arranged on the upper side of the outer casing, and a sewage outlet is arranged at the bottom of the outer casing.
- the preliminary purification device further includes a sedimentation tank, and the sewage outlet is connected to the sedimentation tank through the pipe section.
- a pipe section is connected to the sewage outlet, and the pipe section is connected to the upper part of the sedimentation tank, and the upper part of the sedimentation tank is connected to the air buffer through the pump and the pipe section.
- An on-line level monitor for detecting the liquid level inside the air buffer is also mounted above the air damper.
- the primary flue gas treatment pipeline is provided with more than one negative ion-charged ceramic, and each negative ion-charged ceramic rear end is correspondingly equipped with a high-speed water mist zone nozzle.
- a baffle is mounted on the rear end of each of the high-speed water mist nozzles.
- the deflector adopts a concave obtuse angle deflector.
- the negative ion-charged ceramic is mounted on the left, right, and upper sides of the primary flue gas treatment pipe.
- the exhaust gas treatment system further includes a cooling tower that cools the hot water in the heat exchanger in the flue gas discharge device.
- the system further comprises a plasma photocatalyst negative ion air deodorizing and sterilizing device for generating air which is treated as air at the male end and air in the production area, and an air inlet of the plasma photocatalyst negative ion air deodorizing and sterilizing device is installed around each kitchen garbage collecting pool.
- the plasma photocatalyst negative ion air deodorization and sterilizing device comprises an air conveying pipeline, a photocatalytic main processor and an activated carbon air filter, a gas input air conveying pipeline, an negative ion device in the air conveying pipeline, and a gas passing through the air conveying pipeline
- the photocatalytic main processor is provided with an air passage, and the air passage is equipped with more than one ultraviolet light tube with an emission wavelength of 253 nm - 258 nm, and the rear end of the ultraviolet light tube is fixedly installed with titanium dioxide light
- the catalytic contact plate is connected to the activated carbon air filter at the end of the air passage, and the gas is output through an activated carbon air filter.
- An air discharge pipe is connected between the photocatalytic main processor and the activated carbon air filter, and an negative ion device is arranged in the air discharge pipe, and the air passage end is connected with the air discharge pipe, the air discharge pipe and the activated carbon air filter Connected.
- the negative ion device adopts a negative ion corrugated plate, and the negative ion corrugated plate is stackedly installed.
- the negative ion corrugated plate is provided with two sections, the front section is horizontally installed, and the rear section is vertical installation.
- the front end of the air conveying pipe is provided with an air inlet, and an automatic sliding gate valve is installed at the rear end of the air inlet.
- the back surface of the ultraviolet light pipe is equipped with a light reflecting plate.
- the air passage in the photocatalytic main processor is Z-shaped.
- the size and shape of the titanium dioxide photocatalytic contact plate coincides with the cross section of the air passage and can be just blocked in the air passage.
- the titanium dioxide photocatalytic touch panel is of a honeycomb type.
- the titanium dioxide photocatalytic touch panel has a thickness of 1 cm - 10 cm and has more than one hole.
- the pulverized material in the step E is subjected to biochemical treatment by a biochemical treatment device, and then dried by an automatic unloading multi-stage drying device, and then subjected to multi-stage drying and material selection to form a mixed feed.
- the biochemical treatment includes the following steps:
- the pre-fermented material is generated by the simultaneous action of the anaerobic fermentation tank and the two auxiliary fermenters;
- the materials in the two sub-fermenters are sent to the main fermenter through the automatic conveying equipment provided at the bottom of the auxiliary fermenter, and the materials in the anaerobic fermentation tank are also passed through the automatic unloading system. Feeded into the main fermenter for secondary fermentation;
- the pre-fermented material When the pre-fermented material is formed in the anaerobic fermentation tank, it will account for 50% of the weight of the total fermentation base - 80% of the bean seed stalk and 20% of the total fermentation base weight - 50% of the timber
- the current season orange stalk of the crop is broken into a powder having a particle diameter of 0.5 mm to 1 mm, and a composite bacterium capable of decomposing the crude fiber is added to biochemically treat the mixture material, and the bacterial strain of the composite bacterium has not less than two One kind of Aspergillus oryzae, the compounding agent is input in an amount of 1% of the mixed solid base, and the chemical components calcium oxide, sodium chloride, sodium hydrogen phosphate and urea are added.
- the artificially inactivated kitchen waste is added to the auxiliary fermenter as the base material, and the bran and the base material are added in an amount of 1% to 2% by weight of the base material.
- 1% - 3% of rice bran and 1% of the weight of the base of sugar as a mixture, and add appropriate amount of water to make a paste the temperature is controlled between 20 ° C - 30 ° C range
- adding 2% - 4% of the bread yeast to the mixture, and fully stirring and strengthening the aeration to enhance the growth of the yeast the fermentation method can adopt the old fermentation method.
- the solid fermentation is carried out by adding the artificially inactivated, washed and dehydrated kitchen waste to the secondary fermenter, and the green wood mold and the tropical silk are selected.
- Yeast, white fungus and endophytic yeast consist of a mixture of four bacteria, the weight ratio of four bacteria is 2:2:1:1, the inoculum is 2% of the total weight, and the total weight is added 1%- - 1.5% urea, temperature 25 ° C - 42 ° C, tumbling once per hour by a stirring device, fermentation time 9 hours - 10 hours.
- the material that has been pre-biochemically processed is input into the main fermenter, and the percentage of the total material weight in the straw fermentation material is 10%-40%, and the baker's yeast fermentation material accounts for 20% of the total material weight percentage.
- the fermentation material in the second sub-fermenter accounts for 40%-70% of the total material weight.
- the waste plastic produced in the step B is reversed by the waste plastic reverse engineering device to generate biodiesel.
- the raw slag crude carbon black artificial aging processor produced by the biodiesel uses aging to grind the material, and then passes through the chemically aged coarse carbon black to enter the physical aging bed, and the crude carbon black is artificially aged.
- the special automatic conveying tool is used to input the material compatibility equipment.
- Each of the compatibility aids is added by the liquid and solid automatic quantitative feeding equipment.
- the material is fully mixed into the low-sulfur high-energy environment-friendly clean coal-forming machine through the multi-layer push-pull screw. After the material is formed, a crude carbon black is obtained.
- the sewage generated in the steps A to E is treated by the rapid sewage treatment and recycling device, and discharged or reused.
- the solid sludge treatment produced in the steps A to E is treated by the hybrid charged adsorbent production device to form a hybrid charged adsorbent.
- the flue gas, the hot flue gas, the dust and the exhaust air generated in the steps A to E are discharged by the environmental treatment device.
- the treated gas is discharged through a plasma photocatalyst negative ion air deodorizing and sterilizing device.
- the oil-water mixture produced in the steps A to E is produced by the distillation-free biodiesel production method, and the method comprises the following steps:
- the bio-fat is sent into the grease colloid removal device by a pump or the like, and then the hydro-pneumatic propulsion machine is started, and the phosphoric acid having a concentration of 85% is added.
- the ratio of phosphoric acid to bio-fat is not more than 1% of the total amount of grease.
- the grease is used to remove the liquid from both ends of the device to cause the colloidal grease to remove the liquid inside the device.
- the impact time is 10 Min——15min, after the end of the phase collision time of the liquid, the diluted brine is added immediately.
- the weight ratio of water to salt in the dilute brine is between 95:5 and 90:10, and the weight ratio of bio-fat to dilute brine is 90: Between 10 and 80:20;
- the biological grease mixture is input into the liquid separation device to be statically layered, the upper layer is a mixed liquid of methanol and glycerin, and the lower layer is crude biodiesel;
- the liquid separation device is set to be opened at the lower liquid discharge port, and the crude biodiesel is transported into the filtering device, and the purified biodiesel is obtained after filtration and the solid catalyst is recovered.
- the oil-water mixture in the oil-water separation tower is heated to 60° C. to 85° C., after the bio-oil is floated, the oil moisture layer is realized, and the upper layer of bio-oil is scraped by the scraper and passes through the oil pipeline. Feed into the oil storage container.
- the cosolvent is selected from methyl alcohol, and the cosolvent is added in an amount of 0.5% to 2% by mass of the bio-fat.
- the co-solvent further comprises butanol added in an amount of 0.5% by mass of the bio-fat.
- the solid anionic metal base catalyst is characterized by reagent activated carbon and nanoparticles of silicate minerals of aluminum, sodium, iron and lithium as a base nucleus, and then wrapped with silicon, aluminum and lithium mesh skeleton medium. And a hybrid carrier with polarity, and the carrier is immersed in the KNO3 liquid, and treated to become a hybrid charge with polarity, a solid anionic metal base catalyst containing 15% - 25% KNO3 .
- the biodiesel is made into emulsified biodiesel by a microemulsified biodiesel manufacturing device, and the method comprises the following steps:
- the crude biodiesel is input into the above micro-emulsified biodiesel device, the stirring system is started, 30%-80% of the national standard diesel oil is added, and the mixture is stirred for 5 minutes;
- the hydrophilic agent is a composite active agent selected from a cationic surfactant and a nonionic surfactant, and the ratio is 50% of a cationic surfactant and 50% of a non-cationic surfactant.
- the surfactant is triethanolamine or hexahydroaniline or cetrimonium bromide and aqueous ammonia.
- the water is added in an amount of 10% to 20% by weight based on the total weight.
- the octadecano-cis-9-enoic acid set amount has an acid value of 200.
- the beneficial effects of the invention are as follows: 1.
- the integrated equipment and method for comprehensively treating the kitchen waste according to the application of the present invention is a comprehensive integration of domestic and foreign kitchen processing industry for the first time with high integration, automation and comprehensiveness.
- the equipment is compatible with the method of resource-based treatment of the inevitable attachment of kitchen waste, adapts to the trend of the international environmental protection industry, and implements the safe disposal and disposal direction of the residue after the centralized treatment of waste is not transferred and digested.
- the application of the invention provides kitchen waste and its inevitable attachments - waste plastic bags, drowning sludge and domestic sewage in the plant, industrial sewage and sludge produced in the production process, various large systems in the same equipment The processing method in the device.
- the application of the present invention provides various high value-added product names, manufacturing methods and uses thereof after the comprehensive recycling of the kitchen waste.
- the application of the invention provides a comprehensive energy-saving production, safe production, no residue transfer treatment for the kitchen waste treatment industry, no room temperature discharge, no odor emission close to the clean production method and mode without sewage discharge.
- the products produced by the invention are National III mineral diesel, low sulfur and high calorific value clean environmental protection coal, and gas three strategic energy sources, which can alleviate the pressure of social supply and demand.
- the high-nutrition microbial protein feed additive produced can effectively fill the gap of the lack of high-protein additives in domestic feed.
- the invention provides a novel garbage carrier (barrel) production method capable of naturally sterilizing and deodorizing the kitchen garbage carrier (barrel) and providing clean air around the outer periphery of the barrel, which is an application surface extremely A wide range of new environmentally friendly cleaning appliances.
- FIG. 1 is a schematic flow chart of a core part of a system of the present invention.
- FIG. 2 is a schematic flow chart of the system of the present invention.
- FIG. 3 is a schematic view showing the production process of the energy plastic carrying device of the present invention.
- Figure 4 is a schematic view showing the structure of the collecting device of the present invention.
- Fig. 5 is a perspective view showing the three-dimensional structure of the kitchen waste bag breaking device of the present invention.
- Fig. 6 is a schematic view showing the structure of a cut surface of a kitchen waste bag breaking device according to the present invention.
- Fig. 7 is a schematic cross-sectional structural view of a kitchen waste bag breaking device according to the present invention.
- FIG. 8 is a schematic structural view of a kitchen garbage combined screening device according to the present invention.
- FIG. 9 is a schematic cross-sectional structural view of a kitchen waste combined screening device according to the present invention.
- Figure 10 is a schematic view showing the structure of a wet advanced oxidation, deodorization, inactivation, cleaning and salt reducing device in the present invention.
- Figure 11 is a schematic view showing the structure of a primary solid separator in the present invention.
- Figure 12 is a schematic view showing the structure of a vertical dewatering apparatus in the present invention.
- Figure 13 is a schematic view showing the internal structure of a vertical dewatering apparatus in the present invention.
- Figure 14 is a schematic view showing the structure of a main biochemical treatment device in the present invention.
- Figure 15 is a schematic view showing the structure of a main fermentation apparatus in the present invention.
- Figure 16 is a perspective view showing the structure of the main biochemical treatment device of the present invention.
- Figure 17 is a schematic view showing the structure of the automatic unloading multi-stage drying device of the present invention.
- Figure 18 is a schematic cross-sectional view showing the pre-drying apparatus of the present invention.
- Figure 19 is a schematic view showing the structure of a main drying device in the present invention.
- Figure 20 is a schematic cross-sectional view showing the main drying apparatus of the present invention.
- Figure 21 is a schematic view showing the structure of a selection device in the present invention.
- Figure 22 is a schematic view showing the structure of a mixed feed device of the present invention.
- Figure 23 is a partial structural view of the waste plastic reversal engineering device of the present invention.
- Figure 24 is a partial structural view of the waste plastic reversal engineering device of the present invention.
- Figure 25 is a partial structural view of the waste plastic reversal engineering device of the present invention.
- Figure 26 is a partial structural view of the waste plastic reversal engineering device of the present invention.
- Figure 27 is a schematic view showing the structure of a coarse carbon black processing apparatus in the present invention.
- Figure 28 is a schematic view showing the structure of a water, oil and solid separation device of the present invention.
- Figure 29 is a schematic view showing the structure of a biodiesel production apparatus of the present invention.
- Figure 30 is a schematic view showing the structure of a cut surface of a bio-oil normal temperature fat exchange device according to the present invention.
- Figure 31 is a schematic view showing the structure of the ultrasonic transducer in the present invention.
- Figure 32 is a schematic view showing the structure of an emulsified biodiesel apparatus of the present invention.
- Figure 33 is a partial structural view of the rapid sewage treatment and recycling device of the present invention.
- Figure 34 is a partial structural view of the rapid sewage treatment and recycling device of the present invention.
- Figure 35 is a partial structural view of the rapid sewage treatment recycling device of the present invention.
- Figure 36 is a partial structural view of the rapid sewage treatment and recycling device of the present invention.
- Figure 37 is a partial schematic view showing the structure of a hybrid charged adsorbent production apparatus of the present invention.
- Figure 38 is a partial schematic view showing the structure of a hybrid charged adsorbent production apparatus of the present invention.
- Figure 39 is a partial schematic view showing the structure of a hybrid charged adsorbent production apparatus of the present invention.
- Figure 40 is a schematic illustration of an exhaust gas treatment system of the present invention.
- Figure 41 is a schematic view showing the double-tower wet gas-solid separator of the present invention and its internal structure.
- Figure 42 is a schematic view showing the construction of a primary flue gas treatment pipe in the present invention.
- Figure 43 is a schematic view showing the flue gas discharge system and its internal structure in the present invention.
- Figure 44 is a schematic view showing the construction of a primary flue gas treatment pipe of the present invention.
- Figure 45 is a schematic view showing the structure of a plasma photocatalyst negative ion air deodorizing and sterilizing device in the present invention.
- Figure 46 is a partial structural view showing the gas collection and pretreatment apparatus of the plasma photocatalyst negative ion air deodorizing and sterilizing device of the present invention.
- This embodiment is a preferred embodiment of the present invention, and other principles and basic structures are the same as or similar to those of the present embodiment, and are all within the scope of the present invention.
- the present invention is mainly a comprehensive kitchen waste processing system, which includes a kitchen garbage bag breaking device, a kitchen garbage combined screening device, and a wet advanced oxidation deodorizing and inactivation cleaning device.
- the salt reduction device, the vertical dewatering device, the material crusher and the automatic control device, the kitchen waste is put into the kitchen garbage bag breaking device for bag breaking treatment, and then input into the kitchen garbage combined screening device for joint screening, the filtered oil water
- the solid mixture is input to the wet advanced oxidation and deodorization inactivation cleaning and salt reducing device for inactivation treatment, and the kitchen waste which has been deactivated by dehumidification and desulfurization by wet advanced oxidation is sent to the dewatering device by the screw conveying pipeline through the dewatering device
- the dehydrated material is input into the material crusher for pulverization, and the automatic control device controls the operation of other devices.
- the material input material crusher is further provided with a biochemical treatment device for biochemical treatment, and the biochemically processed materials are input into the pre-drying equipment and the main drying equipment for drying, and then selected by the selected device. After mixing of the mixed feed devices, a feed product is formed.
- the solid waste input from the kitchen waste combined screening device is processed into the waste plastic reverse engineering device, and then the biodiesel is formed by the distillation-free biodiesel production device and the emulsified biodiesel device, and the residual residue is passed through the crude carbon black treatment device. Processed into coarse carbon black.
- the sewage generated by the system is input into the rapid sewage treatment and recycling device, the tail gas input tail gas environmental protection treatment device generated by the system and the plasma photocatalyst negative ion air deodorization sterilization device are processed and discharged, and the sludge generated by the system is input into the hybrid charged adsorbent production device. Hybrid charged adsorbent production.
- the material after dehydration is pulverized by a material crusher.
- the source of the invention is an energy plastic carrying device A, and the kitchen waste is put into the energy plastic carrying device A, and then the energy plastic carrying device A for the kitchen garbage collected by the kitchen garbage collecting point is collected and transported by the special collecting vehicle B. Go to the production and processing workshop.
- the production process steps of the energy plastic carrying device used in the present invention are as follows:
- Aa based on a plastic carrier resin suitable for the manufacture of kitchen waste bins
- ultra-fine anatase titanium dioxide A3 (in this embodiment, the particle size of titanium dioxide is less than 1 ⁇ m) is stirred by a mixer with A4 as energy
- the raw material wherein the weight ratio of the nanometer natural energy stone powder and the carbon black in the energy raw material is 50%-85%: 50%-15%, and the ultrafine anatase titanium dioxide accounts for 10% of the total weight of the mixture- —15%
- the Chinese patent of the applicant application No. 201010154643.3 for the production steps of the energy plastic masterbatch of the present invention, reference may be made to the Chinese patent of the applicant application No. 201010154643.3;
- energy raw material in the drying equipment A5 is kept at a temperature of 100-120 ° C for 1-2 hours, and the dried energy raw material is added to the material of 2% aminosilane or hard fatty acid magnesium which accounts for the specific gravity of the energy raw material.
- Dispersant ;
- the energy raw material to which the dispersing agent has been added is uniformly mixed with the plastic carrier resin and the calcium oxide filler, wherein the weight ratio of the plastic carrier resin to the energy raw material to which the dispersing agent is added is 1:2 to 1:1, the plastic carrier resin and the oxidation Calcium was added in an amount of 20:1.
- the above-mentioned treated materials are mixed into a professional plastic mixing equipment A6 for mixing, and extruded by the extruder A7 to produce a plastic energy masterbatch.
- the Af, plastic energy masterbatch is molded by the injection molding machine A7a according to the geometry of the molding die for manufacturing the kitchen waste-receiving device.
- the kitchen waste-containing device made by the above-mentioned process of the present invention has a long-term release of 5000-12000/cm 3 negative ions regardless of size and shape, and the special structure of natural energy stone powder can make it It emits light with a wavelength of 4-14 microns for a long time. This wavelength of light is suitable for exciting the photons of titanium dioxide in the equipment, so that the garbage-loading equipment can generate photo-reaction process for a long time.
- the energy consumed is for the equipment. Its own body, in line with the principle of conservation of energy.
- the energy plastic kitchen garbage container used in the invention can release a large amount of negative ions for a long time, and has long-term photocatalytic ability, and the generated photogenerated electrons and photoholes have strong energy, far higher than the kitchen
- the strength of the molecular chain of junk organic pollutants can easily decompose organic pollutants into the most primitive state and form a highly effective antibacterial effect.
- the special collection vehicle B transports the kitchen waste to the production processing workshop, and then puts it into the kitchen garbage breaking bag device.
- the main body of the kitchen garbage bag breaking device is a cylindrical outer casing D11.
- the cylindrical outer casing D11 is arranged in a horizontal structure, and the cylindrical outer casing D11 is supported by a support frame (not shown). .
- the cylindrical outer casing D11 is open at one end, and is the discharge port D18 of the present invention, and the other end is blocked.
- the plug is internally provided with a piston D13 capable of sliding back and forth along the cylindrical outer casing D11, and the cross section of the piston D13 and the cylinder
- the cross section of the shaped outer casing D11 coincides.
- the power tool D12 is mounted on the outer side of the cylindrical outer casing D11.
- the power tool D12 is a pneumatic power tool or a hydraulic power tool, that is, a cylinder or a hydraulic cylinder.
- the power tool D12 is connected to the piston D13 through a connecting rod. Through the telescopic movement of the power tool D12, the piston D13 is made to reciprocate linearly in the inner cavity of the horizontal cylindrical casing D11.
- a plurality of sipe D14 is formed on the periphery of the piston D13.
- the bottom of the cross section of the sipe D14 is rectangular, and the top is triangular.
- the number of sipe D14 is suitable for the need of breaking the bag, and can be according to the outer casing D11.
- the diameter is adjusted, and in this embodiment, eight are used.
- a plurality of tools D16 are fixedly mounted, the number of the tools D16 is the same as the number of the sipes D14, and the mounting position of the cutter D16 corresponds to the installation of the sipes D14, that is,
- Each tool D16 corresponds to a sipe D14, and the cross-sectional shape of the tool D16 coincides with the shape of the sipe D14, which can be slightly smaller than the shape of the sipe D14, so that the tool D16 can move freely in the sipe D14, and the cross section of the tool D16 is also
- the bottom has a rectangular shape and the top blade has a triangular shape.
- the cutter D16 can adopt two structural forms, and the installation angle of the blade is at an angle of 90 degrees with the cross section of the discharge port of the cylinder D11, or is 30 degrees from the inner wall. .
- the length of the cutter D16 is about 1/5 of the total length of the cylindrical outer casing D161
- the length of the piston D13 is about 2/5 of the total length of the cylindrical outer casing D11.
- the cutter D16 and the piston D13 The length can be set according to actual needs. When the piston D13 retreats to the end point, the space between the piston D13 and the cutter D16 is the empty position EQ.
- the top position of the cylindrical outer casing D11 in the kitchen waste bag breaking device is provided with a feed port D21, and the feed port D21 is disposed corresponding to the space position D1.
- the kitchen garbage collection box D19 is fixedly mounted at the feed port D21.
- the outer casing of the collection box D19 has a funnel type, which is close to the position of the feed port D21 on the cylindrical outer casing D11.
- a pneumatic slide gate valve 18 is mounted on the blanking pipe D20 for partitioning the odor from the next processing section.
- a concave guide rail D17 is fixedly mounted on a lower portion of the inner wall of the cylindrical outer casing D11, and one or more pulleys D15 are mounted at a position corresponding to the concave guide rail D17 under the piston D13, and the pulley D15 is matched with the concave guide rail D17. It can guarantee that the piston D13 does not deviate from the center point during the action.
- a square rolling clapper D22 is arranged at a position corresponding to the discharge port D18 (also referred to as a non-powered driving end of the casing), and the rolling clapper D22 is provided with kinetic energy by the motor D28 in cooperation with the transmission to drive the rotation thereof, and the rolling clapper D22 is laterally
- the discharge port D18 is mounted on the cylindrical casing D11.
- a plurality of compressed air injection grooves D23 are formed on each side of the rolling frame D22, and the compressed air injection grooves D23 are strip-shaped, and each compressed air The ejection grooves D23 are arranged in parallel.
- the inside of the square rolling clapper D22 is a cavity D25.
- the cavity D25 is internally provided with a compressed air air duct D24 and a gas injection nozzle D26.
- the compressed air air duct D24 is provided with compressed air and can be sprayed by gas.
- the nozzle D26 is ejected, the air jet direction of the gas jet nozzle D26 is the same as the discharge direction of the discharge port D18, the gas is ejected 1-2 times per second, and the air ejected from the gas jet nozzle D26 is ejected through the compressed air ejection slot D23.
- Use a gas jet to blow the plastic bag forward.
- the piston of the main equipment D13 uses a pneumatic tool as a power source to make a straight-line push-pull action in the horizontal direction.
- the square rolling clapper D22 provided at the discharge port D18 also starts to roll at the same time.
- the pneumatic slide gate valve D27 of the discharge pipe D20 of the kitchen garbage collection box D19 is opened, the garbage passes through the discharge pipe D20 from top to bottom, and the feed space position D1 which is presented when the piston D13 of the main device is retracted to the end point.
- the kitchen waste is passed through the feed port D21 during this time, and at the same time enters the empty space D1 of the inner cavity of the main device.
- the piston D13 at this moment pushes the kitchen waste to the front by the push rod action of the pneumatic tool, and the piston D13 is pushed forward, at this time.
- the inner cavity under the mouth D21 is infested by the piston D13, the feed port D21 is closed, and the kitchen waste is pushed by the piston D13 toward the inner cutter D16 of the equipment cylinder casing D11, and is disposed on the outer circumference of the piston D13.
- the sipe D14 allows the blade to penetrate into the sipe D14, and the plastic bag of the kitchen waste is cut by the blade at this time.
- the piston D13 is pushed to the position of the rolling shutter D22 of the discharge port D18, and the broken kitchen garbage receiving bag is strong in the rolling clapper D22.
- the built-in kitchen waste leaks out from the crack of the plastic bag.
- the multi-stage gravitational compressed air set in the rolling clapper D22 passes through the exit slot D23 which is directed to the clapper surface, and the kitchen waste is further taken off.
- the bag, and the gravitational gas jet blows the plastic bag forward, avoiding being covered by the falling kitchen waste, and affecting the next sorting work.
- the splitting device for the kitchen garbage receiving bag in the invention is a production process of converting the kitchen waste into a microbial high-protein feed, and preventing the plastic pieces from being mixed into the feed, and the plastic can be realized by the device.
- the combination of the bag splitting, the smashing of the board, and the blowing of the bag to ensure that the bag is broken into pieces during the bag breaking process of the kitchen waste, especially to break the bag and not break, the kitchen The garbage is removed from the bag and is not covered by the garbage.
- the kitchen waste After the bag is broken, the kitchen waste enters the kitchen and garbage combined screening device, and is filtered.
- the broken kitchen waste is firstly pushed into the magnetic separator as a preliminary screening, and then added to the liquid air flotation sorting device.
- the utility model mainly relates to hydraulic sorting and salt washing of the kitchen waste.
- the kitchen garbage combined screening device of the present invention is mainly used for screening the kitchen waste that has been broken, and It is mainly used for hydraulic sorting and salt washing of kitchen waste. Therefore, this part of the invention is called a water float screening device or a liquid air flotation sorting device.
- the upper part of the casing E11 of the kitchen garbage combined screening device of the present invention has a round barrel shape, and the lower part is composed of an inner hollow cone E18, and the feeding port is arranged at the upper middle part of the casing E11, and the kitchen waste is used by the pipe water flow force. From the exit of the previous section, the air-floating zone E10 inside the casing is pushed from the top to the bottom.
- the water used for the pipeline is the treated water for the sewage treatment system.
- the pipeline is equipped with the inlet pipe E20 near the inlet, and the front end of the inlet pipe E20.
- the hydraulic pressure pump E21 is installed, and the kitchen waste is flushed into the air floating area E10 inside the casing by the action of the hydraulic pressure pump E21.
- the kitchen garbage combined screening device of the present invention is mainly divided into an air floating zone E10 and a non-air floating zone E32, and a partition plate E25 is disposed inside the casing E11.
- the partition plate E25 is disposed inside the casing E11.
- the façade is divided into about 1/3 position, and the inside of the casing is divided into an air floating zone E10 and a non-air floating zone E32, that is, the air floating zone E10 occupies about 2/3 of the inner space of the casing, and the non-air floating zone E32 occupies the interior of the casing.
- the feed port is connected to the upper side of the air floating zone E10.
- a rolling jaw E30 (or a tumbler) is installed at a position near the top of the air floating area E10 near the liquid surface.
- two rolling teeth E30 are provided, and two rolling teeth E30 are installed one above the other. 1/2 of the lower rolling jaws are disposed in the liquid surface, the upper rolling jaws are disposed above the liquid surface, and the two rolling jaws E30 are synchronously driven to rotate by the rolling motor E39.
- the tooth movement trajectories of the two rolling teeth E30 are passed between the mutual tooth positions, that is, when the two rolling teeth E30 rotate, the tooth positions of the first rolling teeth are set at the second rolling ⁇ .
- the tooth position of the second rolling tooth is disposed between two adjacent tooth positions of the first rolling tooth, and the group of rolling teeth E30 is used for kitchen waste.
- the fishing operation and unloading operation when the low-density material in the liquid air-floating process floats on the water surface is mainly used for fishing for light-weight materials such as plastic bags and toothpicks, and the rolling teeth underneath are used to remove plastic bags and toothpicks. Then it is transported away through the rolling jaws above.
- the bottom of the casing E11 is provided with a residue discharge port E22, and the residue discharge port E22 is provided with a valve E23.
- the residue discharge port E22 and the valve E23 are mainly arranged corresponding to the air floating zone E10 for weighting the material.
- the object is removed.
- more than one air nozzle E24 is disposed around the residue discharge port E22, and air is introduced into the water body for performing a tumbling and tumbling action on the water body and the material in the air floating area E10.
- a circulating water pipe E40 is also installed between the non-air floating zone E32 and the air floating zone E10, and one end of the circulating water pipe E40 is a water outlet E41 at one end of the non-air floating zone, and one end of the air floating zone E10 is a water filling port, circulating water
- the pipes are connected through the water storage tank E42 to realize liquid air flotation sorting of the kitchen waste.
- the partition plate E25 is installed with a semi-floating material leakage outlet E26 at a position 20 cm or more from the bottom, and a louver guide groove E27 having an opening upward at the leakage outlet E26, and the groove direction of each louver guide groove E27 is pneumatically mounted.
- the push-pull rod E28 and the pneumatic device E38 push the pneumatic push-pull rod E28 up and down to realize the opening and closing of the louver guide groove E27, and the opening angle control, thereby controlling the semi-floating material, that is, the kitchen which is regarded as useful.
- the garbage enters the non-air floating zone E32.
- the non-air floating zone E32 is another barrel communicating with the air floating zone E10, and the air floating zone E10 and the non-air floating zone E32 are communicated through the leakage outlet E26 of the flat floating layer material.
- the water outlet E41 disposed on one side of the non-air floating zone mainly ensures that the horizontal liquid level of the non-air floating zone E32 is lower than the horizontal liquid level of the air floating zone E10, and enters the reservoir through the output water body.
- the air floating area E10 is replenished, and under the action of the hydraulic pressure pump E21 installed on the water supply pipe, the water body is strongly input into the lower part of the air floating area E10 to strengthen the water body and material tumbling action, and strengthen A useful semi-float enters the non-air-floating zone through the louvered diversion trough E27.
- the lower part of the non-air floating area E32 is provided with a material output device E33, and one end of the material output device E33 is disposed in the non-air floating area E32, and the other end is exposed outside the casing E11, and is exposed on the outer side of the casing E11.
- a discharge port E35 There is a discharge port E35, a material auger E33 is internally provided with a screw auger E37, a discharge motor E36 is fixedly mounted on the outer end of the material output device E33, a transmission E34 is mounted corresponding to the discharge motor E36, and a discharge motor E36 is passed through the transmission.
- the E34 drives the screw auger E37 to rotate, and the material is stirred from the bottom to the top in the non-air floating zone E32, and then discharged from the discharge port E35 to the next section.
- the upper part of the casing E11 is provided with a liquid level automatic control device E29 for controlling the water level in the air floating area E10 to overflow the waterproof body.
- the kitchen waste combined screening device of the present invention is disposed at the lower part of the ground or above the ground, and the food waste that has been broken is pushed into the magnetic separator (the magnetic separator removes iron impurities in the kitchen waste by using a magnet)
- the kitchen waste is pushed into the device by the hydraulic discharge pipe, and the material contains plastic bags, glass bottles, metal sheets, small light wood strips, etc., and the complex kitchen materials are in liquid gas.
- the plastic bag and the lightweight small-shaped wooden strip are pushed to the water surface with the density lower than other materials by the floating force of the air, they are caught by the roll E30 and sent to another roll E30.
- the light material conveying trough enters the waste plastic reversal engineering section or the waste plastic collection chamber, and the glass bottles, glass fragments and metal dense materials in the liquid air floating area E10 sink to the bottom of the air floating area E10, and wait Open the heavy material discharge port E22 at an appropriate time and collect it from the automatic valve E23 and deliver it to the workshop to be treated by the automatic conveying tool.
- the louver guide trough E27 can be opened, so that the flat-floating layer of the high-protein feed can be used to automatically enter the leaking outlet E26 of the louver diversion trough E27 and enter the non-volume.
- the push-pull rod E28 disposed in the louver guide groove E27 is pneumatically controlled, and the opening and closing movement of the guiding trough body E27 can be automatically performed in the set time during the production process, and the air floating area is acted upon.
- the useful material in E10 is delivered to the non-air-floating zone E32.
- the beveled ribbon conveyor E33 starts to start, and while the partial water body is effectively separated, the initially sorted kitchen material is sent to the next station device for further processing. deal with.
- the kitchen-to-garbage combined screening device of the present invention can utilize the opening and closing action of the air flotation and water float, the rolling and the louver diversion trough, and the water level pressure difference between the air floating zone and the non-air floating zone, Plastics, toothpicks, etc. are removed, and the heavy materials such as glass and metal in the kitchen waste are removed by the deposition process, and finally the useful materials are output for further processing to realize automatic screening of the kitchen waste.
- the inclined bevel conveyor starts to start, and while the part of the water body is effectively separated, the initially sorted kitchen material is sent to the next station device, that is, wet advanced oxidation, Deodorization, inactivation, cleaning and salt reduction devices.
- the wet advanced oxidation, deodorization, inactivation, cleaning and salt reducing device in the invention mainly utilizes ozone gas to sterilize and clean the kitchen waste in the water body, and the device is divided into more than one reactor F34, and each reaction
- the device F34 is connected to each other through a pump and a pipe and circulated to each of the reactors F34.
- the number of the specific reactors F34 can be set according to actual needs.
- the reactor F34 has a cylindrical shape and is a stainless steel cavity structure, the lower part of the reactor F34 is a semicircular head F35, the top of the reactor F34 is a semicircular or flat top head F37, and the top of the reactor F34 is sealed.
- An automatic exhaust valve F53 is installed on the head F37, and an ozone destroyer F39 is connected to the automatic exhaust valve F53. The gas in the reactor F34 can be eliminated into the ozone destroyer F39 through the automatic exhaust valve F53, and passed through the ozone destroyer F39.
- a beveled ribbon conveyor F36 is connected to the inlet of the reactor F34, and the sorted kitchen waste is sent to the wet advanced oxidation and deodorization, sterilization, and cleaning by the inclined spiral conveyor F36.
- the beveled ribbon conveyor F36 has a tubular shape, and a conveying screw is disposed inside, and the material is sent to the reactor F34 by the rotation of the conveying screw.
- More than one granular activated carbon reaction sphere F41 is fixedly mounted on the inner periphery of the inner chamber of the reactor F34, and the position is placed in the upper middle portion of the inner chamber of the reactor F34, and the granular activated carbon reaction sphere F41 is a stainless steel mesh shell, and the particle activity is The carbon is encapsulated inside the stainless steel mesh casing.
- the total volume of the granular activated carbon accounts for 15% to 98% of the volume of the active carbon reaction sphere F41 sphere, and the combined application of the granular activated carbon reaction sphere and ozone It can accelerate the conversion of ozone into hydroxyl radicals in the liquid state, and achieve the artificial forced inactivation and deodorization speed of bacteria in the water.
- the top of the inner chamber of the reactor F34 is also equipped with an online liquid level automatic control monitor F40 for monitoring the liquid level in the reactor F34, and the online liquid level automatic control monitor F40 can be realized by a liquid sensor, and The liquid level is adjusted by the water level of the other reactor F34 to control the supply and discharge of the pipe F54.
- a gas, water, and material mixer F42 for ozone-water-mixing of materials is further installed on the outer casing of the reactor F34.
- the mixer F42 is a three-way connection, one end of which is connected to the inner cavity of the reactor F34 through the communication pipe F55, and the other end is connected to the outlet F43 of the high-viscosity cam rotor pump F49, and the center end of the mixer F42 is connected with an air inlet.
- the air inlet is connected to the waterproof check valve F56, and the gas supplied by the ozone generator F44 enters through the air pipe F57 and passes through the waterproof check valve F56, enters the mixer F42 and is strongly mixed with water and material, thereby making the water-
- the kitchen waste-ozone mixture is transported to another reactor F34 through a high viscosity cam rotor pump F49 disposed in a circulation line at the lower portion of the reactor F34 to form a cycle between the two reactors. , control the mixing of the material for continuous oxidation time.
- the above structure is the front structure of the wet advanced oxidation, deodorization, inactivation, cleaning and salt reducing device in the present invention, and the wet advanced oxidation, deodorization, inactivation, cleaning and salt reducing device of the present invention further comprises a rear structure
- the latter part of the advanced oxidation deodorization, sterilization and salt reduction device is a solid and liquid separator.
- the separator is composed of a tilted mesh barrel F52, and the separator front end is connected.
- the barrel F52 is provided with a plurality of rows of mesh holes.
- the mesh diameter is 3-8 mm
- the outer casing F45 is provided outside the barrel F52.
- a window F46 is mounted on the side of the outer casing F45 for viewing the inside of the barrel F52.
- the bottom of the outer casing F45 is provided with a water receiver F47 for receiving the water leaked from the mesh barrel F52, and the entire length of the inclined barrel F52 is provided with a flow guiding screw leading to the discharge port F48, that is, in the inclined mesh shape.
- the full length of the barrel F52 is equipped with a spiral ribbon, and the material is led by the spiral belt.
- the rotating power of the inclined mesh barrel F52 is driven by the AC motor and the transmission, which is not shown in the figure.
- the wet advanced oxidation, deodorization, inactivation, cleaning and salt reduction device is used to put the water and kitchen waste mixture into the reactor F34 through the inclined conveyor F36, and the kitchen waste mixture and the water volume.
- the ratio is 5:7, which is fluid, and is continuously circulated between the inside and the outside of each reactor by a high-viscosity cam rotor pump F49, and ozone gas and water are added to the water-gas mixer F42.
- the kitchen garbage material is forcibly mixed.
- the concentration of ozone in the mixture is 10g/T - 15g/T.
- the mixture is treated with the reaction time in and out of the reactor as the advanced oxidation reaction.
- the whole time is 5min - 15min, due to The ozone is reduced in water at any time, and the chain reaction is initiated under the assistance of the activated carbon reaction sphere to accelerate the conversion of ozone into hydroxyl radicals, similar to the advanced oxidation process of O 3 /H 2 O 2 or O 3 /UV.
- the monoatomic oxygen and hydroxyl OH which produce strong oxidation, artificially inactivate and deodorize the pathogenic bacteria in the kitchen waste and remove the sodium chloride substance.
- the lower valve of the reaction vessel outlet 15A is opened, and the high-viscosity cam rotor pump is used to input the solid and liquid separator for dehydration.
- the ozone can be used for oxidizing, deodorizing and desalting the kitchen waste, preventing the unpleasant smell from being emitted, polluting the air, and at the same time, eating the meal.
- Bacteria, viruses and other microorganisms in the kitchen waste are inactivated to prevent their spread, especially if the kitchen waste needs to be biochemically treated in the next stage, the treatment process is protected from the interference of bacteria.
- the kitchen waste that has been inactivated, deodorized, desalted, and primary dehydrated by wet advanced oxidation is sent to the dewatering device for dehydration by the screw conveying pipe.
- the dewatering is performed by a vertical dewatering device, see FIG. 12 and Figure 13 shows that the vertical dewatering device of the present invention mainly comprises a casing G49, a vertical inner leakage tower G50 and a ribbon propulsion rod G51.
- the outer casing G49 has a vertical cylindrical shape, and the vertical inner leakage tower G50 is provided.
- a stainless steel bearing sleeve G56 is disposed inside the outer casing G49 adjacent to the inner wall of the outer casing G49.
- the vertical inner leakage tower G50 is a vertically mounted upper and lower cone (please refer to the attached Figure 13)
- the vertical internal leakage tower G50 is composed of more than one tower body, each tower body has a truncated cone shape, and each tower body is provided with a reinforcing flange G67 at the upper and lower circumferential positions thereof.
- the connection of the adjacent towers is abutment between the upper and lower flanges G67 of the tower body, and is fixed by bolts G68, and the plurality of tower bodies are spliced into one whole vertical inner leakage tower G50.
- each tower The flange of the top of the body is mounted at the flange position Surface anti-kickback diversion eaves G59.
- a plurality of high pressure water recoil nozzles G53 are arranged around the outer portion of the vertical inner leakage tower G50 in the outer casing G49, and the high pressure water recoil nozzle G53 is mounted on the water pipe G65.
- the water pipes G65 are provided with more than one, each water pipe G65 is vertically disposed inside the outer casing G49 and distributed around the outside of the vertical inner leakage tower G50.
- Each water pipe G65 is provided with more than one high pressure water recoil nozzle G53 for cleaning the vertical inner leakage tower G50. Anti-clogging.
- the ribbon push rod G51 is disposed inside the vertical inner leak tower G50 and conforms to the internal shape of the vertical inner leak tower G50.
- the middle of the ribbon push rod G51 is a spiral rotating shaft, and the rotating shaft is provided with a propeller screw and a screw.
- the shaft spacing of the belt is gradually narrowed from the lower 25CM to the top of the tower, and the terminal spacing is 10CM.
- a motor G54 and a transmission G64 are mounted on the outer side of the outer casing G49.
- the motor G54 drives the transmission G64 to rotate.
- the bottom of the casing G49 is equipped with a steering converter G66.
- the transmission G64 is rotated by the belt to drive the steering device G66, and the steering converter G66 converts the horizontal rotation into a vertical position.
- the steering converter G66 drives the ribbon push rod G51 to rotate.
- the steering converter G66 can use a worm gear pair or a helical gear pair.
- the feed port G62 is disposed on the lower side of the vertical inner leak tower G50, and the discharge port G60 is disposed on the upper side of the vertical inner leak tower G50 to allow the material to run from bottom to top.
- the top of the vertical inner leakage tower G50 is equipped with a shaft fixing plate G61 for mounting a rotating shaft of the spiral belt, and an adjustable discharge speed is also arranged between the shaft fixing plate G61 and the end of the ribbon on the ribbon pushing rod G51.
- the sealing plate and the sealing plate can be adjusted up and down, and are controlled by a hydraulic or pneumatic tool 16.
- the upper and lower adjustment of the sealing plate can adjust the size of the discharging port G60, thereby adjusting the discharging speed.
- a vertical stainless steel vertical plate G57 is fixed around the vertical inner leakage tower G50, and a stainless steel vertical plate G57 is vertically arranged.
- a plurality of leakage holes G58 are distributed around the vertical inner leakage tower G50, and the leakage hole G58 is elongated and arranged.
- the anti-backlash guide G59 is installed on the outer circle of the flange of the vertical inner leakage tower G50 and the reinforcement ring of the stainless steel vertical plate G57.
- the anti-backlash guide G59 is at a 30 degree angle with the tower body.
- the anti-backlash guide flow G59 is disposed close to the rounded edge of the upper flange G67 and the reinforcing collar G69 of the tower body of the vertical inner leakage tower G50.
- the inside of the outer casing G49 is provided with a water receiving groove G55 corresponding to the bottom of the vertical inner leakage tower G50 for receiving water leaking from the vertical inner leakage tower G50, and a water outlet G63 is connected to the bottom of the water receiving tank G55 for discharging water.
- a door G52 is mounted on the side of the outer casing G49, and the door G52 is a vertical three-door body, that is, the outer casing enclosing the inner leakage tower is a tetrahedron, and the three sides are provided with a door body that can be opened.
- the vertical dewatering device of the present invention is mainly for dehydrating treatment of kitchen waste which has been inactivated, deodorized, desalted, and primary dehydrated by wet advanced oxidation.
- the device When working, the device is started, and the motor G54 is matched with the shifting system G64.
- the source firstly drives the tower-type propeller rod G51 through the shaft to rotate, and then the kitchen waste that has completed the wet advanced oxidation and primary dehydration is sent to the feeding port G62 of the vertical dewatering device via the conveying tool, and the material is carried along with the spiral belt.
- the direction of movement of the ribbon on the push rod G51 is pushed from bottom to top until the top of the inner leak tower is sealed, the material is pressed under the action of pressure, and is simultaneously discharged by the discharge port G60, and the water body is taken out.
- the water leakage hole G58 of each tower body leaks out, passes through the anti-backlash guide flow G59 from the top to the bottom to the water tank G55 at the bottom of the inner leak tower, and enters the oil water treatment section through the water outlet pipe connected to the water tank G55, and is The discharged dehydrated material is transported into the material crushing section by the conveying equipment.
- the water leakage hole G58 is placed by the high pressure water from the top to the bottom of the inner leaking tower. Recoil cleaning.
- the vertical dewatering device of the invention adopts a vertical inner leakage tower and a spiral propulsion rod structure to dehydrate the kitchen waste, has a simple structure and good dehydration effect, and has a sealing plate which can be adjusted up and down at the exit for adjusting Output speed to control the degree of dehydration.
- the dehydrated kitchen waste is sent to the material crusher H63 by the pneumatic propulsion device.
- the crushing device adopts a multi-axis structure design, and the material is broken by the low-speed high-torque shearing structure. This technology is a well-known technology.
- the kitchen waste is further processed for reuse.
- the biochemical fermentation device of the present invention is mainly used for biochemical treatment of kitchen waste, and the biochemical fermentation device is mainly used. It comprises a plurality of anaerobic fermentation tanks I65 used in combination with each other and a main fermentation unit I71, which are anaerobic fermentation and aerobic fermentation, respectively.
- the anaerobic fermentation process is provided with an anaerobic fermentation tank I65, the anaerobic fermentation tank I65 is cylindrical, the top is provided with a sealing cover I66, and the sealing cover I66 is controlled by a pneumatic tool (ie, an automatic flipper I94), this embodiment
- a pneumatic tool ie, an automatic flipper I94
- the automatic clamshell I94 is connected to the top of the sealing cover I66 through a connecting rod, and the connecting rod is moved by the cylinder, and the sealing cover I66 is pulled by the connecting rod to realize opening and closing.
- the bottom of the anaerobic fermentation tank I65 is equipped with an automatic unloading system I67.
- the automatic unloading system I67 is tubular, with a spiral stirring knife inside.
- the anaerobic fermentation tank I65 is equipped with an automatically movable material agitator I68, anaerobic.
- a strain activation tank I69 is arranged on one side of the fermentation tank I65, and a discharge port I95 is arranged on the side of the strain activation tank I69, and the discharge port I95 is connected to the automatic discharge system 4.
- the anaerobic fermentation section is provided with a plurality of anaerobic fermentation tanks used in combination with each other, one of which is a strain activation pool I69.
- the main fermentation apparatus is divided into two sub-fermenters I71 and one or more main fermenters.
- a material hoist I64 is provided, and the material hoist I64 is used for kitchen waste. Lift up and put into one of the sub-fermenters.
- Two auxiliary fermenters I71 are installed above the main fermenter, and a material conveying pipeline is arranged between the main and the auxiliary fermenters, and the conveying pipeline is an automatic conveying device I74 disposed at the bottom of the auxiliary fermenter I71.
- the automatic conveying is provided.
- the device I74 is cylindrical, and a cylindrical stirring shell is provided with a spiral stirring knife.
- the material is sent to the main fermenter through the automatic conveying device I74, and a pneumatic valve is arranged in the middle of the connecting passage of the auxiliary fermenter I71 and the main fermenter inlet. I85.
- a stirring device I73 for tumbling action is installed in the auxiliary fermenter I71, and the stirring device I73 is a middle main shaft, and a plurality of stirring blades are fixedly mounted on the central shaft for tumbling the material.
- an exhaust port I91 is opened in the upper portion of the casing of the sub-fermenter I71, and an air blower I92 is connected to the exhaust port I91 for discharging the gas generated in the sub-fermentor I71.
- the main fermenter mainly comprises a horizontal shell I75, a support I76, a heat transfer oil transport pipe I77 and a double-layer ribbon stirrer I78.
- the double-layer ribbon stirrer I78 has a shaft body and an inner layer ribbon.
- the inner spiral belt is disposed inside the outer spiral ribbon, and the inner spiral ribbon and the outer spiral ribbon are spirally belt-shaped, and are respectively fixedly mounted on the shaft body, the inner layer spiral belt and the outer layer spiral The spiral direction of the belt is opposite.
- the shaft of the double-layer ribbon stirrer I78 is provided with a raking blade I79.
- the transmission system in this embodiment includes the motor I80, the transmission I81, the gear I82 and the chain I83, and the gear I82 and the chain I83 are respectively arranged.
- a plurality of transmissions I81 are provided, and the specific number can be set according to actual needs.
- the motor I80 directly drives the main transmission, and the main transmission is driven by the transmission shaft.
- Each of the slave transmissions is provided with a driving gear I82, and a double-sided ribbon agitator I78 is respectively provided with a driven gear on both ends of the shaft body, and two driving gears I82 are respectively connected to the driven gear through the chain I83.
- a feed port I84 is opened above the main fermentation device, and a pneumatic valve I85 is installed at the feed port I84.
- An observation window I86 is installed on the upper middle portion of the horizontal casing I75 for viewing the reaction situation in the horizontal casing I75.
- the upper part of the horizontal casing I75 is also equipped with an air transmission pipe, a pipe I87 and a material sampling port. I88, the air transmission and exhaust pipe I87 is used for introducing air into the horizontal casing I75 or discharging the internal gas of the horizontal casing I75, and the material sampling port I88 is used for sampling the materials in the horizontal casing I75.
- the upper part of the horizontal casing I75 is provided with an automatic discharge hole I89, and the automatic discharge hole I89 is provided with an automatic valve gate I90 for discharging.
- an exhaust port (not shown) is also provided in the main fermenter.
- An automatic temperature control system is also installed in the biochemical device of the present invention.
- the method for biochemical fermentation by the above biochemical treatment device comprises the following steps:
- Anaerobic fermentation tank I65 fermentation The solid base material is pulverized and added to the strain for biochemical treatment.
- the first is to consider the normal crop orange in the surrounding area of the kitchen waste treatment plant.
- Stalk in this embodiment, take the bean seed crop orange stalk (such as: one or more of soybean, mung bean, red bean and pea) to account for 50%-80% of the weight of the total fermentation base, and take the wood crop (such as: wheat, corn, millet, rice), the current season of orange stalks accounted for 20% -50% of the total weight of the fermentation base, in this example, the weight ratio of the two is 60%: 40%, the above
- the two kinds of orange stalks are used as a mixture.
- the reason for using this mixed solid base is that the legume crop orange stalk has high protein content, but the soluble sugar content is low, and the microbial activity is not high at the initial stage of fermentation, while the straw crop stalk is low.
- the nutritional value of the plant itself is not high, but the soluble sugar content is high.
- the mixing of the two crops of orange stalks not only improves the quality of the fermentation, but also complements the nutrients of the two types of crop stalks;
- the diameter is 0.5m M——1mm powder, and adding a composite microbial agent capable of decomposing crude fiber to biochemically treat the above mixture material, and the complex bacteria agent refers to not less than two kinds of bacteria, one of which is Aspergillus oryzae, a composite microbial agent
- the input amount is 1% of the mixed solid base, and the chemical components calcium oxide, sodium chloride, sodium hydrogen phosphate and urea are added;
- the main fermentation device I70 is composed of two main fermenters and two sub-fermenters.
- the main fermentation device I70 is composed of two main fermenters and two sub-fermenters. Pre-fermentation of materials by different strains. Firstly, in one of the sub-fermenters 8, the artificially inactivated kitchen waste is added as a base material, and the bran which accounts for 8%-10% by weight of the base material, 10% by weight of the base material, 15% of rice bran and The white sugar, which accounts for 1% by weight of the base material, is added as a mixture to the crushed base material to form a paste, and then 2-3% of the strain is added.
- the fermentation method adopts the old fermentation method (the first fermentation strain is bread).
- Yeast added in an amount of 2% - 3% by weight of the total fermented base, and 1% of the weight of the fermented base, mixed with the broken base and adjusted to a paste, heated to 24 ° C - 25 °C, then add baker's yeast), and use the heat source of other sections of the kitchen waste treatment work, and fully stir and strengthen the aeration to enhance the growth of the yeast.
- the fermentation time is 12 hours after stopping the stirring and aeration.
- the old fermentation method After each fermentation is completed, 10% of the total material is stored as the next yeast material at the time of unloading, and the amount of baker's yeast added in each subsequent fermentation can be reduced, and only the bacteria added in the first fermentation are added. 60% of the weight.
- Another sub-fermenter I71 is a pre-fermenter for the main raw material, and solid-state fermentation is carried out using the kitchen waste which has been artificially inactivated, washed and dehydrated.
- the strains selected at this stage are composed of Trichoderma viride, Candida tropicalis, White bacillus and Saccharomyces cerevisiae.
- the weight ratio of the four bacteria is 2:2:1:1.
- the inoculum ie, the amount of mixed bacteria
- the temperature is 25 ° C - 30 ° C is better, the highest does not exceed 42 ° C, by
- the automatic equipment rolls once every hour the fermentation time is 9 hours - 10 hours
- the ventilation condition is 8min / h (that is, 8 minutes of ventilation per hour)
- the ventilation is 0.2m 3 / h.
- the heat source of this pre-fermentation section is provided by the waste heat generated by the heat source of other sections of the kitchen waste treatment work.
- the pre-biochemically processed material is input into the main fermenter, wherein the treatment in the main fermenter comprises: the straw fermenting material and the material in the pre-biochemical treatment device are input into the main fermenter in the main biochemical device, and the input ratio of the material is: straw 10% - 40% of the total material weight percentage in the fermentation material, the baker's yeast fermentation material accounts for 20% of the total material weight percentage, and the second pre-biochemically treated fermentation material accounts for 40% - 70% of the total material weight percentage.
- the double-layer ribbon stirrer 14 rotates 360 degrees under the driving of the power source, the rotation speed is 6-9 rpm, and the rotating motion is the round-trip direction.
- the material is slowly stirred at a low speed.
- the temperature in the main fermenter starts from the initial temperature of 20 °C, and the temperature is gradually increased to 28 ° C.
- the air valve 23 is closed, and the temperature is raised to 35 ° C - 38 ° C.
- the exhaust valve After 3 hours of constant temperature, open the exhaust valve and use the positive pressure in the main biochemical device to discharge the water.
- open the wind exhaust device I112 when the fermentation material with the water vapor in the exhaust system into the gas-water separator means and an air treatment device for processing environment (not part of the invention).
- the total secondary fermentation time is 9 hours.
- the biochemical treatment device adopts the method of combined fermentation of anaerobic fermentation and aerobic fermentation, and the two-step fermentation of the main fermenter and the auxiliary fermenter realizes the effect of automatic biochemical fermentation, the structure is simple and reasonable, and the fermentation effect is good.
- the automatic unloading multi-stage drying device of the present invention mainly comprises a pre-drying device J93 and a main drying device.
- the pre-drying device J93 is installed above the main drying device, and the pre-drying device J93 is an accessory device of the main drying device.
- the pre-drying device J93 is a horizontal sleeve design, and the material automatic flap J94 is provided inside, the implementation
- the pre-drying device J93 is provided with a spindle in the middle
- the material automatic flap J94 is a flipper plate fixedly mounted on the spindle, and the spindle can be driven to rotate by a motor disposed outside the pre-drying device J93.
- the pre-drying equipment J93 is equipped with a screw auger automatic discharge device J95 (or automatic material discharge and discharge device) at the bottom, and the material pre-dried by the pre-drying device J93 is input through the screw auger automatic discharge device J95.
- the automatic auger J95 of the auger auger has a cylindrical shape, and a screw auger is arranged inside, and the auger is driven by the motor to rotate.
- the outer casing of the pre-drying device J93 is on both sides, and the inner casing J97 of the pre-drying device is formed between the two sides, and the inner cavity J97 of the outer casing is provided with heat-conducting oil, etc., and the hot exhaust gas of the main drying device is arranged by the pipe. After passing through the heat transfer oil layer of the pre-drying chamber J97, it passes through the outside of the equipment.
- the heat source in the pre-drying device J93 is derived from the exhaust gas discharge port J96 of the main drying device, and enters the inner cavity J97 of the pre-drying device through the pipe, and heat is transferred by the heat transfer oil carried in the inner cavity of the interlayer, and The tail end of the heat pipe is introduced into the air treatment equipment of the rear end by the air introducing device J98, and the air with smoke, fine dust and moisture is collected and environmentally treated.
- the main drying device in the present invention is provided with a gas or liquid fuel combustion chamber J99 and a burner J100, and a combustion gas or a liquid fuel is generated in the combustion chamber J99 by the burner J100 to generate hot air, which is introduced into the main drying device by the air guiding hood. Referring to FIG.
- the middle of the main drying device is a horizontally rotatable cylindrical body J102 which is reversible in a 360 degree direction, and the front and rear ends of the main drying device are respectively fixed heads J101.
- two or more sub-cylinders rotating in the direction of the main cylinder of the rotating horizontal cylindrical body J102 are provided inside the rotating horizontal cylindrical body J102, and the diameters and lengths of the respective cylinders are different, respectively
- the outer tube is small, the outer tube is a fixed foundation and layered, and the hot air is used to dry the horizontal cylinder.
- the cylinder body is provided with a plurality of rotating sleeves.
- the material to be dried enters the innermost sleeve
- the material advances. And then falling into the second layer of sleeve, at this time, the advancement direction of the material in the second layer sleeve is opposite to the advancing direction of the innermost sleeve, and the material is made to fall and advance in the multi-layer sleeve. Move until you reach the outermost main drum.
- the plurality of inner cylinders are all circular in cross section, and a guide spiral ribbon is extended along the inner wall of the inner cylinder, and the spiral directions of the guide spiral ribbons on the adjacent inner cylinders are opposite to each other.
- the outer side is installed with the airflow disturbing fin J103 in the circumferential direction for disturbing the airflow.
- the installation angle of the deflector is 20 degrees - 30 degrees, which guides the gas to guide the flow.
- the innermost cylinder The body moves with the main cylinder, and the kinetic energy of the movement is brought up by the mechanical rotation of the main cylinder.
- the moving direction of the input material is guided by the guide nut and advances toward the discharge port of the cylinder.
- the outer side of the outermost cylinder is provided with a sub-transmission wheel J111, the motor J108 drives the main transmission wheel J110 through the transmission J109, the main transmission wheel J110 drives the sub-transmission wheel J111 to rotate, and the auxiliary transmission wheel J111 drives all the cylinders.
- the overall movement of the body, the guiding ribbons in the layers of the cylinder are set in different directions, and the material is guided by the guiding material.
- the hot gas stream perturbs and washes the material, and the airflow is accompanied by a turbulent trajectory phenomenon (mixed layer), so that the transport and diffusion mode of the hot gas flow in the cylinder will be the key to drying the material.
- the discharge port J104 falls into the inlet J105 of the secondary inner cylinder body, and is guided by the guide material ribbon and the heat.
- the direction of the airflow is reversed and reaches the discharge port of the layer, and then falls into the feed port of the outer sleeve of the layer of the cylinder.
- the material to be dried is made multiple times with the hot gas flow. After the reverse contact, it finally falls into the main rotating cylinder, that is, the outermost cylinder, and is guided by the guiding screw to the main discharge port J106, and is transported by the automatic conveying tool to the next section, in the automatic unloading
- the other end of the multi-stage drying device is provided with a hot air discharge port J107, and the hot air discharge port J107 is connected to the outer casing interlayer J97 of the pre-drying device J93.
- the working method of the automatic unloading multi-stage drying device of the invention is as follows: the protein nutrient feed (that is, the biochemically treated kitchen waste) which has been biochemically fermented is sent to the pre-drying device J93 through the material hoist, and the material is installed.
- the stirring flap system in the pre-drying device J93 is turned at a speed of 10-18 rotations per second.
- the inner cavity of the device has been passed through the hot exhaust gas of the main drying device through the interlayer of the pre-drying device J93 to pre-dry the device J93.
- the temperature of the inner chamber is raised to 80 ° C - 120 ° C.
- the residence time of the material in the pre-drying device J93 is 1.5 hours - 3 hours, and the hot humid air in the pre-drying device J93 is discharged from the exhaust port by the air-inducing device J98.
- the material is sent to the innermost cylindrical body of the main drying device by the ribbon auger automatic discharge device disposed at the lower part of the pre-drying device J93, the main drying device inlet and The outlet temperature is 240 ° C - 280 ° C and 80 ° C - 120 ° C, at this time the material is in direct contact with the hot gas, and through the action of the spiral strips in the various layers of the drum, the forward flow is established to establish the heat transfer process, When the material is dried by the inner layer drum, it automatically enters the next layer of the drum, and the heat transfer process is established by the reverse flow method before entering the cylinder of the next layer.
- each horizontal cylinder is 25-29 rpm.
- the feed is directly contacted with the hot air flow after so many times of reverse direction.
- the material is continuously dried and sent to the material selection by automatic conveying tools.
- the device at this time has become an unselected protein nutrient feed.
- the automatic unloading multi-stage drying device of the invention uses the secondary heat drying to dry the kitchen waste, and has the function of automatic unloading, the structure is simple, the drying effect is good, energy saving, and environmental protection are saved.
- the dried protein nutrient feed is selected by the automatic conveying system into the selection device.
- the material selection device of the present invention performs the final fine screening of the dried protein nutrient feed.
- the front-end process of fine screening is to biochemically treat the kitchen waste. This section is the debris that has not been caught by screening in the previous process and the large organic matter that has not been completely decomposed in the biochemical process. Isolation from protein nutrient feed.
- the equipment base K108 is used as the bearing foundation, and the protective cover K109 is installed on the upper part of the base K108 for preventing the material from running out.
- the production protective cover K109 is provided with the inclined metal rolling screen cylinder K110.
- the metal rolling The screen diameter ⁇ of the screen cylinder on the screen cylinder K110 is 4 mm - 6 mm, and the interval between the hole and the hole is 2 mm.
- the inclination angle of the metal rolling screen cylinder K110 is 1 degree - 20 degrees, and The inclination angle is adjusted, and an adjustment bolt is arranged inside to adjust the inclination angle thereof.
- the inner cavity of the downward end of the metal rolling screen cylinder K110 is provided with a spiral belt K111 along the cylinder wall as a guiding rail, and the weight is guided by the spiral belt K111. After the debris and large debris enter the dump outlet, they fall into the debris receiver K112.
- a finished carrier K113 is mounted on the base K108 below the metal rolling screen cylinder K110, and a funnel-shaped receiving device is arranged under the metal rolling screen cylinder K110, and the material leaked through the metal rolling screen cylinder K110 The funnel-shaped receiving device falls onto the finished carrier K113.
- the finished carrier K113 is in the shape of a conveyor belt, and the lower part of the finished carrier K113 is equipped with an automatic conveying tool K114, which is used for conveying the finished product into the warehouse or directly into the feeding preparation workshop of the next section.
- a secondary selector is installed in the lower portion of the debris acceptor K112, and the debris falling into the debris receiver K112 is secondarily selected.
- the secondary selector is connected by a chain plate.
- the conveyor K115 carries the animal material forward, and the size object flapper K116 is installed in the front direction of the chain conveyor K115 near the tail end.
- the size object flapper K116 is disposed at a position of not less than 5 mm above the chain conveyor K115.
- the material size can be adjusted to adjust the distance between the object splitter K116 and the chain conveyor K115, and the material can be fed into the finished product conveying system through the gap between the object splitter K116 and the chain conveyor K115. After that, enter the finished carrier.
- the working process of the material selection device in the invention is as follows: the dried protein nutrition feed (ie the kitchen waste product) of the invention, the input speed is about 30 kg/min - 80 kg / min, the material is rolled by metal
- the rotation of the screen cylinder K110 advances along the oblique direction of the metal rolling screen cylinder K110, and the material is continuously turned in the metal rolling screen cylinder K110 with the metal rolling screen cylinder K110, and the large object or the heavy object is Rolling up and moving forward in the oblique direction and entering the guiding track of the spiral belt K111, is sent into the heavy debris and the bulk material receiving interface, and the finished product is smashed from the wall hole of the metal rolling screen cylinder K110 into the finished carrier K113 .
- the material of the large-sized debris receiving device is sent to the chain conveyor belt.
- the material is conveyed to the separation port of the object splitting gate K116, and the material capable of passing the gap of the object shunting gate K116 is the finished product.
- the finished product conveying system After being sent to the finished product conveying system, it is sent to the finished product carrier, and the large piece of material or heavy debris is separated by the pneumatic feeder, and then dialed into the debris collection box.
- the feed product produced by the kitchen waste is screened, and the screening efficiency is fast and the precision is high.
- automatic processing such as automatic feeding and automatic discharging into the warehouse can be realized.
- the produced feed can also be mixed by means of a mixed feed device.
- the mixed feed device used in the present invention consists of a pulverizer, a cylindrical pulse dust collector L117, a spiral mixer L117L, a ring die granulator L118, and a countercurrent flow.
- the cooler L118L and the rotary grading screening L119 and the automatic weighing and packaging device L120 are composed of six parts.
- the waste plastic reversal engineering device is a device connected to the next section of the rolling molar E30 of FIG.
- the waste plastic, waste paper, waste cloth and other debris sorted by the air flotation sorting device are taken out by the rolling caries E30, and enter the centrifugal dewatering equipment of the waste plastic reversal engineering device through the conveying system to carry out basic materials.
- the main treatment device is taken from the conveyor belt M122 as the starting point, and the material is sent to the pneumatic automatic feeder M123 which can move forward and backward through the rail, and the raw material is sent to the cracking catalytic horizontal reactor M124 (reaction)
- the structure of the kettle can be found in the Chinese patent publication No. CN102220152A and the publication No. 201660599U.
- the reactor M124 can be rotated 360 degrees with an automatic random scraping device M125, and the material is added with oxidation in the reactor M124.
- the synthetic fuel of the bio-oil product obtained from the project, and the combustible gas obtained by reversing the project, the production fuel used is self-sufficient, and the exhaust gas generated by the cracking furnace M126 during the combustion process is output from the gas outlet of the furnace body and is connected by a pipe.
- Exhaust gas environmental protection equipment system M127 Exhaust gas environmental protection equipment system M127.
- the material in the reactor M124 is cracked under anaerobic conditions to obtain an oil and gas mixture.
- the vacuum system M130 is automatically opened, and the check valve of the reactor M124 is followed.
- M128 is automatically opened, oil and gas first enter the oil wax separator M129.
- the oil and gas enter the first-stage heavy oil separator M131 along the pipeline under the action of the vacuum equipment of the next stage, and the light oil and gas pass through the safety.
- the water sealing device enters the first stage condenser M132, the mixed oil enters the oil carrying container M133, and the gas that cannot be liquefied is transferred into the negative pressure device M134 for cis and reverse gas rinsing, and the rinsed gas continues to enter the rear stage vertical water.
- the sealed gas safety conveyor M135 compresses and dehydrates the combustible gas from the special secondary gas compressor M136, and then delivers it to the first stage gas compressor to compress the gas to 0.5mpa, and the second stage gas compressor compresses the gas to 1mpa, and the flammable gas is transported to the gas storage M137 for use.
- the mixed oil After the mixed oil enters the oil-bearing container M133 to cool down, the mixed oil is input into the diesel refining equipment through a special oil pump, and the equipment is started from the first-stage chemical decarburization and decontamination synthesizer M138, and then enters the carbon removal rinser M139 and dewaxed.
- the chemical agent required in the carbon removal rinser M139 and the dewaxing glue remover M140 is set in several chemical containers, and the liquid agent addition zone M141 and the solid agent addition zone M142, all additives
- the automatic dosing device automatically feeds according to the set process.
- the refined oil After the refined oil has passed the test, it enters the diesel synthesis equipment M143 to adjust the quality (according to the quality of each refinery, adjusted to the same quality and then shipped out), then enters the fixed bed filtration equipment for smooth and reverse double-layer filtration, followed by Qualified National III standard diesel is obtained and transferred to the warehouse.
- a non-vaporizable residue that is, a crude carbon black
- the crude carbon black may be treated by the crude carbon black treatment device for the residue after the anaerobic cracking.
- the crude carbon black processing device comprises a coarse carbon black artificial aging processor N144, which is a device for aging materials by using ozone, after being chemically aged.
- the crude carbon black then enters the physical aging bed N145, and the aged carbon bed is steamed under the condition of pressure 2.8mpa-3.2mpa for 25-35 minutes.
- the above two artificial aging methods are implemented to implement the change.
- the specific volume of the coarse carbon black forcibly changing the orderly characteristics of the external crystallization of the carbon black particles, helps the embedding and enhances the carbon-hydrogen ratio of the carbon black.
- the crude carbon black is artificially aged, it is input into the material compatibility equipment N146 by a special automatic conveying tool.
- the materials are divided into two categories: liquid and solid.
- the remaining share of the weight of the material is treated crude carbon black.
- Each of the compatibility aids is added by liquid and solid automatic dosing and feeding equipment N147.
- the material is fully mixed into the low-sulfur high-energy environment-friendly clean coal by multi-layer push-pull screw N148.
- Forming machine N149 after the material is formed, the finished product is called a low-sulfur high-energy clean coal.
- the quality is 0.2-0.5% of total sulfur, the grade of coke slag is grade 1, and the ash is 5.5-7%.
- the coarse carbon black used in this embodiment refer to the Chinese patent of the publication number: CN102220179A.
- the collecting device, the kitchen garbage bag breaking device, the kitchen garbage liquid air flotation sorting device, the wet advanced oxidation, the deodorizing, the inactivation, the cleaning and salt reducing device, the primary solid separator and the vertical dewatering device All of them are provided with water outlet pipes, and the oil, water and solid mixture from the various outlet pipes are sent to the distillation-free biodiesel production device for diesel production. Please refer to FIG. 28 to FIG. 31 for the biodiesel in the present invention.
- the front end of the manufacturing system is provided with an oil-water mixing tank O150.
- the oil, water and solid mixture generated in each section of the kitchen waste treatment process is transported to the oil-water mixing tank O150 through the water outlet pipe, and the oil-water mixing tank O150 is disposed at the tail end of the water outlet pipe.
- the horizontal end of the oil-water mixing tank O150 is provided with a horizontal spiral-belt solid-liquid separation device O151 for removing solids of oil, water and solid mixture.
- the horizontal spiral-belt solid-liquid separation device O151 includes a lying The cylindrical casing has a filter screen inside the casing, and a conveying screw is fixed inside the filter screen, the motor is matched with the transmission to drive the filter screen and the spiral belt rotates, and the horizontal spiral belt solid-liquid separation device O151 is provided with oil and water mixing at the bottom.
- the oil, water and solid mixture is input into the horizontal spiral belt solid-liquid separation equipment O151 through the pipeline through the pump, and after the liquid-solid separation by the horizontal spiral-belt solid-liquid separation equipment O151, the oil and water mixture is input through the conveying pipeline.
- the oil-water separation tower O152 is disposed at the rear end of the horizontal spiral belt solid-liquid separation device O151, and the oil-and-water mixture after de-solidification is sent to the oil-water separation tower O152.
- the oil-water separation tower O152 is a vertical cylinder.
- the inlet port is disposed at the middle and lower sides of the side, and the oil-water separation tower O152 is internally provided with a heating pipe O153.
- the heating pipe O153 extends from the lower part of the oil-water separation tower O152 to the inside of the oil-water separation tower O152, and then is output from the upper part of the oil-water separation tower O152.
- the heat source used in the heating pipe O153 is the waste heat of the heat-conducting oil furnace, which can save energy use.
- a heat source can also be separately provided.
- the top of the oil-water separation tower O152 is equipped with an infrared water level locator O154 for positioning the oil-water mixture at the time of oil-water separation, and thereby automatically controlling the amount of oil-water mixture.
- the oil-water separation tower O152 is provided with an oil scraper O155 (like a wiper to scrape off the oil) and an oil outlet pipe O156 on the side close to the upper portion.
- the scraper O155 has a strip-shaped plate shape and is separated by oil and water.
- the motor at the top of the tower O152 is rotated to scrape the oil in the oil-water mixture into the oil sump and output through the oil outlet pipe O156.
- an electric valve O157 is provided on the oil discharge pipe O156, and the bio-oil is controlled to enter the oil storage container O149 from the oil discharge pipe O156 through the electric valve O157.
- biodiesel production is carried out by using the grease removed from the kitchen waste.
- the front end of the biodiesel production device is a grease colloid removal device O158.
- the grease colloid removal device is used.
- O158 is a rectangular shape, and the grease gel removal device O158 is fixedly provided with a hole impact plate O159 in the middle, and a hole is formed in the impact plate O159.
- the two facing positions of the impact plate O159 are respectively installed with a rotary hydraulic propulsion machine O160.
- the rotary hydraulic propulsion machine O160 includes a propeller blade disposed inside the grease gel removal device O158 and a motor disposed outside the grease gel removal device O158, and the motor drives the propeller blade to rotate.
- the bio-oil material is input from the oil storage container O149 into the oil gel removal device O158 by a special oil pump to effectively remove the phosphorus ester, sugar, protein and other impurities in the oil, and prevent the glue.
- the quality covers the fine particles of grease in the latter stage, and the barrier grease contacts the catalyst.
- the ozone oxidation processor is composed of an ozone generator O174, an anti-liquid recoil valve O175, a powerful gas, a liquid mixer O176, a reactor O177, a circulation pump O178, an oil inlet pipe O179, an oil outlet O180, and a liquid.
- ozone generator O174 is connected with strong gas and liquid mixer O176 through anti-liquid recoil valve O175, strong gas and liquid mixer O176 through oil inlet pipe O179 and grease colloid
- the removal equipment O158 is connected, the powerful gas and liquid mixer O176 is connected to the reactor O177 through a pipeline, the circulating pump O178 is connected to the reactor O177, the bottom of the reactor O177 is the oil outlet O180, and the oil outlet O180 is passed through the pipeline and the bio-oil.
- the normal temperature grease exchange equipment O161 is connected, the liquid level controller O181 is installed in the reactor O177, and the ozone residual gas destroyer O182 is installed on the top of the reactor O177.
- a theorem feeder O183 is also mounted on top of the reactor O177.
- the oil and fat can remove impurities, pigments, odors, proteins, and the like from the fat by the ozone oxidation processor.
- the main body of the biodiesel production device is a bio-oil normal temperature grease exchange device O161.
- the bio-oil normal temperature grease exchange device O161 is a cylindrical cone-bottom reaction kettle, and the bio-oil normal temperature grease exchange device O161 is equipped with more than one ultrasonic wave.
- the generator O162 in this embodiment, is provided with four, each of the ultrasonic generators O162 is respectively provided with a sleeve O163, a sleeve O163 is surrounded by an internal threaded jet hole O164, and a sleeve is fixed above the sleeve O163.
- a pneumatic take-off device O184 is connected above the locking device O165, and acts on the depth of the inlet of the control sleeve O163 and the ultrasonic transducer O162 in the bio-oil normal temperature grease exchange device, and the ultrasonic generator O162 is passed through the card holder O165. It is installed inside the bio-oil normal temperature grease exchange equipment O161.
- the bio-oil normal temperature grease exchange equipment O161 is equipped with a liquid guiding tube O166, one end of the liquid guiding tube O166 is connected to the upper part of the bio-oil normal temperature grease exchange equipment O161, and the other end is connected to the bottom of the bio-oil normal-temperature fat exchange equipment O161, and the pump O167 is connected at Liquid conduit O166.
- the top of the bio-oil normal temperature grease exchange equipment O161 is equipped with a top cover O168, the top cover O168 is provided with a feed port O169, and the bio-oil normal temperature grease exchange device O161 is equipped with a window O170.
- a gas pipe O171 is provided at the bottom of the bio-oil normal temperature grease exchange device O161, and one end of the gas pipe O171 is connected to the compressed air machine.
- methanol and a co-solvent are added from the feed port O169.
- the co-solvent should be selected to enhance the mutual solubility of the oil and the methanol, and to be recyclable.
- the ultrasonic generator O162 is introduced into the bio-oil from the top to the bottom of the bio-oil normal temperature grease exchange device O161 by pneumatic or hydraulic tools, and the compressed air is blown from the bottom of the bio-oil normal temperature grease exchange device O161. , thereby promoting the accelerated co-solubilization of bio-oil and methanol, and inputting the bio-fat mixture to the inner cavity of the casing O163 through the oil pump O167, flowing from top to bottom into the ultrasonic treatment, and the ultrasonic frequency is gradually enhanced from 25KHz to 30KHz, the time is 20 - 60min.
- the liquid separation device O172 is in the form of a vertical cylinder, and the liquid separation device O172 is provided with a filtering device O173 at the rear end of the liquid oil normal temperature grease exchange device O161, and the mixing after the ultrasonic treatment is completed.
- the liquid is supplied to the liquid separation device O172, and the obtained crude biodiesel is obtained by the filtration device O173 to obtain biodiesel.
- the method for producing biodiesel that is, the method for operating the above biodiesel manufacturing system, comprises the following steps:
- the oil-water mixture is sent to the oil-water separation tower O152 for oil-water separation.
- the oil-water mixture in the oil-water separation tower O152 is heated to 60 ° C by using the residual heat of the heat-conducting oil furnace - 85 °C, after the biological grease floats to realize the oil moisture layer, the lower layer of water is sent to the sewage treatment system by the conveying pipeline, and the upper layer of the biological grease is scraped out by the scraper O155, and sent into the oil storage container through the oil outlet pipe O156;
- the bio-fat is sent into the grease colloid removal device O158 by a pump or the like, and then the hydro-pneumatic propulsion machine O160 is started, and the concentration is 85%.
- the ratio of phosphoric acid, phosphoric acid and bio-oil is not more than 1% of the total amount of grease.
- the liquid-pulling thrust at both ends of the O158 is removed by the grease colloid removal device, and the liquid inside the O158 is removed.
- the impact time is established. Within the required time range of the set process conditions, in the present embodiment, the collision time is 10 min - 15 min, and after the end of the liquid impact time, the diluted brine is immediately added, and the weight ratio of water to salt is 95:5. Between 90:10, the weight ratio of bio-oil to dilute brine is between 90:10 and 80:20.
- the action of electrolyte salt accelerates flocculation and the formed micelles are more stable;
- the solid catalyst is characterized by the reagent activated carbon and the nanoparticles of the silicate mineral of the cyclic structure of aluminum, sodium, iron, magnesium and lithium.
- the base nucleus itself can release 12,000/cm 3 or more negative ions as qualified products, and then immerse the base nucleus in a mixed liquid of alkaline silica sol and aluminum sol and lithium hydride, and take it out at a temperature of 650-720 ° C. After constant temperature for one hour, after cooling, it is screened and refined to form a hybrid medium with silicon, aluminum and lithium mesh, and a polar hybrid carrier. The carrier is then immersed in the solution of KNO 3 . After taking out, drying in a drying apparatus at 110 ° C to obtain a basic catalyst carrying 15% - 25% of KNO 3 .
- the initial frequency of the ultrasonic generator O162 is 25KHZ, the time is 1min, and then gradually increase to 30KHZ, the time is 30min - 40min, the reaction temperature is 25 - 35 °C.
- the bio-fat mixture is input into the liquid separation device O172, and the upper layer is a mixed liquid of methanol and glycerin, and the lower layer is crude biodiesel;
- the liquid separation device is set to be opened in the lower liquid discharge port, and the crude biodiesel is transported into the filtering device O173, and the purified biodiesel is obtained after filtration and the solid catalyst is recovered, and can be recycled after being recycled.
- the biodiesel is then fed into a storage container for further refining, while the methanol and glycerin mixture is used for other purposes.
- the biodiesel manufacturing system of the invention can automatically separate the solids, moisture and the like contained in the kitchen waste, and then further convert the contained fats and oils into biodiesel for use, the device structure is simple, the process, the energy saving and the production cost are low. .
- the distillation-free biodiesel production device produces crude biodiesel, and the crude biodiesel is further emulsified by the emulsified biodiesel device to form emulsified biodiesel.
- the device is mainly a housing P174.
- the upper portion of the housing P174 has a straight cylindrical shape, and the lower portion is a semicircular body.
- the housing P174 is internally provided with a vertical agitator P175, and the power source drives the vertical agitator P175 to rotate.
- the power source includes a motor P176 and a shifting device P177 fixedly mounted on the top of the housing P174, the motor P176 being disposed above the shifting device P177, and the motor P176 driving the vertical agitator P175 to rotate by the shifting device P177.
- a support frame P180 of a rotating shaft is provided in a semicircle at the bottom of the casing P174 for supporting the rotating shaft of the vertical agitator P175.
- the vertical shaft of the vertical agitator P175 is equipped with a plurality of slurry type straight mixers P178, and can also be replaced by paddle type leaf blades.
- the lower part of the central shaft of the vertical mixer P175 is equipped with a turbine or a disk.
- the curved blade slurry P179 and the cylindrical inner wall of the casing P174 are provided with a plurality of liquid guiding vanes P183 (provided inside the casing P174 to act as a spoiler), and a plurality of inlet ports P181 are arranged at the top of the casing P174.
- Each of the feed ports P181 is connected to the dosing device P182 through a pipe.
- each dosing device P182 is used for automatic feeding of various additives.
- the top of the casing P174 is further provided with an oxygen-enriched water inlet pipe P186 and penetrates into the casing P174 to connect the oxygen-enriched water atomizing nozzle P185, the inlet pipe P186 is connected to the high-pressure pump P187, and the ozone generator P188 outputs the O3 gas to enter the strong water and gas.
- the mixer P189 is mixed with water, it is sent to the oxygen-enriched water reserve tank P191 through the conveyance of the pipe P190, and the water outlet of the oxygen-enriched water reserve tank P191 is connected to the high-pressure pump P187.
- the upper part of the casing P174 is provided with an oil inlet port P192, one end of which is threaded inside the casing, and the other end is connected with the oil pump, and the lower part of the casing P174 is also provided with a finished discharge port P184, and the obtained emulsified biodiesel is discharged from the discharge port P184.
- the output is then sent to the oil storage through the pipeline and the pump.
- the oxygen-enriched micro-emulsified biodiesel produced in the present invention acts on various heat source fuels.
- the method for preparing the emulsified biodiesel in the present invention that is, the operation method of the above device in the present invention is as follows: the present invention is mainly directed to further processing of biodiesel produced by a production process from oil and fat, and oxygen-enriched microemulsification of biodiesel. Refined diesel technology.
- the method for preparing the emulsified biodiesel in the present invention comprises the following steps:
- the hydrophilic agent is a composite active agent combined with a cationic surfactant and a nonionic surfactant.
- the two types of surfactants are triethanolamine, hexahydroaniline or west. Tribromoammonium bromide and ammonia water, the ratio is 50% of cationic surfactant and 50% of nonionic surfactant.
- the hydrophilic agent is used to degrade the rigidity of the mask, increase the fluidity, reduce the bending energy required for the formation of microemulsion, and is easy to form.
- the milking solution is stirred for 1 min to 15 min after the hydrophilic agent is added;
- butanol can be used as a co-surfactant, and continue to do not indirectly stir the mixture for 15min, when stirring, the vertical stirrer 2 for 100 rev / min - Stirring at 130 rpm;
- isopentane as a self-ignition temperature regulator.
- isopentane is mixed with the above liquids of (1)-(3) and stirred for 5 minutes.
- the amount of oxygen-enriched water varies from 1% to 20% of the total weight of the product depending on the product, in this embodiment,
- the ozone generator supplies O 3 , the gas flow rate of ozone transport is 250ml/min, and is mixed with the water body in the powerful water and gas mixer, and then input into the oxygen-rich water storage tank to be naturally decomposed into oxygen enriched in water, and the natural decomposition time is 30 min.
- the dissolved oxygen content in the water reaches 27-35%, forming oxygen-enriched water.
- the oxygen-enriched water is added in an amount of 10%-20% of the total weight.
- the mixture is stirred for 15 minutes, and the rotation speed is adjusted to 170 rpm.
- octadecyl-cis-9-ene The acid is added in an amount of 70% to 90% by weight of the oxygen-enriched water added, and is continuously condensed until the clarification is transparent under the stirring of the stirring device.
- the rotation speed of the agitator is adjusted to 280-340 rpm, generally Continuous stirring is required for 40-60 minutes.
- micro-emulsified diesel fuel produced by petrochemical diesel can be used as a heat source fuel, and the micro-emulsified diesel oil containing less than 10% of oxygen-rich water and containing more than 80% of the national standard III petrochemical diesel can be used as a diesel fuel for cleaning vehicles.
- the biodiesel extracted from the kitchen waste can be further refined by the invention to produce oxygen-enriched micro-emulsified biodiesel, which can expand the application range.
- the invention also provides a rapid sewage treatment and recycling device, and the wastewater generated in all the production processes in the invention is concentrated and rapidly processed into qualified industrial water reuse, and is used as the production water for the kitchen garbage resource treatment.
- the rapid sewage treatment and recycling device firstly allows sewage to enter the sewage filtration tank Q185, and uses the debris in the sewage filtration tank Q185.
- the gate Q186 is isolated from the impurities in the sewage.
- the debris block Q186 is also provided with an anti-plug back buffer Q187.
- the sewage after passing through the fence Q186 is input by the water pump into the hot felt sewage treatment device Q188.
- the device has a cavity Q189.
- the casing Q190 the sewage enters the top of the casing through the pressure pump, and the discharge pipe also has a venting port Q191, and the top of the casing is provided with a plurality of atomizing spray heads Q192 communicating with the inlet pipe, and the atomizing spray head Q192
- a hot and hard felt Q193 ie, two-layer structure, upper layer, lower layer, and two layers of misalignment
- the hot felt Q193 has multiple shallow shallow grooves on the surface of the Q193 (the shallow ditch Q194 is criss-crossed).
- the heat source of the hot felt Q193 is heat transfer of the heat transfer oil pipe Q195, the felt surface temperature is controlled between 90 and 200 ° C, and the bottom of the hot felt Q193 is provided with a micro solid.
- the water body flows between the hot felt Q193 and the high temperature resistant cushion Q199 into the bottom of the inner cavity of the equipment.
- the top of the casing Q190 is provided with an automatic suction and exhaust valve Q200, and the casing Q190 is located above the hot felt Q193 for hot steam collection.
- Port Q201, the hot steam collecting port Q201 is connected to the heat exchanger Q202 through a pipe, converts the hot water steam into a water body to the collecting tank Q203 and merges with the discharged water body on the lower side of the casing, and pumps the water body of the collecting tank Q203 from the pool.
- this system is an ozone-water reactor, which is a sleeve-type structure with two inner and outer cavities, the inner chamber is a gas-water reaction chamber Q205, and the outer chamber is a gas-water circulation reaction buffer chamber Q206.
- the inner cavity has an inner casing, and the outer cavity has an outer casing.
- the top of the inner casing is provided with an automatic exhaust valve Q207 and a liquid level control online monitor Q208 for monitoring the liquid level, and the ozone-water reactor inner cavity Inlet inlet tube
- the end position is equipped with activated carbon reaction ball Q209.
- the reaction ball Q209 is used to accelerate the conversion of ozone into hydroxyl radicals in water, so as to accelerate the degradation rate of organic matter in the water by ozone.
- the upper part of the reaction ball Q209 is impervious to water and the lower part is mesh.
- the ball is filled with granular activated carbon, and the volume of activated carbon contained in the ball accounts for 15% to 95% of the volume of the reaction sphere.
- the gas-water mixture in the inner chamber is transported to the outer chamber through the inner and outer chamber connecting pipe Q213 of the reactor, and then the water pump Q211 provided outside the advanced oxidation reactor is supplied with the water-in-water mixer to replenish the ozone, and then re-enters the inner chamber to allow the gas.
- the water mixture was subjected to such a cyclic motion for 2 to 5 minutes.
- the reaction of the gas-water mixture reaches a set time, it is discharged from the drain port Q212 provided on the bottom side of the inner chamber, and the residual sludge is discharged through the drain port Q212 at the bottom of the reactor, and the drain port is the drain port of the outer casing.
- the gas water mixer Q215 mentioned above is installed at one position of the circulating pipe in the advanced oxidation reactor, and the mixer is a three-way connection method.
- the circulating water is connected to both ends, and one port in the middle is connected with the waterproof check valve Q216, and the other interface of the waterproof check valve Q216 is connected to the gas pipeline of the ozone generator, and leads to the gas, water and material mixer Q217
- the water body enters the transfer tank Q218, and then the water body is sent into the activated carbon filter fixed bed Q219 for treatment, and then enters the composite filtration device Q220.
- the filtering mode of the device is to carry out the bottom-up reverse direction by pressurization. After filtration, the initially filtered water body is transported into the composite filtering device Q220 through a water pump and a pipeline.
- the device Q220 is composed of a plurality of sets of filter tanks Q221, and the filter tanks are respectively provided with a plurality of vertical types.
- the filter column Q222 has a water outlet hole at half of the length of each filter column Q222.
- the bottom of the filter column Q222 is equipped with a filter screen of 80-140 mesh, the working pressure is 0.5-1mpa, and the top of the filter tank Q221 has a water inlet.
- the tank body is divided into two layers, a sealing partition plate Q225 is installed between the tank and the tank, and each layer of the tank is respectively provided with a filter column tray Q226, which is opened on the Q226.
- the diameter of the filter column Q222 is matched, and the number of holes is also the same as the number of the filter column Q222 to be installed.
- the contact edge of the Q226 pallet and the filter column Q222 are provided with a leakproof seal Q227, the upper tank
- the upper side is installed with water inlet diversion pipe Q228, the inflow diversion pipe Q228 is connected to the upper part of the lower tank, the lower side of the upper tank is provided with the water diversion pipe Q229, and the outlet diversion pipe Q229 is connected to the lower tank.
- the lower part is provided with an exhaust port Q230 on the upper and lower sides of the can body.
- Each filter column Q222 is equipped with two kinds of solid adsorbents, the lower layer is activated carbon Q231, and the upper layer is hybrid charge adsorbent Q232.
- the joint mode of the two adsorbents is random joint, and the water outlet after water filtration is set in composite filtration.
- the side of the bottom of the device is Q233, and the center of the bottom head is provided with a sediment discharge port Q234.
- the water body treated by the composite filter device has reached a level of clear turbidity, no odor, no heavy metal ions, and has been basically
- the ozone gas and the generated strong oxidant are removed, and the clean water treated by the composite filtering device directly enters the ultraviolet sterilizer Q235 to perform the final step treatment on the water body, and the obtained qualified water body acts on the production water.
- the operation method of the rapid treatment and reuse device for sewage is as follows: all the sewage in the whole process of the kitchen waste recycling process is concentrated into the sewage collection basin through the discharge pipe, and the debris contained in the sewage is coarsely blocked.
- the grid is isolated, and the water enters the hot felt sewage treatment equipment.
- the sewage is sprayed to contact the hot felt body, the water body instantaneously contacts the hot plate in the shallow groove, the microorganisms basically die, and the hot water vapor rises upward and rises.
- the hot mist water vapor is introduced into the heat exchanger by the hot steam collecting port and returns to the liquid water.
- the precipitation zone is discharged from the sewage outlet located at the bottom of the microsolid precipitation zone, and the supernatant is discharged from the drainage port at the upper portion of the microsolid precipitation zone, and after being merged with the water body liquefied by the heat exchanger, the advanced oxidation reaction device is input through the pipeline.
- the water enters the powerful gas-water mixer and is strongly mixed with the ozone gas supplied by the ozone generator, and then enters the ozone-water reactor.
- the charcoal reaction ball passes through the sewage water net of the reaction ball and enters the gas-water mixed water body circulation system of the reactor, and the water pump continuously circulates the water body in the inner cavity and the outer cavity to act on the advanced oxidation reaction, and the reaction time is 2-5 minutes.
- the concentration of ozone in the water is 1 - 5g / T.
- the ozone in the water is activated by activated carbon to initiate a chain reaction in water to accelerate the conversion of ozone into hydroxyl radicals, similar to O 3 /H. 2 O 2 or O 3 /UV advanced oxidation process, the residue of the precipitate layer in the lower part of the reactor is periodically discharged from the sewage outlet.
- the water body first enters the fixed bed of activated carbon for reverse filtration, and then outputs the pressure control valve to the composite filtration device.
- the water body first passes through the filtration layer of the hybrid charged absorbent, and the adsorbent is not solid.
- the polar adsorbent is a base nucleus, and the outer layer is coated with a combination of a silicon-aluminum microporous skeleton and a polar absorbing agent.
- the adsorbent acts on various inorganic and organic substances hidden in the water.
- the heavy metal ions in the water body produce larger and faster adsorption.
- the water body treated by the hybrid charge adsorbent naturally passes through the activated carbon adsorption layer, it is refined, and then enters the ultraviolet sterilizer to perform the final step on the water body.
- the treatment uses ultraviolet radiation in the sterilizer, the intensity is 2600-3000UW/cm 2 , the wavelength is 235-258nm, and the irradiation time to the water body is 1-4s. When the water body completes the whole process, it enters the cistern container. As production water for the treatment of kitchen waste.
- the sludge adhered to the kitchen waste is processed by the hybrid charged adsorbent production device.
- the hybrid charged adsorbent production device can process the pollution of the inevitable attachment of the kitchen waste.
- the utilization of the sludge in the mud and the plant area is the best choice for the non-transfer treatment of environmentally friendly residues, and it is also the implementation and application of the pollution control method.
- the production method of the hybrid charged adsorbent is mainly for the cumbersome use of microorganisms in the sludge, and the technical requirements are high, and under a condition of natural dryness, the microbial cells are only metabolically treated in a stagnant state, not Death, and a key problem that can be revived once the moisture is given, and a solid adsorbent is produced by using a microbial individual or a dead microorganism individual living in the sludge as a pore module.
- the hybrid charged adsorbent production device is forcibly inactivated by manually forcibly inactivating the sludge by the artificial inactivater R236.
- the treated sludge is sent to the curing equipment R237 through the automatic conveying equipment for curing or semi-curing process.
- the solidified or semi-solidified sludge is transferred by the automatic conveying equipment.
- the pellet is fed into the sludge propeller R238, and the sludge is pushed into the anaerobic pyrolysis reactor R239.
- the sludge propeller is installed on the guide rail. When the feed is fed, the outlet is connected to the reaction tank inlet, and if the feed is completed When the propeller can retreat by itself, the discharge port is separated from the feed port of the reaction kettle, and the inlet of the reaction kettle is sealed and closed.
- the outer shell of the reaction kettle is a furnace body, the reaction kettle is installed horizontally, and the other end of the same axial direction of the feed inlet is provided with a vapor outlet, and the vapor outlet is controlled by a one-way automatic valve, and the reaction kettle is at a set pressure.
- the valve is automatically opened, and the vapor enters the water-sealed combustible gas collection and processing device R240.
- the combustible gas rises into the heat exchanger through the water seal interface, the non-liquefiable gas generated is combustible gas, and the return pipeline is returned to the pyrolysis furnace for use as a gas.
- the heat source fuel is reused, and the hot flue gas discharged from the cracking furnace is treated by the fuel cracking furnace tail gas processing system R241 together with the hot flue gas generated by the other materials in the kitchen waste recycling process.
- the sludge crevice moisture that has completed the anaerobic heating has been forced into water vapor and discharged with the combustible gas.
- the set pyrolysis time is completed, the microbial dead body residue contained in the sludge in the reaction vessel is coked, and the sludge formation rate is consolidated.
- the discharge port of the reaction vessel is opened, and the reaction kettle is used.
- the automatic discharge screw belt unloads the sludge, transfers it to the pipeline type spiral belt conveyor and sends it to the aging warehouse R242. It is naturally aged for 12 to 48 hours, and then the naturally aged microporous sludge particles are placed.
- the acidification time is 12-18 hours, which acts to remove the dead bodies of the coked microorganisms, and at the same time acts to remove the metal impurity ions and causes the pore structure skeleton of the particles to be exposed, so that the hydrogen ions
- the sludge particles after the acidification process are sent to the hot water rinse tank R244 for rinsing, and after adjusting the pH to 6.5-8, the rinsed granular material is transferred into the hot steam by the conveying device.
- Bed R245 undergoes a preliminary physical activation with an activation time of 1.5 to 2.5 hours.
- the physically activated microporous particles are placed in a high temperature anaerobic activation furnace R246 for high temperature activation for 1-4 hours, and the controlled heating rate is 15-30 ° C / min.
- the exhaust gas of the activation furnace is discharged into the tail gas environmental protection treatment system. .
- the screened finished product is a non-polar microporous adsorbent, which becomes the base of the hybrid charged adsorbent.
- the mixed liquid of acidic aluminum and silicon solution is thoroughly mixed with the non-polar microporous adsorbent, and then processed into a high temperature furnace, the temperature is 650 ° C - 700 ° C, the temperature is constant for 1 hour, and the material is taken out and pulverized.
- the core of the nano-scale micropores and pores is a non-polar adsorbent and the outer layer is loaded with a polar micro-porous sorbent composition of a silicon- or aluminum-mesh skeleton medium-mixed charged adsorbent, which can be used for meals.
- the treatment of sewage produced In the treatment of kitchen waste resources, the treatment of sewage produced.
- the hybrid charged adsorbent production device and the manufacturing method thereof are as follows: the sewage generated in the whole process of the kitchen waste resource treatment and the domestic sewage in the plant area are treated and reused in the residual sludge.
- the sludge is first input into the manual forced inactivation equipment, and the vertical circulating conveyor cassette in the equipment allows the sludge to reverse from the top and bottom.
- the reaction time is 5-20 min, and the ozone dosage is 12 g/kg.
- the sludge enters the primary curing equipment from the automatic conveying system.
- the equipment is composed of horizontal multi-layer ribbons.
- the steering of the ribbons and ribbons is reversed and smoothed.
- the action of twisting, tearing and tumbling is strongly sheared, and the additive is added by the dosing device for 20-25 min.
- the sludge temperature has naturally risen to about 60 ° C, and the sludge is granulated into a large size.
- the inlet of the reaction kettle is automatically retreated by the guide rail. At this time, the cover of the reaction port of the reaction kettle is sealed and closed, and the inside of the kettle is in an anaerobic operation state.
- the temperature in the kettle is 30 ° C / min, the final temperature is 220 ° C, and the temperature is kept constant for 1 hour.
- the sludge is heated in the kettle. During the solution, water vapor and flammable gas will be generated.
- the one-way valve at the rear end of the reactor is automatically opened, and the vapor and flammable gas mixture is pressed into the water-sealed safety equipment and allowed to contain water.
- the gas enters the heat exchanger, and the non-liquefiable gas generated at this time is flammable gas, and is returned to the pyrolysis furnace through the pipeline as a supplementary raw material for the heat source.
- the automatic discharge screw provided in the kettle is discharged from the discharge port on the side of the kettle, and sent to the aging warehouse by the conveying equipment, which is naturally aged for 12-48 hours, and then will be naturally aged.
- the sludge is placed in the acidification equipment, and the sludge is statically immersed for 12 hours in a concentration of 20% sulfuric acid solution, which acts to remove the dead body residue of the coking microorganism and remove the metal impurity ions, so that the hydrogen ion replaces the additive. Calcium ion.
- the sludge has exposed the pore structure skeleton of the particles, and the acidified sludge particles are put into a hot water rinser at 80 ° C for rinsing and pH adjustment, and then enter the hot steam bed for physical activation, and the hot steam flow rate is 250 mL/min.
- the activation time is 1.5 hours, and the physically activated sludge particles are input into the high temperature resistance furnace, the heating rate is controlled to be 20 ° C / min, the activation temperature of the isolated air is 650 ° C - 700 ° C, and the constant temperature activation time is 1 hour - 1.5 hour.
- a non-polar adsorbent has been prepared as a base nucleus of the hybrid charge adsorbent. Further, the prepared non-polar adsorbent is further processed into particles of a certain size, and then uniformly mixed with the acidic aluminum solution and the silicon solution. When mixed, the weight ratio of the non-polar adsorbent, the acidic aluminum solution and the silicon solution is mixed. 20:20:10, the mixture is placed in a high temperature furnace, the treatment temperature is 680 ° C -720 ° C, constant temperature for 1 hour, after the temperature is reduced, the hybrid charge adsorbent is prepared.
- the exhaust gas, the hot flue gas, the dust, the exhaust air, and the like generated in each process of the kitchen waste recycling treatment are collectively processed by the exhaust gas environmental protection processing device to ensure that the air discharge port has no irritating odor discharge, No harmful toxic gas emissions, no odorous gas emissions, no micro-particle emissions, no room temperature emissions.
- the exhaust gas environmental protection device of the present invention mainly comprises an exhaust gas buffer device, an air inlet, a primary purification pipeline, a primary gas, water, and a solid.
- the starting point of the whole system is the exhaust gas buffer S247
- the outer exhaust buffer S247 has a cylindrical shape and the bottom is Conical
- exhaust gas buffer S247 is provided with a plurality of air inlets S272 inside the casing
- the air buffer chamber is filled with water body
- the top end surface formed by the water body is the water body interface S248,
- the bottom of the exhaust gas buffer S247 is equipped with the sewage outlet S249.
- the sewage outlet S249 is connected to the inside of the circulating water tank S258 through the pipe section
- the circulating water tank is connected with the water circulation pipe 4, which acts on the water body inside the buffer to ensure the interface position of the water body and the water body to cool down.
- an in-line liquid level monitor S251 is also installed in the exhaust gas buffer S247 for real-time monitoring of the water body interface height inside the exhaust gas buffer S247.
- a circulating water tank S258 is arranged outside the exhaust gas buffer S247, and the circulating water tank S258 is connected to the sediment pool S270 through the pipe section.
- the sewage outlet S249 side in the exhaust gas buffer S247 communicates with the upper part of the circulating water tank S258 through the pipe section S275, and the water pipe is arranged on the pipe section.
- the upper part of the circulating water tank S258 is connected to the automatic circulating water pump S252 through the pipe section, and the automatic circulating water pump S252 water outlet is connected to the middle of the exhaust gas buffer S247, and the circulating water is discharged through the water curtain spraying nozzle 26 in the exhaust gas buffer.
- the upper side of the exhaust gas buffer S247 is provided with a primary flue gas treatment pipe S253.
- the upper, the left and the right sides of the primary flue gas treatment pipe S253 are misplaced with a plurality of negative ion-charged ceramics S254, the negative ions.
- the charged ceramic does not need to be powered to start, and can naturally release negative ions.
- a high-speed water mist nozzle S255 and a concave obtuse angle deflector S256 are installed, and the high-speed water mist nozzle S255 is behind the negative ion-charged ceramic S254.
- the multi-layer water curtain is formed at the end, which is a high-pressure water mist area of negative ions, and the obtuse angle baffle acts on the instantaneous airflow path direction of the high-speed flue gas, so that the moving direction of the dense dust particle does not flow along the gas direction.
- the primary flue gas treatment pipeline S253 is inclined, the front end of the primary flue gas treatment pipeline S253 is connected to the exhaust gas buffer S247, and the primary gas, water and solid separator S257 is connected to the rear end of the primary flue gas treatment pipeline S253.
- a carbon slag filter S271 is disposed under the gas, water, and solid separator S257 for filtering the carbon residue in the sediment in the primary gas, water, and solid separator S257.
- the primary gas, water, and solid separator S257 is connected to the twin-tower rotary sprinkler system S259 through a water-gas mixing conduit.
- the water body is sent to the next-stage water-gas mixing pipe, but the gas is introduced into the twin-tower rotary sprinkler system S259 by the draft fan device.
- the double-tower rotary sprinkler system S259 includes two vertical processing towers arranged side by side. After the flue gas first enters one of the processing towers, the gas flows from top to bottom into the lower part of the other tower body.
- the gas is further operated from bottom to top in the lower part of the tower, and at the same time, the rotating high-pressure nozzle S260 installed around the periphery of the double tower sprays water on the gas, and the gas is smoothly cleaned, and the bottom of the double tower is provided with a water outlet S261.
- the water outlet S261 flows into the water and gas mixing pipe, and the cleaned hot flue gas has been formed into the water and gas mixing pipe S263 by the air introducing device S262 installed outside the tower.
- the water The gas mixing pipe S263 is installed in a horizontally inclined manner to connect the air guiding device.
- the water and gas mixing pipe S263 has a slightly higher end and the other end is slightly lower, and the water body discharged from the water outlet of the lower part of the double tower rotary sprinkler system S259
- the hot gas derived from the induced draft fan directly enters the water and gas mixing pipe S263 to the slightly lower end and enters the flue gas discharging device S264.
- the flue gas discharge device S264 includes three parts, the lower part is a tank S265, and the top of the tank S265 is connected to a heat exchanger S266, and the upper part of the heat exchanger is a gas.
- the discharge pipe S267 wherein the lower tank S265 is connected to the water outlet of the water and gas mixing pipe S263, and the wet slag discharge port and the water outlet S268 are provided on one side of the lower tank S265.
- the circulating water in the heat exchanger S266 is supplied from the cooling tower S269, and the cooling tower S269 sucks the water in the sedimentation tank S270 through the pump and delivers it to the heat exchanger S266 through the pipeline, and the hot water in the heat exchanger S266 After the gas is cooled, when the hot water enters the heat exchanger S266, the steam is cooled and liquefied into a water body to fall, enters the lower tank S265, and is discharged through the water outlet S268, and the dry gas that cannot be liquefied is discharged from the discharge port.
- the gas discharge temperature is not higher than 38 °C.
- the exhaust gas environmental protection treatment device of the present invention mainly comprises an exhaust gas buffer device added to the front end of the exhaust gas treatment system, and the structural design thereof.
- the structure of other parts of the exhaust gas environmental protection treatment device of the present invention can be referred to the prior Chinese patent application for application. No. 201010168879.2, the publication number is CN101816874A, and the structure of the patent is substantially the same as the exhaust gas environmental protection treatment device in the present invention.
- the exhaust gas environmental protection treatment device of the present invention can centrally treat the flue gas, hot flue gas, dust, and exhaust air generated in each process of the kitchen waste resource treatment, and ensure that the air discharge port has no irritating odor discharge, and no Harmful and toxic gas emissions, no odorous gas emissions, no micro-particle emissions, no room temperature emissions.
- the exhaust gas environmental protection treatment device of the present invention can desulfurize the exhaust gas and reduce the carbon dioxide emission, and can also remove the carbon dust particles contained in the exhaust gas, thereby achieving no pollution and almost no white smoke emission, effectively changing the conventional gas furnace.
- the weak acid corrosion generated by the tail exhaust gas discharge process causes the pipeline to be easily damaged, which guarantees the service life of the system.
- the exhaust gas environmental protection treatment device of the invention can also reduce the temperature of the exhaust gas to substantially the same emission as the atmosphere, thereby also ensuring the service life of the system.
- the odor generated in the whole process is also processed by the plasma photocatalyst negative ion air deodorizing and sterilizing device, and the plasma photocatalyst negative ion air deodorizing and sterilizing device is applied to the odor overflowing in the processing of each kitchen waste and the entire workshop.
- the air is collected and collected to continuously and efficiently remove harmful microorganisms, kill bacteria and viruses, and degrade the odor in the air.
- the air inlet T270 of the plasma photocatalyst negative ion air deodorizing and sterilizing device of the present invention is installed around each kitchen garbage collecting pool to ensure the prevention of the spread of pollutants and the possibility of overflowing odors.
- the production section and the upper part of the production workshop are equipped with an automatic slide gate valve T271 at the rear end of each air inlet T270.
- the automatic slide gate valve T271 is controlled to open and close by a pneumatic device or an electric device.
- the automatic slide gate valve T271 is used to prevent air treatment. When the equipment is faulty and the machine is shut down for maintenance, it is ensured that the pollution source does not spread.
- the rear end of the automatic slide gate valve T271 is connected to the air conveying pipe T272, and the negative ion corrugated plate T273 is provided in the air conveying pipe T272 (in this embodiment, the plastic used for the energy plastic carrying device is used.
- the raw material is coated on both sides of the steel plate, and then formed into a corrugated shape by pressing and bending.
- the front end of the air conveying pipe T272 is installed at a distance of 30 cm - 80 cm from the entrance end, and a plurality of stacked stacks of 15,000 pieces/cm 3 are installed.
- An anion corrugated sheet T273 (designed according to the pipe and air volume), where the negative ion corrugated sheet T273 is horizontally mounted
- the vertical negative ion corrugated plate is installed vertically at the rear end of the horizontally mounted negative ion corrugated plate.
- a horizontal negative ion corrugated plate is combined with a vertical negative ion corrugated plate, and when implemented, You can set multiple segments according to actual needs.
- each segment of the negative ion corrugated plate comprises more than one piece, and the spacing between the plates and the plate is 10 mm.
- the end of the air conveying pipe T272 is connected with a photocatalytic main processor T274. After the air is processed through the negative ion zone, the air is guided by the induced draft fan installed in the photocatalytic main processor T274 to the tail end of the air supply duct, and then enters. Photocatalytic main processor T274.
- the photocatalytic main processor T274 is provided with an air passage, the air passage is a Z-shaped air passage, the Z-shaped air passage is a Z-shaped guide plate T275, and the Z-shaped guide plate T275 is a mirror aluminum alloy plate.
- the light emitted by the ultraviolet light pipe T276 light source is reflected in the Z-shaped air channel, and the Z-shaped air channel is provided with a plurality of ultraviolet light pipes T276 (horizontal mounting) with an emission wavelength of 253 nm - 258 nm, each ultraviolet light
- the back surface of the light pipe T276 is equipped with a smooth reflecting plate T277 for reflecting the light source emitted from the ultraviolet light pipe T276 into the air passage to maximize its function.
- a honeycomb-shaped titanium dioxide photocatalytic contact plate T278 is installed at a distance of 10 cm to 20 cm behind the ultraviolet light pipe T276.
- the size and shape of the photocatalytic contact plate T278 are the same as the Z-shaped air passage cross-section, and can be just blocked.
- the photocatalytic contact plate T278 has a thickness of 1 cm - 10 cm, and a plurality of holes are formed in the upper portion, and a plurality of plasma generators T283 are installed at a corner position of the Z-shaped air channel of the photocatalytic main processor T274, and the plasma is installed.
- the discharge power of the generator is 2.5WH/m 3
- the tail end of the Z-shaped air passage in the photocatalytic main processor T274 is connected with an air discharge pipe T279, and the tail end inside the air discharge pipe T279 is installed with a negative ion amount that can be released.
- 15000/cm 3 stacked second negative ion corrugated plate T280, the second negative ion corrugated plate T280 has the same structure as the first negative ion corrugated plate T273, and the air passes through the laminated second negative ion corrugated plate T280 and enters the activated carbon air filter. After the T281 treatment, it is discharged.
- the activated carbon air filter T281 is provided with activated carbon in the outer casing to carry out the final activated carbon adsorption on the gas.
- the plasma photocatalyst negative ion air deodorizing and sterilizing device of the present invention operates as follows: when the kitchen waste enters the collecting pool, the air introducing device of the present invention is activated, and the automatic sliding gate valve T271 at the front end of the air collecting pipe around the pool is opened. If the production workshop or other collection pool does not need to handle the air, the automatic slide gate valve T271 at the front end of the air collection pipeline is closed. If the production workshop or other collection pool also needs to handle the air, the front end of the collection pipeline The automatic slide valve is open. Due to the action of the air blower, the air containing bacteria and odor is processed into the negative ion laminated corrugated plate T273 in the pipe through the gate valve T271.
- the corrugated plate and the corrugated plate is 5 mm—— 10mm
- the negative ion laminated corrugated plate T273 releases 15000 pieces/cm 3 of negative ions and does not need to be energized. It carries out the first capture and killing of the cells and odors with cations in the passing air, after the first killing and
- the deodorizing gas enters the plasma processing zone along the air conveying pipeline under the strong action of the air deflector, and then continues Continue to enter the photocatalytic main processor T274, the gas enters the main processor and moves from bottom to top in the zigzag direction.
- the gas is installed under the ultraviolet light emitted by the ultraviolet light tube T276 of the four walls of the Z-shaped channel, and then enters the honeycomb.
- Hydroxyl radicals and superoxide ion radicals these capabilities are far higher than the strength of the general organic pollutant molecular chain, so when the air enters the Z-shaped channel, the organic pollutants in the air are decomposed into the most primitive state, especially After several times of repeated photocatalytic treatment of air in the Z-shaped air passage, the bacterial virus in the air has been effectively removed, and the odor in the air is simultaneously degraded, in order to further ensure that the discharged air is fresh and qualified, in the Z-shaped air passage.
- the plasma generator 13 is installed at the corner position to enhance the degradation and removal of pollutants, and has been subjected to photocatalysis and plasma combined treatment.
- the plasma photocatalyst negative ion air deodorizing and sterilizing device in the invention can collect and treat the odor overflowing in each section of the kitchen waste treatment process and the air of the entire workshop, and continuously and efficiently remove harmful microorganisms from the collected air. Kill bacteria, viruses, and degrade the odor in the air.
- the gas discharged at this time is odorless, sterile, free of solid particles, free from toxic and harmful substances, and fresh and clean.
- the automatic control device in the invention is mainly applied to the automatic intelligent control of the production process of the kitchen waste feeding, screening, cleaning, biochemical treatment, drying and fine screening in the process of the kitchen garbage resource recycling process, and the control system is well-known. technology.
- This device adopts multiple PLCs in parallel to complete the central control function.
- Each PLC has its own independent program.
- Each field electrical unit and operation command collects signals through PLC to RS-422 communication.
- the method is transmitted to the upper computer to form a complete distributed control system. All electrical control units are divided into several large-scale on-site control units according to the operation requirements of various production equipments on site, and independent program control is established, and the main operation room is established.
- the integrated equipment and method for all-round processing of kitchen wastes is a set of domestic and foreign kitchen processing industry for the first time with high integration, automation and comprehensive comprehensive equipment, compatible with kitchen waste
- the method of resource treatment is inevitable, adapting to the trend of the international environmental protection industry, and implementing the safe disposal and disposal direction of the residue after the comprehensive treatment of waste is not transferred and digested, and secondary pollution is not generated.
- the application of the invention provides kitchen waste and its inevitable attachments - waste plastic bags, drowning sludge and domestic sewage in the plant, industrial sewage and sludge produced in the production process, various large systems in the same equipment The processing method in the device.
- the application of the present invention provides various high value-added product names, manufacturing methods and uses thereof after the comprehensive recycling of the kitchen waste.
- the application of the invention provides a comprehensive energy-saving production, safe production, no residue transfer treatment for the kitchen waste treatment industry, no room temperature discharge, no odor emission close to the clean production method and mode without sewage discharge.
- the products produced by the invention are National III mineral diesel, low sulfur and high calorific value clean environmental protection coal, and gas three strategic energy sources, which can alleviate the pressure of social supply and demand.
- the high-nutrition microbial protein feed additive produced can effectively fill the gap of the lack of high-protein additives in domestic feed.
- the invention provides a novel garbage carrier (barrel) production method capable of naturally sterilizing and deodorizing the kitchen garbage carrier (barrel) and providing clean air around the outer periphery of the barrel, which is an application surface extremely A wide range of new environmentally friendly cleaning appliances.
- the present invention is a complete set of integrated kitchen waste processing equipment, a plurality of special large-scale devices and systems are assembled, each having its own independence and application range, but also having coherence and detour between the devices and the devices. In order to more clearly and completely express the application mode and production process of the complete equipment and its related methods and related formulas, the actual case description.
- the kitchen waste used is from restaurants, hotels, Chinese restaurants, western restaurants, government canteens, school canteens, etc. in a prefecture-level city in the Pearl River Delta of the People's Republic of China.
- the production rate of the products in the case and the methods and related formulas used in the production are set according to the dining habits, characteristics and food quality of the humanities in the area.
- the kitchen wastes referred to in the specific embodiment are clear.
- the transportation work is carried out by the environmental protection and transportation enterprises designated by the relevant government departments.
- the whole set of equipment for comprehensive treatment of kitchen and kitchen waste is provided by South China Renewable Resources (Zhongshan) Co., Ltd., and the specific implementation location is at the kitchen waste processing base in the company.
- the base daily processing capacity is set to 200 tons, and the embodiment, the production process and method, and the related formulations of the integrated equipment for processing 50 tons per day are described as a specific embodiment of the present invention.
- this collection bucket is a loading tool distributed to the source of each kitchen, and is also a transport tool from the source to the processing plant. It protects the source of the sanitary environment and avoids transit. The possible secondary pollution has a very important key. Therefore, it is necessary to use a kitchen waste bin with a sterilization and deodorization function in the barrel and a negative oxygen ion fresh air around the barrel.
- the specific manufacturing method is as follows: :
- the carbon black is subjected to ozone oxidation treatment, and the carbon black particle size is ⁇ 2 um.
- the ozone oxidation treatment is a conventional oxidation treatment of the carbon black by the ozone oxidation equipment in the prior art, so that the internal surface area of the carbon black is increased by more than 4 times. This promotes the adsorption capacity of carbon black.
- the treated carbon black is thoroughly mixed with the nanometer tourmaline powder as a base material, wherein the carbon black accounts for 15% of the total weight of the base material, and the nanometer tourmaline powder accounts for 85% of the total weight, in the mixed base material.
- ultrafine titanium dioxide is added and further mixed as an energy raw material, and the ultrafine titanium oxide is added in an amount of 10% by weight based on the total weight of the base.
- the mixed energy raw materials are further dried at 100-120 ° C for 1-2 hours (the mixed energy raw materials are completely dried).
- the energy raw material is added with a dispersing agent, and the dispersing agent adopts a coupling agent related to the basic resin, in particular, a coupling agent which is used to facilitate mixing with the carrier resin, and the dispersing agent is added in an amount of 3% of the energy raw material.
- a coupling agent which is used to facilitate mixing with the carrier resin
- the dispersing agent is added in an amount of 3% of the energy raw material.
- One of the dispersing agents selected in the present embodiment is magnesium stearate.
- the energy raw material added with the dispersing agent is further added to the plastic carrier resin, and uniformly mixed to form a well-mixed village material.
- the plastic carrier resin used in the embodiment is PE, and the ratio of the amount of the plastic carrier resin to the energy raw material is 30%: 70%.
- the mixture described above is input into a special mixing equipment for kneading, and a coupling agent is further added during the kneading process.
- the coupling agent selected in the embodiment is an aminoalkane coupling agent, and the amount thereof is added.
- the ratio of the total weight of the energy raw material to the plastic carrier is 2%: 98%, and the mixing temperature is set at the normal temperature of the mixed resin, and the plastic energy is made when the kneaded material passes through the extruder and completes the cooling and pelletizing process. Masterbatch.
- the further output energy detected plastic masterbatch which measures infrared radiation in the wavelength range of 4-16, the whole firing process was ⁇ 0.86, a concentration of 7000 ions / cm 3 or more, when it is determined masterbatch
- the energy masterbatch that meets the production standard is mixed with HPPE and ABS plastic rubber particles.
- the mixing ratio of PE and ABS is determined according to the load weight of the kitchen waste bin, while the energy masterbatch accounts for three.
- 70% of the mixed plastic resin is finally injection molded by a professional injection molding machine to form a barrel and a lid.
- the flow rate of the solution and the temperature of the barrel, the mold temperature control, and the injection pressure are all Production technology methods according to industry routines.
- the prepared kitchen garbage container is assembled and tested to naturally release more than 5,000/cm 3 of negative ion content, and then distributed to each kitchen garbage collection point, thereby ensuring that the kitchen waste is from entering the receiving bucket. Will not smell bad in hours.
- the environmentally-friendly cleaning and transportation enterprises designated by the government collect and deliver the kitchen waste carried by the above-mentioned carrying barrels to the processing plant area.
- the collection port is operated by the main control room to open the sluice cover, and the vent gate valve disposed around the upper side of the collection port is opened, and the plasma photocatalyst negative ion air treatment system is activated. .
- the kitchen waste is sent to the collector by the automatic unloading equipment.
- the collection device brake cover is automatically closed. Since the air treatment system has been activated, the odor of the garbage is introduced into the treatment device to sterilize and deodorize.
- the air environment in the plant area is fresh, and at the same time, after the kitchen waste enters the collector, the horizontal automatic gate valve in the lower part of the device is opened, and the garbage naturally falls into the propelled bag breaking device.
- the kitchen waste enters the discharge pipe after breaking the bag, and uses the water flow force to send the kitchen waste into the liquid air flotation sorting device.
- the main sorting device of the device is 6m 3 , which is set at the main
- the semi-floating material discharge louver opening in the middle and lower part of the sorting device is closed, and the water body starts to inject water into the main device bucket through the water pipe system.
- the water injection amount is based on the set water surface height, and is controlled by the liquid surface automatic positioner.
- the sub-input kitchen waste is 1/3-1.5/3 of the total cubic volume of the main unit water body. When the water body rises to the set liquid level, the main and auxiliary rolls placed on the upper part of the main unit are shifted by the motor.
- the box starts to roll, and the compressed air valve located at the lower part of the main device is opened, and the high-pressure air emitted from the plurality of gas nozzles is used to flip the kitchen waste immersed in the water body under the buoyancy of water, and the plastic with lower density at this time
- the debris such as cloth strips and toothpicks floats to the upper layer of the water body, and is swept upward by the rolling caries, and is captured by the auxiliary caries provided on the upper part of the main roll side and then discharged to the light debris collection bucket.
- the louver opening in the middle and lower part of the water body is opened, and the kitchen waste of the semi-floating layer is pressed against the louver mouth by the hydraulic pressure difference of the main device water body, and enters the auxiliary device.
- the circulating water pump is started to deliver water to the buffer water tank and the main device is replenished.
- This action is to ensure that the liquid level of the main device is higher than the liquid level of the auxiliary device, when the semi-floating layer
- the valve at the discharge opening of the main device is opened, and the density at the bottom of the device is large or large, such as: metal debris, glass, broken Porcelain pieces, heavy debris and discarded small quantities of raw chicken, duck, fish or large pieces of meat in the kitchen waste are discharged from the residue discharge port and delivered to the set location by automatic conveying tools.
- the selected kitchen waste is selected into the input crusher, and after the liquid air flotation is sorted, the food waste that is beneficial for the production of protein feed has been basically carried out for the first time. Desalination step and cleaning process.
- the used kitchen waste that has been sorted is discharged from the discharge port of the auxiliary device in the liquid air flotation sorting device and automatically sent to the first-stage reactor and the second reaction of the wet advanced oxidation device through the conveying tool.
- the internal cavity of the secondary reactor is 5m 3 , the amount of kitchen waste is 5T, and the fresh water is injected 2T.
- the input of both is controlled by an automatic quantitative tool and passed through a liquid level controller installed in the kettle. Set the height of the water level in the reactor.
- the waterproof check valve mainly acts to prevent the water from flowing back into the ozone generator. While the ozone gas enters the gas-water mixer, the high-viscosity cam rotor pump installed between the circulation pipes is started, and the blend of the kitchen waste and the water body is strongly pushed into the water, gas mixer and into the mixer.
- Ozone gas implements kitchen waste-water-ozone gas mixing, and promotes the dissolution of ozone in the activated water, and then enters the reaction kettle, and another cam rotor pump pumps the kitchen waste in the reaction kettle-water- - the mixture of ozone gas is strongly input into another reaction kettle, and the reaction is repeated as a reaction process, especially in the case where the ozone-containing material is acted upon by the activated carbon fixed reaction ball in the reactor, causing a chain reaction in the mixture to accelerate the ozone Conversion to hydroxyl radicals, similar to the advanced oxidation process of O 3 /H 3 O 3 or O 3 /UV, the above reaction of organic matter, bacteria and microorganisms in kitchen wastes is instantaneously dispersed in water with oxidation of single primary oxygen Very rapid, single primary oxygen O and hydroxyl radical OH can forcibly inactivate pathogens and spores in kitchen waste within 1-2 minutes.
- the pump port The working pressure is 0.25mpa, the conveying strength is 500kg/min, the reaction time of the mixture in the kettle is 10min, and the ozone concentration in the kitchen waste water is 12g/T.
- the gas overflow port and ozone are arranged in the upper part of the reactor.
- the destroyer is always on, and the process of desalting and inactivation of the original bacteria has been completed after the kitchen waste has undergone advanced oxidation. Effectively ensure the quality of inoculation and expansion work in the subsequent protein feed production process, and effectively eliminate the interference of bacteria and remove the salt into the kitchen waste.
- the kitchen waste processed by the previous step is discharged from the discharge port at the lower part of the reactor and enters the primary solid-liquid separator. After separating most of the water body, the kitchen waste having a water content of about 85% is obtained, and then the snail is obtained.
- the belt conveyor is gradually fed into the vertical dewatering device, and the adjustable water pressure plate installed on the upper part of the dewatering device is adjusted by the hydraulic device to the closed state, and the middle shaft running through the shaft center of the ribbon is driven by the gearbox with a 3.7KW motor, and Rotating at 580 rpm, the electric ball valve connected to the water outlet of the water separator installed in the lower part of the dehydration tower is automatically opened.
- the kitchen waste is put into the feeding port at the lower part of the dehydration tower, and the kitchen waste is large.
- the extrusion action of the small spiral ribbon and the shell and the resistance of the water pressure plate at the top of the tower increase the material conveying resistance.
- the discharge door provided on the top side of the tower automatically opens. This discharge port is controlled by hydraulic pressure.
- the kitchen waste is continuously pushed up to the dewatering zone through the concentration zone in the lower part of the dehydration tower, and continuous dewatering and discharging are carried out, and the removed water body flows out from the grid of the tower body shell and is disposed along the grid.
- the outer baffle of the fixed ring flows into the water receiving device and is discharged through the drain port.
- the discharge amount of the dehydrated material is 8T/h, and the continuous running time of the dehydration tower is set no more than 8 hours. After the shutdown, it is installed around the dehydration tower.
- the high pressure water recoil nozzle cleans the water outlet gap of the grid strip.
- the rated working pressure of the water outlet is 0.35mpa, the water supply intensity is 14L/min, and the cleaning time is 10min.
- the route connected to the upper process is divided into two processes of different working properties, one of which is: an oil extraction process.
- the oil-containing water body above the middle of the pool is input into the oil-water separation tower by using a water pump, and the oil-water separation tower is used. It is composed of two towers, and there are pipelines in the middle. The two towers are all cavities. The total volume of the cavity is 60m 3 and the water body is 50m 3 .
- the heating pipeline inside the tower The hot gas enters the water body through the heat transfer of the pipe wall, and the hot gas source is collected in the hot tail gas of the heat transfer oil boiler for production.
- the oil in the water body is heated to 80 ° C, the oil in the water body is completely separated from the water, and the upper layer is upward. Floating up and naturally entering the upper part of the inclined partition provided in the upper part of the oil-water separation tower, flowing down the inclined surface of the partition into the oil-bearing bearing area, and then passing the oil through the oil discharge pipe through the scraper plate installed in the bearing area Into the biodiesel production area, the resulting oil is about 180kg.
- the temperature of 80 ° C most of the bacteria and microorganisms are inactivated in the water body at the lower part of the oil-water separation tower, and are input into the sewage treatment zone through the drain port at the lower part of the tower.
- the other of the two different working properties described above is the crushing process: when the kitchen waste discharged from the dewatering process is about 45%, and the pneumatic pusher is input into the crusher for crushing, this is a well-known technique. This is no longer stated.
- the two pre-biochemical fermenters have an internal volume of 10m 3 Entering 7 tons of kitchen waste, another pre-biochemical fermenter with an internal volume of 30m 3 , entering the kitchen waste and the fiber nutrient material input from another straw biochemical fermentation device, the intermixing of kitchen waste and fiber nutrients
- the ratio is determined by the type of feed that is ultimately produced by the visual symbol. In this embodiment, each accounted for 50%, but the total weight of the two entered the biochemical fermenter was 20 tons.
- the biochemical treatment of 7 tons of kitchen waste is based on the use of baker's yeast as a strain.
- the bran is added to the base by 2% by weight of the base material, 2.5% of rice bran, and 1% of brown sugar is mixed and adjusted.
- the bread yeast is added to the mixture by 3% by weight of the base material, and fully stirred to enhance the aeration to enhance the growth of the yeast.
- the fermentation time is 12 hour.
- Another biochemical processor containing 20 tons of mixed-mix kitchen waste was put into the combined compound strains of Trichoderma viride and Candida tropicalis and Pseudomonas and Pseudomonas syringae. Directly fed microorganisms in the Chinese Species Catalogue.
- the ratio is 2:2:1:1, and the inoculation amount is 3% of the substrate quality.
- the inoculation method is that the composite strains are added one after another, and 0.5% urea is added, and the biochemical fermentation is continued for 10 hours.
- the heat source of the fermentation is feed.
- the waste heat of the dryer is provided, the temperature is set to 32 ° C, the ventilation condition is 8 min / h, the ventilation is 0.2 m 3 / h, and the green wood mold in the strain with the white fungus reduces the crude fiber content of the base material extremely significantly, and Candida tropicalis, white fungus and Trichoderma viride can increase the crude protein and true protein to a significant level, and use the endophytic bacteria as the auxiliary mold, the first expansion of the pre-biochemical fermenter.
- the implementation of this case is in the Pearl River Delta region of southern China. Therefore, the type of straw selected in this case is selected locally, with local legume straw and grass.
- the wood crops are mixed with straw, using peanut stalks, broad bean stalks, bean stalks of legume stalks and rice stalks, sugar cane heads and tails, and corn stalks of the current season, such as wheat stalks.
- the above-mentioned straw combination is based on the high content of straw protein such as legume crops, but the sugar content is low, and the microbial activity is not high at the initial stage of fermentation, and then mixed with the straw straw containing higher soluble sugar content, not only Improve the quality of the fermentation, and make the nutrients of the two types of crop straws complement each other, so as to achieve better feed quality.
- the ratio of the two types of straw is 60% for legumes and 40% for straws.
- the crop stalks are properly cleaned, kicked out the rotten, moldy parts and dirt, sand and other debris, and exposed to the surface to remove the surface moisture, inhibit the growth and reproduction of the mold, and smash the straw into 0.5-1 mm by the pulverizer. Powder.
- the chemical composition of 2 kg of calcium oxide, 0.2 kg of sodium chloride, 3 kg of sodium hydrogen phosphate and 0.5 kg of urea is added, and the weight of the chemical component is required per ton of straw.
- the chemical component acts on the decomposition of lignin, softens the straw, destroys the crystal structure of the plant cell wall, breaks the physical and chemical state of the close combination of lignin and cellulose, improves the biochemical treatment effect and the palatability of the feed.
- the above-mentioned activation liquid and chemical components are uniformly stirred to obtain a fermentation liquid.
- the fermentation broth is sprayed into the material in the biochemical fermentation tank, the ratio of the straw to the fermentation broth is 1:2, and then the materials of several pools are uniformly stirred by the automatic stirring device installed on the side of the biochemical pool for about 10 minutes.
- the material was compacted after the end of the agitation.
- the biochemical fermentation tank cover is sealed and closed by a hydraulic automatic system, and the biochemical treatment time is 7-9 days in the next season, and the required temperature is normal temperature.
- the composite microbial agent biochemically treats the straw, so that the crude fiber is effectively degraded and saccharified, and the rich bacterial protein and physiological active substance are synthesized, and the biological energy contained in the straw is not consumed. Therefore, under normal conditions, no heat phenomenon and gas production phenomenon and swelling phenomenon will occur.
- the biochemical treatment of the straw the color is bright and golden yellow, the hand feels delicate and soft, the aroma is rich, and the wine is slightly scented.
- the material of the pre-biochemical treatment will now be stated. After 10 hours of pretreatment, the material is input into the lower two groups of main biochemical devices by a screw conveyor at the bottom of the biochemical device.
- the volume of the main biochemical chamber of each group is 20 m3.
- Baker's yeast is a kind of material, and it needs to remain about 10% to enter the main biochemical device, which is used for the next fermentation, because the next fermentation is the old fermentation method.
- the automatic slide gate valve of the material delivery port installed between the main and auxiliary biochemical devices is closed.
- the rotation speed is 7 rev / min, for horizontal 360o rotation, the direction of the outer ribbon of the agitator In the forward direction, the direction of movement of the inner layer of the ribbon is reversed.
- the heat transfer oil is output from the heat transfer oil boiler, and is sent to the two sides of the biochemical device through the heat pump, and the material is heated by the heat transfer of the biochemical case, according to the aerobic or anaerobic conditions and bacteria of various selected strains. The optimum conditions for the breeding conditions to adapt to the temperature conditions.
- the initial temperature is 20 ° C, gradually increase to 28 ° C, after 4 hours of constant temperature, close the air inlet and outlet, and gradually increase the temperature to 35 ° C -38 ° C, after a constant temperature of 3 hours, this period of biochemical fermentation of oxygen supply
- the points are between the gap between the source materials and the specific area.
- the kitchen waste that has undergone biochemical fermentation has been converted into microbial protein feed, and the water content is about 35%.
- the main biochemical fermenter is opened at the discharge port on the bottom side, the feed is discharged into the feed hoist and is lifted.
- the machine is sent to the pre-drying device in the drying device.
- the hot air of the pre-drying device is derived from the exhaust heat of the main drying device, and the hot gas enters the outer casing of the pre-drying device, and the inner cavity is heated by the heat-conducting oil in the inner cavity of the device casing.
- the inner cavity volume is 16m3, the feed volume is 8 tons per time, and the inner cavity temperature of the device is 100 °C.
- the middle shaft flap installed in the equipment is rotated by the motor and the transmission, and the rotation speed is 12 rpm. Min, at this time, the feed is rotated by the flap, the material is heated continuously in contact with the hot gas and the wall of the cylinder, and when the feed below the temperature of the cylinder wall of the apparatus continuously contacts the wall of the cylinder, the wall of the cylinder is cooled, but Under the rotation of the flap, the cycle of change is short, the temperature change range is small, the temperature of the wall of the tube can be considered to be constant, and the feed without contact with the wall of the tube is subjected to radiation heat transfer by the heated feed particles, which can also be said to be particles. Surface receiving radiation heat.
- the main drying device is a horizontal shaftless rotary airflow drying device.
- the main drying device in the case of the specific embodiment is a four-layer rotating drum structure, and the inner wall of each layer of the rotating drum is provided with a spiral belt connecting the wall of the cylinder, the innermost rotating drum has a pitch of 150 mm, the cylindrical body has a diameter of 700 mm, and the cylinder length is 4000 mm;
- the next layer of drum has a pitch of 200mm, the cylinder diameter is 1200,mm, and the cylinder length is 4600mm;
- the next layer of the drum has a pitch of 300mm, the cylinder diameter is 1800mm, and the cylinder length is 4600mm;
- the outermost drum is the main drum of the drying equipment.
- the pitch is 450mm, the diameter of the cylinder is 2200mm, and the length of the cylinder is 6000mm.
- each layer of the drum is based on the outer drum.
- Several fixed brackets are installed in the circumference of the inner drum, which are fixed one by one.
- the rotation speed of the drum is 29 rpm, and the upper part of the tail end of the main drying equipment is equipped with an exhaust port.
- the hot air is led by the air blower.
- the heat source of the main drying device is generated by the diesel injection burner in the combustion chamber, and the hot air is sent into the drying device by the adjustable reverse fan disposed at the side of the combustion chamber.
- the feed is started when the inlet temperature is 280 ° C and the outlet temperature is higher than 110 ° C.
- the feed rate is 20 kg/min, and the gas flow rate is 1.2 m/s.
- the feed first enters the innermost rotating drum and then advances in contact with the hot air flow in the forward direction of the spiral belt.
- the feed reaches the end of the rotating drum, it naturally falls into the next layer of the rotating drum and advances with the advancement direction of the spiral belt. After countercurrent contact with the hot air flow, it naturally falls into the next layer.
- the direction of the drum's forward direction is in contact with the hot air flow in the same way as the innermost drum.
- the feed finally falls into the main drum and follows the snail. Push the belt forward to the discharge port.
- the sleeve type horizontal drum is used to extend the forward track of the feed to ensure that the material has sufficient residence time contact with the hot air, and the moisture in the feed is quickly evaporated by the heat energy.
- the dried feed is gradually fed into the feed selection device through the conveying equipment, and the feed drum is rotated by the inclined drum in the device, and the movement track is continuously rolled forward, and at this time, the large number of the mesh of the drum screen cannot be passed.
- the article or heavy object is fed into the ribbon guide at the end of the drum and falls into the mixing box with the direction of advancement of the ribbon, while the feed smaller than the mesh of the roller falls through the aperture into the finished carrier. Then, the mixed materials in the mixing box are subjected to secondary screening to select a slightly larger-sized feed, and then crushed and returned to the finished carrier.
- the calorie consumption energy required for the above biochemical fermentation and feed drying process is about 630 kcal/kg, and the produced product is a high protein nutrient feed with a feed weight of 12.7 tons.
- the quality of the test product is:
- Qualified products are golden yellow, brightly colored, slightly scented and toasted
- High-nutrition feed enters the feed granulation production area. According to the size and adaptability of various aquatic animals, special feeds such as puffed floating materials and semi-floating materials are produced through special equipment. This technique is well known and will not be described here.
- the extracted fat and water enters the biodiesel production area.
- the measured oil and fat was 1.6 tons, accounting for 3.2% of the 50 tons of kitchen waste entering.
- the method for treating this grease is to adopt a distillation-free production method, which has strong adaptability to raw materials, is clean, safe and simple in the production process, and the entire production process is carried out at normal temperature.
- the crude oil and fat in the oil storage tank are first taken out from the container by the oil pump, and sent to the bio-oil lipid removal impinging stream reactor for the removal of the gel. At this time, the installation is started in the impact reaction.
- the hydro-pneumatic propulsion machine at both ends of the machine will force the grease to collide with the orifice plate provided in the impactor.
- 0.8% phosphoric acid is added to the grease in the process, and the continuous phase collides with the orifice plate, and the hole of the orifice plate is used.
- the oil at both ends is strongly traversed by each other for 15 minutes. This step acts on phospholipids that cannot be hydrated in oils, that is to say, non-hydrated phospholipids, especially the symmetry of its structure, affected by the spatial effects of molecular structure, hydrophilic Poor sex, the reason why it is not easy to absorb water and expand, will seriously affect the difficulty and quality of bio-oil processing into biodiesel.
- the strong mixing and scouring of phosphoric acid in oil and fat destroys the micro-metal complex of non-hydrated phospholipids, thereby transforming into Hydrated phospholipids.
- add 10% diluted brine to the oil the input amount is 120kg, and continue to force the oil to collide with each other by means of the rotary pulp at both ends, stop after 20min, and let stand for layering, due to The action of the electrolyte promotes the flocculation of the impurities in the oil in the hydrated phospholipids, and reduces the oil content of the formed colloidal mass.
- the gum in the bio-fat is detached, and the colloid in the oil is effectively prevented from covering the grease particles in the next fatning step, thereby ensuring contact between the grease and the catalyst.
- the colloidal grease is separated from the grease impactor, and then input into the fat exchange reaction vessel.
- the volume of the reaction chamber is 3 m3.
- the radial impeller installed at the bottom is started. At medium speed, the grease is quickly tumbling, and the feed port is opened.
- 80 kg of methanol and 3.2 kg of methyl ethyl ketone and 1 kg of t-butanol are added.
- methyl ethyl ketone and t-butanol are co-solvents, and the co-solvent contains a lipophilic group compatible with the oil.
- a polar group capable of binding to methanol wherein an oxygen atom contained in the molecule forms a hydrogen bond with methanol, promoting mutual solubility of the oil and the methanol, forming a homogeneous system, and effectively accelerating the alcoholysis exchange reaction with the catalyst.
- the base nucleus is then impregnated with a mixed liquid of an alkali silica sol and an aluminum sol and lithium hydride, and then taken out at a temperature of 650 ° C to 720 ° C for one hour. After cooling, it is ground into 50-80 mesh particles, and made into a non-polar adsorbent-based core, which is wrapped with silicon, aluminum-lithium mesh skeleton medium and polar hybrid catalyst.
- the catalyst was immersed in an aqueous KNO 3 solution, taken out, and dried at 110 ° C to obtain a KNO 3 solid alkali metal catalyst having a KNO 3 loading of 25%. This solid catalyst was added in an amount of 24 kg.
- the contact surface between the molecules of the reaction medium is increased, and the reaction is pushed in the positive direction.
- the reaction is installed in the kettle and immersed in the grease.
- the ultrasonic probe is turned on, the number of probes is four, the initial frequency is 25KHz, and gradually increases to 30KHz after 1min.
- the flow of grease is generated by hundreds of millions.
- the cavitation nucleus of the tiny bubble vibrates under the action of the sound field, and when the sound pressure reaches a certain value, collapse cavitation occurs.
- the 1.53 tons of biodiesel produced still has tiny water.
- the above-mentioned biodiesel is used to produce micro-emulsified diesel without dehydration. .
- the water content of the biodiesel was measured, and the water content in the oil was measured to be 4.6 kg.
- the biodiesel is input into the special device of micro-emulsified oil by the oil pump, and the stirring system in the starting device is set to rotate at 128 rpm.
- the composite ion surfactant is added as a hydrophilic agent, and the other is a cationic surface.
- the active agent is a nonionic surfactant
- the above two types of surfactants include triethanolamine, hexahydroaniline and aqueous ammonia and intermediate butanol, the percentage of which is a combination of a cationic hydrophilic surfactant and a nonionic surface.
- the active agents each accounted for 50% and the amount used was 2.5% of the biodiesel moisture content.
- 300 kg of mineral diesel oil is added to biodiesel, and the water content in the total weight of biodiesel and mineral diesel is adjusted to 10%, that is, the amount of water to be added is 180 kg.
- the agitator The speed was changed to 200 rpm.
- Waste plastic processing (waste plastic reversal project):
- the waste plastic is derived from the waste plastics selected by the liquid air flotation screening device described in the sixth step of the present embodiment, and is sent to the waste plastic processing area through the conveyor belt - the waste plastic reverse engineering production area
- a total of 280kg of waste plastics were selected from 50T kitchen waste, including plastic bags, plastic bottles, bottle caps, plastic lunch boxes, as well as toothpicks, wooden chopsticks, cloth strips, etc., special equipment for plastic reversal engineering.
- the minimum feed amount is 2.5 tons, so the waste plastics screened in this case is only 280kg, which can not meet the production requirements of the equipment. Only other waste plastics can be added into 4.5 tons.
- the operation is as follows:
- the waste plastic used does not need to be cleaned, does not need to be screened, does not need to be dried, and is directly fed into the pneumatic automatic feeder through the sealed conveyor belt through the trough, and the waste plastic is continuously used by the reciprocating push-pull action of the automatic feeder. It is sent to the cracking reactor for cracking catalysis.
- the cracking reactor is a horizontal reactor.
- the tank is equipped with a fin-type shaftless random scraping device.
- the shell of the reactor is a cracking furnace body.
- the heat source conditions of the cracking furnace are The micro-emulsified biodiesel at the 13th point in the case is self-fueled.
- the reactor starts to heat up, the lifting speed is 100 ° C / h, and the waste plastic is continuously fed into the reaction.
- the total feeding time of the kettle was 40 min. Thereafter, the set amount of calcium oxide is immediately added, and the calcium oxide reacts with the water in the waste plastic to instantly increase the temperature of the material in the kettle to prevent coke formation, and also convert the chlorine-containing material into calcium chloride and effectively Adjusting the pH value of the reactants, adding 5 minutes after the calcium oxide addition process, adding zinc, aluminum-based metal solid catalyst and non-metal catalyst, the catalyst is added in an amount of 62 kg, wherein the aluminum-based metal solid catalyst acts on the gas, waiting for all After all the additives were added to the reaction vessel, the feed port of the reaction vessel was closed tightly, and the reaction in the autoclave was in an anaerobic state.
- the one-way valve connected to the rear end of the reactor is automatically opened, and the water vapor in the kettle is converted into liquid water from the valve through the first-stage condenser.
- the drain outlet is directly discharged, and the pH of the water is 6.5.
- the material in the kettle enters the cracking process.
- the high-condensation point wax discharged from the reactor sublimation passes through the check valve and enters the wax collector.
- the oil and gas clamp carries a small amount of tiny carbon particles and continues to pass through the oil and gas separation device, the magnetic ring disposed in the device will trap some of the tiny carbon particles, and the oil and gas will enter the secondary heat exchanger.
- the easily liquefied oil enters.
- the oil collector, and the non-liquefiable combustible gas is placed in the gas reverse cleaner by the gravitational force of the negative pressure system of the latter stage, and the negative pressure system is automatically turned on after receiving the gas electronic sensor signal provided in the system.
- the flammable gas passes the first cleaning, it enters the next-stage weak alkaline water washing system, and quickly passes through the rear-stage safety water sealing device to enter the special gas compressor for primary desorption.
- the pressure of the combustible gas is increased to 0.5mpa, and then the secondary gas compressor is introduced to increase the pressure of the combustible gas to 1mpa. After the secondary dehydration, the gas is directly sent to the gas storage reservoir for use.
- the combustible gas is output from the storage tank, after the first stage decompression is 0.4-0.5 mpa, and then the second decompression is 0.1-02 mpa, and is input into the furnace combustion, and the cracking in the case of the specific embodiment
- the exhaust gas of the furnace combustion chamber is treated by the tail gas environmental protection treatment system.
- the oil of the oil collector is input into a special oil-water separator, and the water that has been liquefied at the same time as the oil is introduced into the oil collector is removed, and then input into the diesel refining system.
- the automatic system automatically stops the infusion and opens the gas collector and odor destruction system at the top of the reactor.
- the stirring device disposed in the reactor is opened, the oil material is in a flow-cutting mode, and the gas agitation system in the lower part of the reactor starts to start, and the oil flow direction rapidly hits the baffle disposed around the inner surface of the synthesizer.
- the quantitative additive device is added to the oil in batches according to the set additive component, two of which are acidic catalyst and acid white clay, etc., when the additives are all added in order, the reaction time is 30 min.
- the oil after decarburization and degumming is discharged through the oil output port provided on the bottom side of the reactor, and then enters the second stage dewaxing, neutralization, quality adjustment synthesis system.
- the stirrer inside the device is started, and the additive is added by the quantitative feeding device, wherein the two materials are alkaline clay and xylene, and the others are liquid additives, after all the additives are added.
- the neutralized and dewaxed oil is input into the later stage of the system and sampled and tested to determine whether it is necessary to increase the type and composition of the chemical materials, and then the quality adjustment is made. After the quality adjustment, the quality is adjusted.
- the oil is transferred to a 350-mesh slag separator, and the separated oil enters the temporary reservoir.
- the oil is output to the metal catalyst fixed bed processor through the temporary oil reservoir for the final refining process, and the oil output from the product discharge port of the fixed bed processor is the refined oil, and the quality thereof conforms to the national III standard diesel oil, and the obtained product is obtained.
- the National III standard diesel oil is 2.2 tons, which is used to provide the fuel for the garbage collection of the kitchen waste.
- the crude carbon black solid residue which is finally non-vaporizable and sublimated is left in the reaction vessel. It is a kind of fine particles with a high fixed carbon, but if it is not properly treated on site, it turns. When it is transferred, it will cause damage to land and air, so it is an indispensable item in the case of this specific implementation.
- the crude carbon black is discharged from the automatic slag outlet of the cracking reactor, and the crude carbon black is sent to a special ozone aging device through a conveying device to artificially age the material, and the external crystallization of the carbon black particles is more orderly, and the particles are The internal order is poor, and the particle specific volume is changed by aging, thereby increasing the oxygen function of the crude carbon black and increasing the hydrocarbon ratio.
- the coarse carbon black is aged, it is composed of the lower part of the aging device.
- the discharge port is discharged, then transported into the physical aging treatment equipment, and subjected to hot steam treatment on a fixed bed, under a condition of a vapor pressure of 2.8 mpa for 25 minutes, which effectively increases the embedding of the combustion material of the crude carbon black. Quantity, modify its characteristics that are difficult to ignite.
- the conveying equipment feeds the material into the coal pulverizer and produces high-energy low-sulfur environmentally friendly coal according to the particle size and shape required by the customer.
- the product quality is 0.2% of total sulfur, 6.58% of ash, 11% of volatile matter, and grade 1 of coke slag.
- the base heat is 5300kcal/kg.
- the sewage and plant domestic sewage generated by the multiple processes referred to in the specific implementation case are after the multiple sewage discharge pipes enter the collecting pool, and the debris floating on the water surface is removed by the rolling grating, and then The pump is pumped into the ribbon dewatering machine to remove small solid debris.
- the water discharged from the dehydrator is directly sent by the water pump to the top of the electric felt processor through the pipe, and then sprayed out at the mechanical atomizing nozzle.
- the rated working pressure of the nozzle is 0.35. Mpa, the water supply intensity is 50-80kg/min.
- the sewage When the fog falls on the hot felt, the sewage is partially converted into water vapor under the heat of the hot felt, partially converted into hot water, and the rising water vapor is converted into liquid state through the condensing device.
- the water enters the reservoir, and the hot water passes through the shallow ditch of the hot felt into the water discharge port at the bottom of the device and enters the reservoir to be mixed with the liquefied water.
- the hardness of the treated water is greatly reduced and the microorganisms in the water are artificially inactivated at a high temperature, and the purified metal ions are separated from the water body.
- the heat source of the hot felt device for treating the sewage is controlled by the heat transfer oil.
- the silicon intermediate frequency device is heated, and the intermediate frequency power supply circuit adopts six-pulse rectification mode, the incoming line voltage is 380V, the intermediate frequency induction coil generates heat of 500000kcal, and the hot felt diameter is 1.5m.
- the water treated by the hot felt When the water treated by the hot felt is treated, it enters the reservoir directly, passes through the pump to enter the strong gas, the water mixer mixes with the ozone gas, enters the front end of the advanced oxidation reactor, and enters the advanced stage through the activated carbon reaction ball.
- the water entering the reactor is first input into the buffer zone of the outer casing, and then enters the strong gas and water mixer again, and is again contacted with the supplemental ozone gas.
- the reaction time is 5 min
- the ozone concentration in the water of the reaction process is 5 g / T
- the water body after the completion of the reaction stays in the reaction kettle for 2 min, in the reaction
- the ozone air overflowing during the process is inactivated by an ozone destroyer that is sucked into the top of the reactor.
- the advanced oxidation treated sewage passes through the water outlet provided at the lower side of the reaction kettle, and the water body is input into the composite filtering device by a water pump.
- the device is composed of a plurality of sets of vertical filter tanks, and the water body enters from the top of the filter tank and is set in the water.
- the pressure is passed through dozens of filter columns.
- the filter column has a diameter of 200 mm and a length of 1 m.
- the upper part of the column is filled with a non-polar adsorbent, and the lower part is filled with a hybrid charge adsorbent.
- the water body Under the adsorption of the adsorbent, the water body has reached a clear and turbidity, no odor, no heavy metal ions, and basically removes the strong oxidant converted from ozone gas present in the water body due to the advanced reaction.
- the ozone concentration is only 0.008 mg/L.
- the water body treated by the composite filtering device is discharged from the drain port provided on the lower side of the device, and then enters the ultraviolet ray sterilizing device, and the ultraviolet radiation intensity is 2600-3000 UW/cm 2 and the wavelength is 235-258 nm, and the irradiation time is 4S, after the water body is sterilized by ultraviolet light, the whole sewage treatment process has been completed. Not only the water quality meets the industrial water reuse standard, but also is used as the production water for the waste disposal of the kitchen waste, and the treatment of the sewage is fast and reliable, and the water consumption per hour is about 5 tons.
- the dewatered sludge generated in the sewage generated from the production and domestic sewage in the sewage treatment process into the sludge storage tank for 24 hours, using the naturally occurring or dead microorganisms naturally produced in the sludge as the pore former.
- the hole-forming module when the sludge in the sludge storage device is taken out and put into the ozone processor, the microorganism is artificially forcibly inactivated by using the sludge in the processor from top to bottom.
- Reverse ozone contact with ozone the time is 2min, the ozone concentration of the ozone processor is 12g/L, and the ozone gas flow rate is 7L/min.
- the ozone exhaust gas is collected and processed by special equipment.
- the sludge that has been forcedly inactivated is sent to the primary curing device by the automatic conveying device, which is composed of horizontal overlapping layers of spiral ribbons.
- the automatic conveying device which is composed of horizontal overlapping layers of spiral ribbons.
- 10% calcium oxide sludge is uniformly mixed for a mixing time of 25 minutes, and the mixed sludge is solidified or semi-cured to form granules.
- the granulated sludge is discharged from the bottom of the mixer, and is continuously conveyed to the pneumatic propulsion equipment by the spiral belt conveying device, and the conveying system quickly sends the granulated sludge into the reaction kettle, and the reaction at this time
- the temperature in the autoclave was 100 ° C, which had jumped over the survival condition zone below 75 ° C of the methanogen.
- the pneumatic propulsion equipment automatically leaves the reaction tank inlet under the guidance of the guide rail. At this time, the feed port of the reaction kettle is sealed and closed at the same time, and the heating speed of the reaction kettle is closed.
- the one-way air valve at the end of the reaction kettle is automatically opened, and the gas is passed through the safety water sealing device, and then enters the exhaust gas environmental protection treatment system, when the temperature in the reaction kettle reaches At 160 ° C, the structure of the sludge was destroyed, and the crystal water of the sludge was quickly released, and the water gas was taken out of the tail end of the kettle and discharged into the water sealer through a one-way gas valve.
- the temperature of the reactor reaches 220 °C, the dead microorganisms are carbonized.
- the cell matrix sol of the microorganism overflows to the outside of the mud and the cokes shrink, and the sludge particles basically form a multi-phenotype. Microcavities and channels.
- the temperature in the reactor was kept at a constant temperature and kept at a constant temperature for one hour, but in order to prevent the sludge from entering pyrolysis, the final temperature setting in the autoclave could not be higher than 260 °C.
- the moisture in the sludge particles in the kettle has basically escaped, and the porosity of the sludge is consolidated.
- the anaerobic heat-treated sludge After the anaerobic heat-treated sludge is cooled, it is discharged from the automatic discharge port of the reaction vessel, and is sent to the processing warehouse by the automatic conveying tool to perform natural aging, and the aging time is 48 hours. Thereafter, the sludge is sent to the acidification.
- the reactor is statically immersed in a 20% strength liquid sulfuric acid for 14 hours to remove the coke knots of the dead organisms, and at the same time remove the metal impurity ions in the sludge, and act on the hydrogen ions instead of the solidification of the sludge mass. Calcium ion.
- the sludge granules substantially completely expose the pore structure skeleton of the granules in this process.
- the acidified sludge particles are discharged from the discharge port of the reactor and then enter the water bleaching.
- the water temperature condition of the water bleaching is 80 ° C, and the pH value is adjusted at this time, and the particles which are floated by the water are fed by the conveyor.
- the hot steam activated room was subjected to a preliminary physical activation stage with a steam flow rate of 250 ml/min and an activation time of 2 hours.
- the sludge particles in the physical activation process are then subjected to high-temperature pipeline type electric heating furnace for high-temperature activation, and are carried out under the condition of isolated air.
- the overflowed hot gas is treated by the tail gas environmental protection treatment system, and the heating rate of the activation furnace is 20 ° C / min, and the activation is performed.
- the temperature is 720 ° C, the activation time is 2 hours.
- the sludge particles are cooled, and after being output, they are refined to become the core material of the hybrid charge adsorbent, and the pores and pore structures are amorphous structures.
- the pore size and pore volume and pore form, pore size and length are naturally constant according to the type and quantity of various microorganisms attached to the sludge, and the pores per gram of finished product are between 1 and 150 million.
- the diameter of the hole is about 0.8-1.2um
- the length of the hole is about 2-5um
- the width is about 0.3-0.4um.
- the acidic aluminum sol and the silica sol are used to prepare a certain dilution, wherein the aluminum sol is 60% and the silica sol is 40%.
- the nucleus material prepared above is mixed in the two mixed sols, and the weight ratio thereof is 78%: 20 %, then take out the mixture and put it into a high-temperature tubular resistance furnace, and keep it at 650 °C for one hour. After the process is finished, the temperature is removed and refined, and the core is made into a non-polar adsorbent.
- the outer layer is an aluminum-silicon skeleton.
- Multi-functional hybrid charged adsorbent material synthesized by medium network polar adsorbent the adsorbent has excellent quality, good mechanical strength, long service life, wide pore size distribution, and organic matter in various inorganic and organic gases and aqueous solutions.
- heavy metal ions and the like have a large adsorption capacity and a fast adsorption rate, and the finished product made of the sludge is applied to the filter column of the composite filtration device of the sewage treatment system in the case of the specific embodiment, and Applied in odor treated odor destroyers.
- the exhaust gas conveying system composed of a plurality of pipes, such as dry dust air generated in the middle, enters the water-sealed flue gas buffer chamber with the action of the two-stage air deflector.
- the flue gas is input from the underwater 150mm, and then jumps from the bottom to the top in the water body. This action causes multiple smokes of different pressures, different wind speeds and air flows to form the same condition after jumping out of the water surface.
- the flue gas is filled with solid particles of carbon particles and other substances, enters the treatment channel of the negative ion and the water curtain, and rushes to the ceramic high-speed water curtain area which can naturally release the negative ion charge.
- the concave, obtuse angle deflector installed on the upper, left and right dislocations, the direction of the instantaneous airflow path is changed. At this time, the moving direction of the dense solid dust particles in the flue gas does not flow in the negative ion region.
- the water vapor washed by the weak alkaline water enters the gas through the exhaust port provided in the upper part of the twin towers.
- Water transport pipelines, and tiny solid materials enter the gas and water transport pipelines along with the water bodies at the drains of the lower towers.
- the hot water vapor entering the gas and water transfer pipeline enters the flue gas discharge system in the upper layer of the pipeline, and the water body and the micro-solid matter entering the gas and water transport pipeline are also in the lower layer of the pipeline, and also enter the flue gas discharge system.
- the discharge system is divided into upper, middle and lower parts.
- the liquefiable gas continues to rise, and the upper gas discharge port of the system is discharged. At this time, the temperature of the exhaust gas discharged is not higher than 38 ° C, which is a room-free gas discharge, and the emitted gas has no odor and carbon particles, and no black smoke.
- the harmful substance, and the air is introduced into the corrugated anion zone provided at the front end of the air discharge port and having a negative ion release amount of 15000/cm 3 under the action of a 1500 m 3 /h air inlet provided in the subsequent stage of the photocatalytic zone, and then discharged.
- the air that is expelled is a clean, odorless air.
- the central intelligent control operating system of this specific implementation case is a well-known technology.
- the specific implementation is to set up a central intelligent control room, a central control operation platform, and a large display screen as a human-machine interface on the production line of each field device.
- the control cabinet is arranged separately from the gas discharge port.
- the central control room operation platform is used as a full-line monitoring center, and the whole line working condition is observed from the main screen, and the computer configuration screen is synchronized with the real-time operation to monitor the display fluid dynamics and the motor running state, and also according to the changes in the production process. Make timely data adjustments, and also make on-site control in the central control system.
- one of the links in the system can be started separately, and the unmanned state can be realized in the main production area in the whole kitchen waste recycling process.
Abstract
Description
Claims (124)
- 一种餐厨垃圾全方位综合处理系统,其特征是:所述的系统包括餐厨垃圾破袋装置、餐厨垃圾联合筛选装置、湿式高级氧化除臭灭活清洗降盐装置、立式脱水装置、物料破碎机和自动控制装置,餐厨垃圾投入餐厨垃圾破袋装置进行破袋处理,然后输入至餐厨垃圾联合筛选装置进行联合筛选,经筛选后的油水固混合物输入至湿式高级氧化除臭灭活清洗降盐装置进行灭活处理,通过湿式高级氧化已灭活除臭除盐初级脱水的餐厨垃圾由螺旋杆输送管道送入脱水装置,经脱水装置脱水后的物料输入物料破碎机进行粉碎,自动控制装置控制其他装置工作。
- 根据权利要求1所述的餐厨垃圾全方位综合处理系统,其特征是:所述的割破装置包括卧式筒状外壳(D11),外壳(D11)一端为出料口(D18),外壳(D11)于出料口(D18)的一端内壁设有固定一个以上的刀具(D12),外壳(D11)另一端内设有能够沿着外壳(D11)内腔滑动的活塞(D13),并连接有推动活塞(D13)运动的动力工具(D12),活塞(D13)上对应于每个刀具(D12)位置处开设有一个刀槽(D14),外壳(D11)顶部中间位置开有进料口(D21)。
- 根据权利要求2所述的餐厨垃圾全方位综合处理系统,其特征是:所述的活塞(D13)底部安装有滑轮(D15),外壳(D11)内壁底部对应于滑轮(D15)位置处固定设有凹形滑轨(D17),滑轮(D15)能够在凹形滑轨(D17)上来回滑动。
- 根据权利要求2所述的餐厨垃圾全方位综合处理系统,其特征是:所述的进料口(D21)位置处安装有收集箱(D19),收集箱(D19)上部呈漏斗形,下部通过下料管道(D20)与外壳(D11)上的进料口(D21)连通,下料管道(D20)上设有气动滑板闸阀(D27)。
- 根据权利要求2或3或4所述的餐厨垃圾全方位综合处理系统,其特征是:所述的外壳(D11)上的出料口(D18)位置处安装有滚动拍板(D22),电机(D28)带动滚动拍板(D22)转动。
- 根据权利要求5所述的餐厨垃圾全方位综合处理系统,其特征是:所述的滚动拍板(D22)呈方形或多边形并设有内腔。
- 根据权利要求6所述的餐厨垃圾全方位综合处理系统,其特征是:所述的滚动拍板(D22)每个面上设有一个以上的压缩空气射出槽(D23),滚动拍板(D22)内设有压缩空气导气管(D24和气体喷射嘴(D23),气体喷射嘴(D26)连接在压缩空气导气管(D24)上,气体喷射嘴(D26)的射流方向与出料口的出料方向相同。
- 根据权利要求7所述的餐厨垃圾全方位综合处理系统,其特征是:所述的压缩空气射出槽(D23)平行设置。
- 根据权利要求2或3或4所述的餐厨垃圾全方位综合处理系统,其特征是:所述的刀具(D16)的刀锋与外壳出料口横截面呈90度角或与外壳内壁呈30度角。
- 根据权利要求1所述的餐厨垃圾全方位综合处理系统,其特征是:所述的餐厨垃圾联合筛选系统包括壳体(E11),壳体(E11)内设有分隔板(E25),通过分隔板(E25)将壳体(E11)内部分为气浮区(E10)和非气浮区(E32),分隔板(E25)上设有物料漏出口(E26),气浮区(E10)处设有进料口,气浮区(E10)下部设有重物料卸出口(E22),重物料卸出口(E22)处设有阀门(E23),重物料卸出口(E22)四周设有一个以上的空气喷嘴(E24),气浮区(E10)上部设有滚耙(E30),非气浮区(E32)内设有物料输出器(E33),物料输出器(E33)一端设置在壳体(E11)内,另一端设置在壳体(E11)外侧,物料输出器(E33)内设有搅龙(E37),物料输出器(E33)上安装有电机(E36)和变速器(E34),电机(E33)配合变速器带动搅龙(E37)转动。
- 根据权利要求10所述的餐厨垃圾全方位综合处理系统,其特征是:所述的物料漏出口(E26)处设有百叶导槽(E27),百叶导槽(E27)连接在气动推进拉杆(E28)上,气动装置(E38)驱动推进拉杆(E28)运动,并由推进拉杆(E28)控制百叶导槽(E27)的开启与闭合。
- 根据权利要求10所述的餐厨垃圾全方位综合处理系统,其特征是:所述的滚耙(E30)设有两个,两个滚耙(E30)一上一下设置,下面的滚耙的1/2设置在气浮区(E10)的液面内,上面的滚耙设置在气浮区(E10)的液面上方,两个滚耙(E30)相互啮合。
- 根据权利要求12所述的餐厨垃圾全方位综合处理系统,其特征是:所述的壳体(E11)上安装有滚耙电机(E39),滚耙电机(E39)同时带动两个滚耙(E30)转动。
- 根据权利要求10至13中任意一项所述的餐厨垃圾全方位综合处理系统,其特征是:所述的物料输出器(E33)处安装有变速器(E34),电机(E36)通过变速器(E34)驱动搅龙(E37)转动。
- 根据权利要求10至13中任意一项所述的餐厨垃圾全方位综合处理系统,其特征是:所述的气浮区(E10)处安装有用于控制液面高度的液面高度自动控制装置(E29)。
- 根据权利要求10至13中任意一项所述的餐厨垃圾全方位综合处理系统,其特征是:所述的壳体(E11)上设有用于向壳体(E11)内输送餐厨垃圾的管道,该管道连接在进水管道(E20)上。
- 根据权利要求10至13中任意一项所述的餐厨垃圾全方位综合处理系统,其特征是:所述的气浮区(E10)的循环水进水口连接水力加压泵(E21),水源由循环储水箱提供,非气浮区(E32)的中下部设有出水口,并通过水泵将水体输入循环储水箱内,用于气浮区(E10)与非气浮区(E32)水体的循环和加强气浮区(E10)内的水体强力翻滚。
- 根据权利要求1所述的餐厨垃圾全方位综合处理系统,其特征是:所述的餐厨垃圾氧化、除臭、灭活、清洗降盐装置包括一个以上的反应器(F34)和用于臭氧——水——物料混合的气、水、物混合器(F42),混合器(F42)上连接有防水单向阀,防水单向阀的一端连接输气管后,再连接臭氧发生设备(F44),混合器(F42)上还连接有高粘度凸轮转子泵(F49)出口,混合器(F42)的出口伸入一个反应器(F34)内,高粘度凸轮转子泵(F49)的入口与另一个反应器(F34)连接,反应器(F34)内设有一个以上的颗粒活性碳反应球(F41),颗粒活性碳反应球(F41)内设有颗粒活性碳,反应器(F34)底部设有物料出口。
- 根据权利要求18所述的餐厨垃圾全方位综合处理系统,其特征是:所述的颗粒活性碳的总体积占颗粒活性碳反应球(F41)球体内腔体积的15%——98%。
- 根据权利要求18所述的餐厨垃圾全方位综合处理系统,其特征是:所述的反应器(F34)顶部设有自动排气阀(F38),自动排气阀(F38)上连接有臭氧毁灭器(F39)。
- 根据权利要求18或19或20所述的餐厨垃圾全方位综合处理系统,其特征是:所述的反应器(F34)底部设有半圆封头(F35),物料出口设置在半圆封头(F35)上。
- 根据权利要求18或19或20所述的餐厨垃圾全方位综合处理系统,其特征是:所述的反应器(F34)中最前端的反应器(F34)上设有斜面螺带输送器(F36),而后端的反应器(F34)上设有水位高度调节管道。
- 根据权利要求18或19或20所述的餐厨垃圾全方位综合处理系统,其特征是:所述的物料出口处连接有固、液分离器。
- 根据权利要求23所述的餐厨垃圾全方位综合处理系统,其特征是:所述的固、液分离器包括外壳(F45)和倾斜网状桶体(F52),倾斜网状桶体(F52)设置在外壳(F45)内,倾斜网状桶体(F52)由电机配合变速器带动转动,倾斜网状桶体(F52)前端设有一排以上的网孔,倾斜网状桶体(F52)内设有连接于网状桶体内壁的螺旋状的螺带,外壳(F45)底部设有接水器(F47)。
- 根据权利要求24所述的餐厨垃圾全方位综合处理系统,其特征是:所述的螺旋状的螺带占倾斜网状桶体(F52)的全长。
- 根据权利要求24所述的餐厨垃圾全方位综合处理系统,其特征是:所述的外壳(F45)上装有视窗(F46)。
- 根据权利要求18或19或20所述的餐厨垃圾全方位综合处理系统,其特征是:所述的反应器(F34)侧面装有人孔。
- 根据权利要求1所述的餐厨垃圾全方位综合处理系统,其特征是:所述的立式脱水装置包括外壳(G49)、立式内漏塔(G50)和螺带推进杆(G51),立式内漏塔(G50)设置在外壳(G49)内部,螺带推进杆(G51)设置在立式内漏塔(G50)内部,立式内漏塔(G50)侧面开有一个以上的漏水孔(G58),立式内漏塔(G50)底部设有进料口(G62),立式内漏塔(G50)顶部设有出料口(G60),外壳(G49)底部安装有驱动螺带推进杆(G51)转动的动力源,外壳(G49)内部对应于立式内漏塔(G50)底部四周设有接水槽(G55),接水槽(G55)上连接有出水口(G63)。
- 根据权利要求28所述的餐厨垃圾全方位综合处理系统,其特征是:所述的外壳(G49)内部,立式内漏塔(G50)四周设有一条以上的水管(G65),每条水管(G65)上连接有一个以上的高压水反冲喷嘴(G53)。
- 根据权利要求28或29所述的餐厨垃圾全方位综合处理系统,其特征是:所述的立式内漏塔(G50)顶部装有安装螺带推进杆(G51)的轴心固定板(G61)。
- 根据权利要求30所述的餐厨垃圾全方位综合处理系统,其特征是:所述的螺带推进杆(G51)上的螺带尾端装有调节出料速度的封口板。
- 根据权利要求28或29所述的餐厨垃圾全方位综合处理系统,其特征是:所述的螺带推进杆(G51)上的螺带的间距为由下部渐步往塔顶收窄。
- 根据权利要求32所述的餐厨垃圾全方位综合处理系统,其特征是:所述的螺带推进杆(G51)上的螺带下端的间距为25CM,终端的间距为10CM。
- 根据权利要求28或29所述的餐厨垃圾全方位综合处理系统,其特征是:所述的动力源包括电机(G54)、变速器(G64)和将水平轴向转动转为竖直轴向转动的转向变换装置(G66),电机(G54)带动变速器(G64)转动,变速器(G64)带动转向变换装置(G66)转动,转向变换装置(G66)带动螺带推进杆(G51)转动。
- 根据权利要求28或29所述的餐厨垃圾全方位综合处理系统,其特征是:所述的外壳(G49)内设有不锈钢支承套(G56)。
- 根据权利要求28或29所述的餐厨垃圾全方位综合处理系统,其特征是:所述的立式内漏塔(G49)外侧四周设有一条以上的不锈钢立板(G56),不锈钢立板(G56)的周围装有一根以上的加固圈套,每根加固圆圈上装有斜面防反冲导流檐。
- 根据权利要求28或29所述的餐厨垃圾全方位综合处理系统,其特征是:所述的立式内漏塔(G49)由一个以上的塔体组成,每个塔体的上下圆周位置装有加强法兰,且相邻塔体的连接均是塔体上下的法兰之间对接,并采用螺栓固定,每个塔体的连接法兰位置上的上层法兰装有斜面防反冲导流檐。
- 根据权利要求1所述的餐厨垃圾全方位综合处理系统,其特征是:所述的生化发酵装置包括厌氧发酵池(I65)和主发酵装置(I70),所述的主发酵装置(I70)包括两个副发酵器(I71)和一个以上的主发酵器,两个副发酵器(I71)设置在主发酵器上方,副发酵器(I71)与主发酵器连接处设有进料口(I84),主发酵装置外设有用于将物料输入至副发酵器(I71)内的物料提升机(I64),副发酵器(I71)内设有搅拌设备(I73),主发酵器内设有双层螺带搅拌器(I78),厌氧发酵池(I65)与主发酵器连接,厌氧发酵池(I65)通过自动卸料系统(I67)将物料投入主发酵器内。
- 根据权利要求38所述的餐厨垃圾全方位综合处理系统,其特征是:所述的双层螺带搅拌器(I78)包括轴体、内层螺带和外侧螺带,内层螺带设置在外层螺带内部,内层螺带和外层螺带均呈螺旋形带状,且分别固定安装在轴体上,内层螺带和外层螺带的螺旋方向相反,双层螺带搅拌器(I78)的轴体周边加装铧叶片(I79)。
- 根据权利要求38或39所述的餐厨垃圾全方位综合处理系统,其特征是:所述的搅拌设备(I73)中间为一个主轴,中轴上固定安装有一个以上的搅拌叶片。
- 根据权利要求38或39所述的餐厨垃圾全方位综合处理系统,其特征是:所述的厌氧发酵池(I65)内上方设有可自动移动的物料搅拌器(I68)。
- 根据权利要求1所述的餐厨垃圾全方位综合处理系统,其特征是:所述的自动卸料多级干燥装置包括预干燥设备(J93)和主干燥设备,预干燥设备(J93)安装于主干燥设上方,预干燥设备(J93)外壳呈两侧,两侧之间形成预干燥设备的外壳夹层内腔(J97),预干燥设备(J93)内设有物料自动翻板(J94),主干燥设备中间为能够360度逆顺方向旋转的卧式圆筒形体(J102),主干燥设备前、后两端分别为固定封头(J101),卧式圆筒形体(J102)内设有一个以上的与卧式圆筒形体(J102)固定安装在一起的副筒体,卧式圆筒形体(J102)和各个副筒体内部均设有导料螺带,主干燥设备上设有气体或液态燃料燃烧室(J99)和燃烧器(J100),燃烧器(J100)产生的热量通入主干燥设备内部,主干燥设备的尾气通过热空气排出口(J107)输入至外壳夹层内腔(J97)内,预干燥设备(J93)的物料输出口对应于主干燥设备最内侧副筒体设置。
- 根据权利要求42所述的餐厨垃圾全方位综合处理系统,其特征是:所述的预干燥设备(J93)底部设有螺带搅龙自动出料器(J95),螺带搅龙自动出料器(J95)呈筒状,内部设有螺带搅龙。
- 根据权利要求42所述的餐厨垃圾全方位综合处理系统,其特征是:所述的预干燥设备(J93)顶部设有引风设备(J98)。
- 根据权利要求42或43或44所述的餐厨垃圾全方位综合处理系统,其特征是:所述的各个副筒体套装在一起,外侧副筒体的物料入口长于内层副筒体的物料出口。
- 根据权利要求42或43或44所述的餐厨垃圾全方位综合处理系统,其特征是:所述的各个副筒体的外侧壁上固定安装有气流扰动翅(J103)。
- 根据权利要求42或43或44所述的餐厨垃圾全方位综合处理系统,其特征是:所述的卧式圆筒形体(J102)和各个副筒体内部的导料螺带方向相反。
- 根据权利要求1所述的餐厨垃圾全方位综合处理系统,其特征是:所述的物料精选装置包括底座(K108)、金属滚动筛网筒(K110)、物料承载器(K113)、自动输送工具(K114)、链板输送机(K115)和分流闸板(K116),金属滚动筛网筒(K110)安装在底座(K108)上,物料承载器(K113)设置在金属滚动筛网筒(K110)下方,自动输送工具(K114)设置在物料承载器(K113)下方,金属滚动筛网筒(K110)前端设有筛网孔,后端设有螺带,链板输送机(K115)设置在金属滚动筛网筒(K110)出料口下方,分流闸板(K116)设置在链板输送机(K115)尾端。
- 根据权利要求48所述的餐厨垃圾全方位综合处理系统,其特征是:所述的筛网孔直径为4mm——6mm,孔与孔这间间隔为2mm。
- 根据权利要求48所述的餐厨垃圾全方位综合处理系统,其特征是:所述的金属滚动筛网筒(K110)倾斜设置,倾斜角度为1度——20度。
- 根据权利要求48或49或50所述的餐厨垃圾全方位综合处理系统,其特征是:所述的分流闸板(K116)处设有用于调节分流闸板(K116)与链板输送机(K115)之间高度的调节装置,分流闸的一侧装有气动拨料器。
- 根据权利要求48或49或50所述的餐厨垃圾全方位综合处理系统,其特征是:所述的金属滚动筛网筒(K110)外侧安装有保护罩(K109)。
- 根据权利要求1所述的餐厨垃圾全方位综合处理系统,其特征是:所述的餐厨垃圾联合筛选装置设有塑料固体输出端,餐厨垃圾联合筛选装置的塑料固体输出端连接有废塑料逆转工程装置。
- 根据权利要求53所述的餐厨垃圾全方位综合处理系统,其特征是:所述的废塑料逆转工程装置主要摆阔主体处理装置,主体处理装置由输送带(M122)将物料送入气压式自动进料机(M123),通过气压式自动进料机(M123)将物料送入裂解催化卧式反应釜(M124)内,反应釜(M124)能够作360度顺、逆旋转,反应釜(M124)内带有自动随机刮壁装置(M125),反应釜(M124)上连接有后级真空系统(M130),反应釜(M124)通过管道与油腊分离器(M129)连接,管道上设有单向阀(M128),油腊分离器(M129)通过管道连接有第一级重油分离器(M131),第一级重油分离器(M131)通过管道连接有第一级冷凝器(M132),第一级冷凝器(M132)底部连接有油料承载容器(M133),第一级冷凝器(M132)后端连接有负压设备(M134),负压设备(M134)后端连接有立式水封式气体安全输送器(M135),立式水封式气体安全输送器(M135)后端连接有二级燃气压缩机(M136),二级燃气压缩机(M136)与燃气贮存库(M137)连接。
- 根据权利要求54所述的餐厨垃圾全方位综合处理系统,其特征是:所述的反应釜(M124)底部设有裂解炉(M126),裂解炉(M126)的出气口管道连接尾气环保装备系统(M127)。
- 根据权利要求54所述的餐厨垃圾全方位综合处理系统,其特征是:所述的油料承载容器(M133)连接有除碳精漂器(M139)和脱腊除胶器(M140)。
- 根据权利要求53所述的餐厨垃圾全方位综合处理系统,其特征是:所述的系统还包括粗炭黑处理装置,粗炭黑处理装置连接在废塑料逆转工程装置的余渣输出口处。
- 根据权利要求57所述的餐厨垃圾全方位综合处理系统,其特征是:所述的粗炭黑处理装置包括粗炭黑人工陈化处理器(N144),粗炭黑人工陈化处理器(N144)与物理陈化床(N145)连接,物理陈化床(N145)通过自动输送工具与物料配伍设备(N146)连接,物料配伍设备(N146)上连接有液、固自动定量加料加料设备(N147),物料配伍设备(N146)后端设有多层推拉式螺杆(N148),多层推拉式螺杆(N148)后端与低硫高能环保清洁燃煤成形机(N149)连接。
- 根据权利要求1所述的餐厨垃圾全方位综合处理系统,其特征是:所述的系统还包括免蒸馏法生物柴油生产装置,各个装置通过管道将油、水、固混合体先经过油水分离,再送入免蒸馏法生物柴油生产装置。
- 根据权利要求59所述的餐厨垃圾全方位综合处理系统,其特征是:所述的免蒸馏法生物柴油生产系统包括卧式螺带固液分离设备(O151)、油水分离塔(O152)、储油容器(O149)、油脂胶质脱除设备(O158)、生物油常温脂交换设备(O161)、分液设备(O172)和过滤设备(O173),卧式螺带固液分离设备(O151)的出口通过管道连接至油水分离塔(O152)中下端,油水分离塔(O152)内设有加热管道(O153),加热管道(O153)从油水分离塔(O152)下部伸入至油水分离塔(O152)内部,再从油水分离塔(O152)中上部输出至油水分离塔(O152)外侧,油水分离塔(O152)顶部设有刮油器(O155),油水分离塔(O152)通过出油管道(O156)与储油容器(O149)连接,出油管道(O156)入口对应于刮油器(O155)设置,储油容器(O149)通过管道与油脂胶质脱除设备(O158)连通,油脂胶质脱除设备(O158)内部设有固定设置有孔洞撞击板(O159),撞击板(O159)的两侧对应位置分别安装有旋浆式水力推进机(O160),旋浆式水力推进机(O160)的螺旋桨扇叶设置在油脂胶质脱除设备(O158)内,电机设置在油脂胶质脱除设备(O158)外侧,电机驱动螺旋桨扇叶转动,油脂胶质脱除设备(O158)下部设有油脂出口,油脂出口通过管道连通至生物油常温脂交换设备(O161)内,生物油常温脂交换设备(O161)内设有一个以上的超声波发生器(O162),生物油常温脂交换设备(O161)顶部开有投料口(O169),生物油常温脂交换设备(O161)底部通过管道连通至分液设备(O172),分液设备(O172)底部通过输油管道连接至过滤设备(O173),过滤设备(O173)输出生物柴油。
- 根据权利要求60所述的餐厨垃圾全方位综合处理系统,其特征是:所述的卧式螺带固液分离设备(O151)包括有一个卧式圆筒形外壳,外壳内设有滤网,滤网内部固定设有输送螺带,螺带驱动电机配合变速器带动滤网及螺带转动,卧式螺带固液分离设备(O151)底部设有油、水混合体输出管道。
- 根据权利要求60所述的餐厨垃圾全方位综合处理系统,其特征是:所述的油水分离塔(O152)的顶部装有红外线水体液面定位仪(O154)。
- 根据权利要求60所述的餐厨垃圾全方位综合处理系统,其特征是:所述的超声波发生器(O162)外围分别装有套管(O163),套管(O163)四周开有内螺纹射流孔(O164),套管(O163)上方固定设有卡定器(O165),通过卡定器(O165)将超声波发生器(O162)安装在生物油常温脂交换设备(O161)内部。
- 根据权利要求60所述的餐厨垃圾全方位综合处理系统,其特征是:所述的生物油常温脂交换设备(O161)内装有液体导流管(O166),液体导流管(O166)一端连接在生物油常温脂交换设备(O161)上部,另一端连接在生物油常温脂交换设备(O161)底部,液体导流管(O166)上连接有泵具(O167)。
- 根据权利要求60所述的餐厨垃圾全方位综合处理系统,其特征是:所述的生物油常温脂交换设备(O161)底部设有鼓气管(O171),鼓气管(O171)的一端连接压缩空气机。
- 根据权利要求60所述的餐厨垃圾全方位综合处理系统,其特征是:所述的系统还包括油脂胶质脱除设备,由专用油泵将生物油脂从储油容器输入油脂胶质脱除设备之后在进入脂交换设备。
- 根据权利要求66所述的餐厨垃圾全方位综合处理系统,其特征是:所述的系统还包括制造乳化生物柴油装置,经脂交换工艺出来的生物油脂输出至制造乳化生物柴油装置。
- 根据权利要求67所述的餐厨垃圾全方位综合处理系统,其特征是:所述的乳化生物柴油的制作装置包括壳体(P174),壳体(P174)内装有垂直搅拌器(P175),动力源带动垂直搅拌器(P175)转动,垂直搅拌器(P175)的中轴上装有一个以上的浆式平直搅拌浆(P178)或桨式折叶桨,垂直搅拌器(P175)的中轴下部安装有涡轮或圆盘弯叶浆(P179),壳体(P174)内的上部装有富氧水雾化喷嘴(P185),壳体(P174)的顶部设置有一个以上的进料口(P181),每个进料口(P181)均通过管道连接有一个定量加料设备(P182),壳体(P174)中上部一侧设有油品进料口(P192),并由管道连接于油品输送泵,壳体(P174)上部装有进水管道(P186)并连接高压泵(P187),进水管道(P186)的水源由富氧水储备箱(P191)提供,而富氧水由臭氧发生器(P188)输出O3气体,并通过气体输送管道进入强力气水混合器(P189)与通过管道(P190)进入水体混合后进入富氧水储备箱(P191),壳体(P174)下部设置有成品出料口(P184)。
- 根据权利要求68所述的餐厨垃圾全方位综合处理系统,其特征是:所述的壳体(P174)上部为圆筒形,下部呈半圆形。
- 根据权利要求69所述的餐厨垃圾全方位综合处理系统,其特征是:所述的壳体(P174)的圆筒形内壁四周安装一个以上的液体导流叶板(P183)。
- 根据权利要求69所述的餐厨垃圾全方位综合处理系统,其特征是:所述的壳体(P174)底部安装有支撑垂直搅拌器(P175)的转轴用的支承架(P180)。
- 根据权利要求68至71所述的餐厨垃圾全方位综合处理系统,其特征是:所述的动力源包括电机(P176)和变速设备(P177),变速设备(P177)固定安装在壳体(P174)顶部,电机(P176)设置在变速设备(P177)上方,电机(P176)通过变速设备(P177)驱动垂直搅拌器(P175)转动。
- 根据权利要求1所述的餐厨垃圾全方位综合处理系统,其特征是:所述的系统中还包括快速污水处理回用装置,各个装置产生的污水通过管道连接至快速污水处理回用装置。
- 根据权利要求73所述的餐厨垃圾全方位综合处理系统,其特征是:所述的快速污水处理回用装置包括污水过滤池(Q185),污水过滤池(Q185)内设置有杂物拦栅(Q186),杂物拦栅(Q186)内设有防塞反冲器(Q187),污水过滤池(Q185)通过进水管道与灼热毡污水处理设备(Q188)连接,灼热毡污水处理设备(Q188)包括内腔(Q189)和机壳(Q190),机壳(Q190)顶部设有多个与进水管相通的雾化喷射头(Q192),雾化喷射头(Q192)下方设有一个灼热毡(Q193),灼热毡(Q193)内设有导热油管道(Q195),灼热毡(Q193)下方的底部设有微固物沉淀区(Q196),微固物沉淀区(Q196)底部设有排污口(Q197),排污口(Q19)7上方设有防污反冲挡板(Q198),灼热毡(Q193)下方装有用于支撑灼热毡(Q193)的耐高温垫层(Q199),机壳(Q190)的顶部开有自动吸排气阀(Q200),机壳(Q190)位于灼热毡(Q193)的上方开有热蒸汽收集口(Q201),热蒸汽收集口(Q201)通过管道与热交换器(Q202)相连,热交换器(Q202)后端连接有集水池(Q203),集水池(Q203)通过管段与高级氧化系统(Q204)连接,高级氧化系统(Q204)具有内外两层空腔,内腔为气水反应腔(Q205),外腔为气水循环反应缓冲腔(Q206),内腔进水口引入管的端部装有活性碳反应球(Q209),活性碳反应球(Q209)内装有颗粒活性碳,内腔底部设有排污口(Q212),排污口(Q212)与外壳的排污口(Q213)相连,内腔的排污口(Q212)上还安装防反冲档板(Q214),高级氧化反应器通过循环管道连接有气水混合器(Q215),气水混合器(Q215)为三通接法,两端接通循环水,而中间的一个端口连接防水单向阀(Q216),防水单向阀Q216的另一接口连通臭氧发生器的输气管道,高级氧化系统(Q204)连接有中转水池(Q218),与中转水池(Q218)连接有活性炭过滤固定床(Q219),活性炭过滤固定床(Q219)上连接有复合过滤设备(Q220),复合过滤设备(Q220)包括一个以上的过滤罐(Q221), 过滤罐(Q221) 内分别设有一支以上的立式过滤柱(Q222),每支过滤柱(Q222)长度的一半位置处开有出水孔,过滤柱(Q222)的底部装有80——140目的滤网,过滤罐(Q221)的顶部有进水口(Q223)和加压管(Q224),过滤罐(Q221) 罐体内分为二层,每层的罐内分别装有过滤柱托板(Q226),过滤柱托板(Q226)上开有与过滤柱(Q222)直径相配的孔口,过滤柱(Q222)插装在过滤柱托板(Q226)内,上层罐体的上部一侧安装进水导流管道(Q228),进水导流管道(Q228)通向下层罐体的上部,上层罐体的下部一侧安装出水导流管道(Q229),出水导流管道(Q229)通向下层罐体的下部,罐体的上、下层一侧分别安装有排气口(Q230),过滤罐(Q221)的出水口设于复合过滤设备(Q220)底部封头的一侧(Q233),底部封头的中心位置设有沉淀物排出口(Q234)。
- 根据权利要求74所述的餐厨垃圾全方位综合处理系统,其特征是:所述的灼热毡(Q193)表面设有多道流水浅沟(Q194)。
- 根据权利要求74所述的餐厨垃圾全方位综合处理系统,其特征是:所述的内腔顶部安装有自动排气阀(Q207)和用于监控液面高度的液面控制在线监控器(Q208)。
- 根据权利要求74所述的餐厨垃圾全方位综合处理系统,其特征是:所述的活性碳反应球(Q209)上部不透水,下部为网状出水口(Q210)。
- 根据权利要求74所述的餐厨垃圾全方位综合处理系统,其特征是:所述的活性碳反应球(Q209)内的颗粒活性碳体积占反应球内腔体积的15%——95%。
- 根据权利要求1所述的餐厨垃圾全方位综合处理系统,其特征是:所述的系统还包括对剩余固体污泥处理的杂化荷电吸附剂生产装置,各个工段产生的污泥都输入至杂化荷电吸附剂生产装置。
- 根据权利要求1所述的餐厨垃圾全方位综合处理系统,其特征是:所述的系统还包括对各个工序中所产生的烟气、热烟气、粉尘等集中处理的尾气环保处理装置。
- 根据权利要求80所述的餐厨垃圾全方位综合处理系统,其特征是:所述的包括尾气缓冲装置、水固分离器(S257)、双塔式旋转喷淋系统(S259)和烟气排放设备(S264),所述的空气缓冲器(S247)和初级烟气处理管道(S253),尾气通入空气缓冲器(S247)内,通过空气缓冲器(S247)输入到初级烟气处理管道(S253)内,经初级烟气处理管道(S253)排入至水固分离器(S257)内,水固分离器(S257)出口通入双塔式旋转喷淋系统(S259)内,经双塔式旋转喷淋系统(S259)处理后输入至烟气排放设备(S264)内,再经烟气排放设备(S264)处理后排出。
- 根据权利要求81所述的餐厨垃圾全方位综合处理系统,其特征是:所述的空气缓冲器(S247)包括圆筒形外壳,外壳内上方设有一个以上的水帘喷射口(S272),外壳底部装有排污口(S249)。
- 根据权利要求81所述的餐厨垃圾全方位综合处理系统,其特征是:所述的尾气缓冲装置(S253)外壳周边开有一个以上的尾气进气口。
- 根据权利要求82所述的餐厨垃圾全方位综合处理系统,其特征是:所述的尾气缓冲装置还包括有储水箱,排污口(S249)通过管段连接至储水箱内。
- 根据权利要求84所述的餐厨垃圾全方位综合处理系统,其特征是:所述的循环水管段通过水阀(S250)连接至储水箱上部,储水箱中、下部通过泵具和管段连接至空气缓冲器(S247)内的水帘喷淋器。
- 根据权利要求82或83或84或85所述的餐厨垃圾全方位综合处理系统,其特征是:所述的空气缓冲器(S247)内部上方还安装有用于检测空气缓冲器(S247)内部液面高度的在线液面监控器(S251)。
- 根据权利要求81或82或83或84或85所述的餐厨垃圾全方位综合处理系统,其特征是:所述的初级烟气处理管道(S253)内设有一个以上的负离子荷电陶瓷(S254),该陶瓷件无须电源,能自然释放负离子,每个负离子荷电陶瓷(S254)后端对应安装有一个高速水雾区喷头(S255)。
- 根据权利要求87所述的餐厨垃圾全方位综合处理系统,其特征是:所述的每个高速水雾区喷头(S255)后端安装有一个导流板(S256)。
- 根据权利要求88所述的餐厨垃圾全方位综合处理系统,其特征是:所述的导流板(S256)采用钝角导流板。
- 根据权利要求87所述的餐厨垃圾全方位综合处理系统,其特征是:所述的负离子荷电陶瓷(S254)安装在初级烟气处理管道(S253)内的左、右、上三面上。
- 根据权利要求81或82或83或84或85所述的餐厨垃圾全方位综合处理系统,其特征是:所述的尾气处理系统还包括冷却塔(S269),冷却塔(S269)对烟气排放设备(S264)中的热交换器(S266)内的热水气进行冷却。
- 根据权利要求1所述的餐厨垃圾全方位综合处理系统,其特征是:所述的系统还包括对产生有以为公端的空气及生产区空气处理的等离子光触媒负离子空气除臭杀菌装置,等离子光触媒负离子空气除臭杀菌装置的进风口安装于各个餐厨垃圾收集池的四周。
- 根据权利要求92所述的餐厨垃圾全方位综合处理系统,其特征是:所述的等离子光触媒负离子空气除臭、杀菌装置包括空气输送管道(T272)、光催化主处理器(T274)和活性碳空气过滤器(T281),气体输入空气输送管道(T272)内,空气输送管道(T272)内设有负离子装置,气体通过空气输送管道(T272)输入至光催化主处理器(T274)内,光催化主处理器(T274)内设有空气通道,空气通道内安装有一个以上的发光波长为253nm——258nm的紫外线光管(T276),紫外线光管(T276)后端固定安装有二氧化钛光催化触板(T278),空气通道尾端与活性碳空气过滤器(T281)连通,通过活性碳空气过滤器(T281)将气体输出。
- 根据权利要求93所述的餐厨垃圾全方位综合处理系统,其特征是:所述的光催化主处理器(T274)和活性碳空气过滤器(T281)之间连接有空气排出管道(T279),空气排出管道(T279)内设有负离子装置,空气通道尾端与空气排出管道(T279)连通,空气排出管道(T279)与活性碳空气过滤器(T281)连通。
- 根据权利要求93所述的餐厨垃圾全方位综合处理系统,其特征是:所述的负离子装置采用负离子波纹板(T273),负离子波纹板(T273)呈层叠式安装。
- 根据权利要求95所述的餐厨垃圾全方位综合处理系统,其特征是:所述的负离子波纹板(T273)设有两段,前段为卧式安装,后段为立式安装。
- 根据权利要求93至96中任意一项所述的餐厨垃圾全方位综合处理系统,其特征是:所述的空气输送管道(T272)前端设有进风口(T270),进风口(T270)的后端安装有自动滑板闸阀(T271)。
- 根据权利要求93至96中任意一项所述的餐厨垃圾全方位综合处理系统,其特征是:所述的紫外线光管(T276)背面均配装光面反射板(T277)。
- 根据权利要求93至96中任意一项所述的餐厨垃圾全方位综合处理系统,其特征是:所述的光催化主处理器(T274)内的空气通道呈Z形,并于Z形的空气通道转角位置装有等离子发生器。
- 根据权利要求93至96中任意一项所述的餐厨垃圾全方位综合处理系统,其特征是:所述的二氧化钛光催化触板(T278)的尺寸和形状与空气通道横截面相吻合,可刚好挡在空气通道内。
- 根据权利要求93至96中任意一项所述的餐厨垃圾全方位综合处理系统,其特征是:所述的二氧化钛光催化触板(T278)呈蜂窝型。
- 根据权利要求101所述的餐厨垃圾全方位综合处理系统,其特征是:所述的二氧化钛光催化触板(T278)为厚度1cm——10cm,上开有一个以上的孔洞。
- 一种采用如权利要求1至102中任意一项所述的餐厨垃圾全方位综合处理系统的转化物制造方法,其特征是:所述的方法包括下述步骤A、将餐厨垃圾收集,并投入餐厨垃圾破袋装置,对其进行破袋处理;B、将破袋后的餐厨垃圾通过餐厨垃圾联合筛选装置进行联合筛选,从中分理处固体塑料和其它;C、对于除去固体塑料后的其他餐厨垃圾通过湿式高级氧化除臭灭活清洗降盐装置进行灭活处理;D、对于灭活后的垃圾通过立式脱水装置进行脱水处理;E、对于脱水后的物料通过物料破碎机进行粉碎。
- 根据权利要求103所述的方法,其特征是:所述的步骤E中粉碎后的物料经过生化处理装置进行生化处理,然后经过自动卸料多级干燥装置进行干燥,然后经过多级干燥和物料精选后,形成混合饲料。
- 根据权利要求104所述的方法,其特征是:所述的生化处理包括下述步骤:A、通过厌氧发酵池(I65)和两个副发酵器(I71)同时作用,生成预发酵物料;B、当预发酵工段完成后,将两个副发酵器(I71)内的物料,通过设于副发酵器(I71)底部的自动输送设备(I74)送进主发酵器,将厌氧发酵池(I65)内的物料,通过自动卸料系统(I67)也送进主发酵器,进行二次发酵;C、二次发酵完成后,进行出料。
- 根据权利要求105所述的方法,其特征是:所述的厌氧发酵池(I65)内生成预发酵物料时,将占总发酵基料重量的50%——80%的豆种作物桔秆和占总发酵基料重量的20%——50%的禾木料作物的当季桔秆破碎成粒径为0.5mm——1mm的粉末,并加入能分解粗纤维的复合菌剂对上述混合物料进行生化处理,所述的复合菌剂中菌种不少于两种,其中一种为米曲霉,复合菌剂的投入量为混合固体基料的1%,并加入化学成份氧化钙、氯化钠、磷酸氢钠和尿素。
- 根据权利要求106所述的方法,其特征是:所述的一个副发酵器(I71)内生成预发酵物料时,在副发酵器(I71)中加入已经人工灭活的餐厨垃圾为基料,加入占基料重量1%——2%的麸皮、占基料重量1%——3%的米糠和占基料重量1%的白糖作为混合料,并加入适量的水调成糊状,温度控制在20℃——30℃之间范围 ,并向混合料中加入占混合料总重量的2%——4%的面包酵母,并充分搅拌、强化曝气,以增强酵母生长,发酵的方式可采用老酵法。
- 根据权利要求107所述的方法,其特征是:所述的一个副发酵器(I71)内生成预发酵物料时,在副发酵器(I71)中加入已经过人工灭活、清洗并已脱水的餐厨垃圾为基料进行固态发酵,选用由绿色木霉、热带假丝酵母菌、白地菌和拟内孢霉酵母菌组成四菌混合菌剂,四菌的重量比例为2:2:1:1,接种量为总重量的2%,同时添加占总重量1%——1.5%的尿素,温度为25℃——42℃,由搅拌设备(I73)每小时翻滚一次,发酵时间9小时——10小时。
- 根据权利要求108所述的方法,其特征是:所述的二次发酵时,将已进行预生化处理的物料输入主发酵器,秸秆发酵物料中总物料重量百分比的10%——40%,面包酵母发酵物料占总物料重量百分比的20%,第二副发酵器(I71)内的发酵物料占总物料重量百分比的40%——70%,当三种经预发酵处理后的物料进入主发酵器内后,双层螺带搅拌器(I78)作360度旋转,旋转动作为往返方向,对物料作低速缓慢搅拌,主发酵器内的温度从初始的20℃开始起温,起温阶段物料平均温度20℃——28℃,恒温时间为4小时后关闭空气阀I87,同时提温至35℃——38℃,恒温时间3小时后,开启第一级引风装置I92,作轻质量排风,当上述的二次恒温时间完成后,再次提温至82℃,时间为2小时,并开启二级引风装置(I92)作强力排风。
- 根据权利要求103所述的方法,其特征是:所述的步骤B中产生的废塑料经过废塑料逆转工程装置逆转生成生物柴油。
- 根据权利要求110所述的方法,其特征是:所述的制造生物柴油产生的余渣粗炭黑人工陈化处理器,利用臭氧对物料进行陈化,通过化学陈化后的粗炭黑再进入物理陈化床,当粗炭黑经过人工陈化后,由专用自动输送工具输入物料配伍设备,每种配伍助剂均由液、固自动定量加料设备添加,通过多层推拉式螺杆将物料充分混合输入低硫高能环保清洁燃煤成形机,待物料成形后得到粗炭黑。
- 根据权利要求103至111中任意一项所述的方法,其特征是:所述的步骤A至步骤E中产生的污水经快速污水处理回用装置处理后,排出或回用。
- 根据权利要求103至111中任意一项所述的方法,其特征是:所述的步骤A至步骤E中产生的固体污泥处理经杂化荷电吸附剂生产装置处理后生成杂化荷电吸附剂。
- 根据权利要求103至111中任意一项所述的方法,其特征是:所述的步骤A至步骤E中产生的烟气、热烟气、粉尘和抽排口空气经环保处理装置处理后排出。
- 根据权利要求114所述的方法,其特征是:所述的处理后的气体经过等离子光触媒负离子空气除臭杀菌装置处理后排出。
- 根据权利要求103至111中任意一项所述的方法,其特征是:所述的步骤A至步骤E中产生的油水混合物通过免蒸馏法生物柴油生产方法生产生物柴油,该方法包括下述步骤:(1)、将餐厨垃圾生产过程中所产生的油、水、固混合物通过卧式螺带固液分离设备(O151)进行脱固处理,得到油水混合液;(2)、将油水混合液输送至油水分离塔(O152)进行油水分离,将分离后的油脂输入储油容器(O149);(3)、当需要对生物油脂时行加工处理时,通过输送泵等工具将生物油脂送进油脂胶质脱除设备(O158)内后,启动旋浆水力推进机(O160),并加入磷酸,磷酸与生物油脂的比例为不超过油脂总量的0.8%——1.2%,利用油脂胶质脱除设备(O158)两端的旋浆推力使油脂胶质脱除设备(O158)内部的液体产生相向撞击,撞击时间为10 min——15min,在液体的相向撞击时间结束后,当即加入稀盐水,稀盐水中水、盐的重量比为95:5至90:10之间,生物油脂与稀盐水的重量比例为90:10至80:20之间;(4)、继续启动旋浆水力推进机(O160),时间为10 min——20min;(5)、油脂混合体于油脂胶质脱除设备(O158)中停留60min——120min;(6)、将已脱胶质的生物油脂被输进生物油常温脂交换设备(O161);(7)、当生物油常温脂交换设备(O161)内的油脂输入的液面达到生产工艺设定的液面高度时,停止输入,开始启动生物油常温脂交换设备(O161)底部的鼓气管(O171),打开投料口(O169),加入固体催化剂和甲醇,固体催化剂用量为生物油脂质量的1.5%——3.5%,甲醇用量为生物油脂质量的3%——8%,在加入甲醇后再加入共溶剂;(8)、利用搅拌器连续搅拌10 min——15min,再加入固体金属碱催化剂,加入量为生物油脂质量的3%——4.5%;(9)、当加入所需要的助剂后,关闭投料孔(O169),开启物料循环输送泵,并开启超声波发生器(O162),超声波发生器(O162)的初始频率为25KHZ,时间为1min,随后逐步增大到30KHZ,时间为30 min——40min,反应温度为25——35℃。(10)、当油脂于生物油常温脂交换设备(O161)中完成脂交换后,将生物油脂混合物输入分液设备(O172)静置分层,上层为甲醇和甘油混合液体,下层为粗制生物柴油;(11)、首先将分液设备设于下部排液口开启,让粗制生物柴油输送进入过滤设备(O173),过滤后得到精制生物柴油并回收固体催化剂。
- 根据权利要求116所述的方法,其特征是:所述的油水分离时,油水分离塔(O152)内的油水混合液加热至60℃——85℃,待生物油脂上浮后实现油水分层,上层的生物油脂由刮油器(O155)刮出,并通过出油管道(O156)送入储油容器内。
- 根据权利要求116所述的方法,其特征是:所述的共溶剂的选择为甲乙醇的任意比例的混合物,共溶剂的加入量是生物油脂质量的0.5%——2%,共溶剂还包括有加入量是生物油脂质量的0.5%的丁醇。
- 根据权利要求116所述的方法,其特征是:所述的固体阴离子金属碱催化剂的特征是以试剂活性碳和铝、钠、铁、锂的环状结构硅酸盐矿物的纳米颗粒为基核,再外裹硅、铝、锂网状骨架介质,且带极性的杂化荷载体,再净该载体浸渍于KNO3液体中,经处理后而成为带极性的杂化荷电,含15%——25%的KNO3的固体阴离子金属碱催化剂。
- 根据权利要求116所述的方法,其特征是:所述的生物柴油通过微乳化生物柴油的制作装置制作成乳化生物柴油,该方法包括下述步骤:(1)、将粗生物柴油输入上述的微乳化生物柴油装置内,启动搅拌系统,加入30%-80%国III标准柴油后,搅拌5min;(2)加入亲水剂,加入量为纯生物柴油和国III标准柴油总重量的2-3%,作1min——15min时间的搅拌;(3)、加入丁醇作为中间体,加入量为纯生物柴油和国III标准柴油总重量的2-4%,继续对混合液作不间接搅拌15min,搅拌时,垂直搅拌器(P175)作100转/min——130转/min的转速搅拌;(4)、加入异戊烷作为自燃温度调节剂,加入量为纯生物柴油总重量的1.5-2%;(4)、加入富氧水,水占产品总重量的1%——20%,再搅拌15min,转速调整为170转/min——200转/min,再加入十八碳—顺—9—烯酸作为乳化剂,十八碳—顺—9—烯酸的加入量为所加入干净水重量的70%——90%,在搅拌设备的连续搅拌下直至澄清透明为止,此时,搅拌器的转速调整为280——340转/min,一般需要连续搅拌40——60min,待静置一定时间观察乳化油为清洁透明无分层后为成品。
- 根据权利要求120所述的方法,其特征是:所述的亲水剂选用阳离子表面活性剂及非离子表面活性剂联合的复配物料作为复合活性剂,配比例为阳离子表面活性剂50%,非离子表面活性剂50%。
- 根据权利要求120所述的方法,其特征是:所述的表面活性剂有三乙醇胺或六氢苯胺或西曲溴铵和氨水。
- 根据权利要求120所述的方法,其特征是:所述的富氧水的加入量为总重量的10%——20%。
- 根据权利要求120所述的方法,其特征是:所述的十八碳—顺—9—烯酸设定量的酸值为200。
Priority Applications (3)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
RU2015123832A RU2015123832A (ru) | 2012-11-23 | 2013-02-16 | Интегрированное устройство для полной переработки бытовых отходов и способ производства продукта |
SG11201503980RA SG11201503980RA (en) | 2012-11-23 | 2013-02-16 | Integrated apparatus for comprehensive treatment of food waste and product manufacturing method |
KR1020157013923A KR20150105299A (ko) | 2012-11-23 | 2013-02-16 | 주방 쓰레기를 전방위적으로 처리하는 통합 장치 및 생산물 제조 방법 |
Applications Claiming Priority (4)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201210481274 | 2012-11-23 | ||
CN201210481274.8 | 2012-11-23 | ||
CN201310038252.9A CN103071666B (zh) | 2012-11-23 | 2013-01-31 | 餐厨垃圾全方位处理的集成化装备及产物制造方法 |
CN201310038252.9 | 2013-01-31 |
Publications (1)
Publication Number | Publication Date |
---|---|
WO2014079135A1 true WO2014079135A1 (zh) | 2014-05-30 |
Family
ID=48098723
Family Applications (10)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
PCT/CN2013/071230 WO2014079171A1 (zh) | 2012-11-23 | 2013-01-31 | 富氧微乳化混合生物柴油的制作方法及装置 |
PCT/CN2013/071204 WO2014079165A1 (zh) | 2012-11-23 | 2013-01-31 | 餐厨垃圾联合筛选系统 |
PCT/CN2013/071225 WO2014079169A1 (zh) | 2012-11-23 | 2013-01-31 | 自动卸料多级干燥装置 |
PCT/CN2013/071237 WO2014079173A1 (zh) | 2012-11-23 | 2013-01-31 | 等离子光触媒负离子空气除臭、杀菌装置 |
PCT/CN2013/071228 WO2014079170A1 (zh) | 2012-11-23 | 2013-01-31 | 免蒸馏法生物柴油生产方法及系统 |
PCT/CN2013/071209 WO2014079166A1 (zh) | 2012-11-23 | 2013-01-31 | 立式脱水装置 |
PCT/CN2013/071210 WO2014079167A1 (zh) | 2012-11-23 | 2013-01-31 | 餐厨垃圾氧化、除臭、灭活、清洗降盐装置 |
PCT/CN2013/071235 WO2014079172A1 (zh) | 2012-11-23 | 2013-01-31 | 尾气处理系统 |
PCT/CN2013/071217 WO2014079168A1 (zh) | 2012-11-23 | 2013-01-31 | 生化发酵方法及装置 |
PCT/CN2013/000146 WO2014079135A1 (zh) | 2012-11-23 | 2013-02-16 | 餐厨垃圾全方位处理的集成化装备及产物制造方法 |
Family Applications Before (9)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
PCT/CN2013/071230 WO2014079171A1 (zh) | 2012-11-23 | 2013-01-31 | 富氧微乳化混合生物柴油的制作方法及装置 |
PCT/CN2013/071204 WO2014079165A1 (zh) | 2012-11-23 | 2013-01-31 | 餐厨垃圾联合筛选系统 |
PCT/CN2013/071225 WO2014079169A1 (zh) | 2012-11-23 | 2013-01-31 | 自动卸料多级干燥装置 |
PCT/CN2013/071237 WO2014079173A1 (zh) | 2012-11-23 | 2013-01-31 | 等离子光触媒负离子空气除臭、杀菌装置 |
PCT/CN2013/071228 WO2014079170A1 (zh) | 2012-11-23 | 2013-01-31 | 免蒸馏法生物柴油生产方法及系统 |
PCT/CN2013/071209 WO2014079166A1 (zh) | 2012-11-23 | 2013-01-31 | 立式脱水装置 |
PCT/CN2013/071210 WO2014079167A1 (zh) | 2012-11-23 | 2013-01-31 | 餐厨垃圾氧化、除臭、灭活、清洗降盐装置 |
PCT/CN2013/071235 WO2014079172A1 (zh) | 2012-11-23 | 2013-01-31 | 尾气处理系统 |
PCT/CN2013/071217 WO2014079168A1 (zh) | 2012-11-23 | 2013-01-31 | 生化发酵方法及装置 |
Country Status (6)
Country | Link |
---|---|
KR (1) | KR20150105299A (zh) |
CN (17) | CN203124393U (zh) |
HK (9) | HK1180713A1 (zh) |
RU (1) | RU2015123832A (zh) |
SG (1) | SG11201503980RA (zh) |
WO (10) | WO2014079171A1 (zh) |
Cited By (8)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN105712756A (zh) * | 2016-04-20 | 2016-06-29 | 常州市苏风机械有限公司 | 一种超高温有机肥发酵设备 |
CN110813997A (zh) * | 2019-11-26 | 2020-02-21 | 浙江任我行教育科技有限公司 | 一种纺织废料处理装置 |
CN111875664A (zh) * | 2020-07-31 | 2020-11-03 | 程红梅 | 一种小分子肽分离装置 |
US10823404B1 (en) | 2016-03-11 | 2020-11-03 | Pyrodyne Thermal, LLC | Materials handling system for feed injection to thermal kiln retorts |
CN112676298A (zh) * | 2020-11-13 | 2021-04-20 | 广东省建筑设计研究院有限公司 | 一种厨余垃圾与市政污泥、粪便的协同处理系统及方法 |
RU217262U1 (ru) * | 2022-12-21 | 2023-03-24 | Татьяна Сергеевна Макарова | Устройство для переработки пластиковых отходов 3D-печати в пластиковый филамент |
US20230142466A1 (en) * | 2021-11-05 | 2023-05-11 | Shenzhen Guanke Technologies Co., Ltd | Grating structure and uv light |
WO2024063256A1 (ko) * | 2022-09-20 | 2024-03-28 | 삼성전자주식회사 | 음식물 쓰레기 처리기 |
Families Citing this family (118)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2014079171A1 (zh) * | 2012-11-23 | 2014-05-30 | 华南再生资源(中山)有限公司 | 富氧微乳化混合生物柴油的制作方法及装置 |
CN103316575A (zh) * | 2013-07-09 | 2013-09-25 | 张家港市春泰环保机械工程有限公司 | 一种餐厨垃圾处理设备中的除臭装置 |
CN103418601B (zh) * | 2013-09-04 | 2015-07-22 | 湖南普惠环境科技有限公司 | 餐厨垃圾分拣、破碎、筛选的一体化设备 |
CN103508644B (zh) * | 2013-09-27 | 2014-11-05 | 浙江大学舟山海洋研究中心 | 油泥资源化利用中破包及筛分去杂一体化装置及方法 |
CN104674530B (zh) * | 2013-11-27 | 2018-08-07 | 海尔集团公司 | 一种具有气体净化装置的干衣机 |
CN103611397B (zh) * | 2013-12-09 | 2016-02-24 | 哈尔滨北方环保工程有限公司 | 高能光量子除臭装置 |
CN103853090A (zh) * | 2014-01-14 | 2014-06-11 | 鄂尔多斯市城市矿产研究开发有限责任公司 | 生活垃圾处理分选系统的自动控制 |
CN103949097B (zh) * | 2014-05-14 | 2016-03-16 | 重庆三峰卡万塔环境产业有限公司 | 垃圾与渗滤液的分离装置 |
CN104003558B (zh) * | 2014-06-17 | 2015-08-19 | 尹小林 | 一种城镇生活垃圾滤液处理装置 |
TWI552922B (zh) * | 2014-09-05 | 2016-10-11 | zhi-xiong Liao | Earth and stone bagging device |
CN104259177A (zh) * | 2014-09-12 | 2015-01-07 | 湖南树林环境科技有限公司 | 一种用餐厨垃圾和农林固废物生产土壤改良剂原料的方法 |
CN104258675B (zh) * | 2014-09-23 | 2016-04-06 | 成都冠禹科技有限公司 | 一种焚烧炉废气净化装置 |
CN104651413A (zh) * | 2014-10-11 | 2015-05-27 | 北京联合燃气技术研究发展中心 | 餐厨垃圾的资源化处理方法及系统 |
CN104263398B (zh) * | 2014-10-21 | 2016-01-20 | 冯曦 | 一种城市垃圾制取垃圾衍生燃料和柴油的方法 |
CN104450495B (zh) * | 2014-11-26 | 2016-04-06 | 上海第二工业大学 | 一种带有无线检测功能的菌类分解垃圾处理系统 |
CN104591475B (zh) * | 2014-12-04 | 2016-04-13 | 常州大学 | 一种餐厨垃圾中油脂物质处理方法 |
CN104588391B (zh) * | 2014-12-24 | 2017-01-04 | 邵宇 | 一种便捷式餐厨垃圾处理系统 |
CN104593954B (zh) * | 2015-01-26 | 2017-09-01 | 吴江市震宇缝制设备有限公司 | 一种缝制机进料装置 |
CN104816403B (zh) * | 2015-05-15 | 2017-03-15 | 马鞍山华诚塑业有限公司 | 一种纸塑分离后综合处理系统 |
CN106626307B (zh) * | 2015-05-15 | 2018-08-28 | 马鞍山华诚塑业有限公司 | 一种纸塑分离后挤塑成型系统的操作方法 |
CN105062697B (zh) * | 2015-08-24 | 2021-06-15 | 华南农业大学 | 一种利用预处理提高餐厨油脂酶法制备生物柴油产量的方法 |
CN105107332B (zh) * | 2015-09-21 | 2018-07-06 | 杨朴 | 一种沸腾炉除尘脱硫及尘灰处理方法 |
CN105251033A (zh) * | 2015-10-29 | 2016-01-20 | 天津万峰环保科技有限公司 | 一种利用特种uv处理恶臭气体的装置 |
CN105505557B (zh) * | 2015-11-25 | 2019-06-14 | 中国科学院广州能源研究所 | 一种连续提取和分离餐厨垃圾油脂的装置 |
CN105382017B (zh) * | 2015-12-22 | 2017-07-18 | 陈惊雷 | 一种垃圾处理器 |
CN105457442A (zh) * | 2015-12-29 | 2016-04-06 | 东莞市美捷金属制品有限公司 | 一种餐厨垃圾处理设备的过滤装置 |
CN105664206B (zh) * | 2016-01-28 | 2018-07-06 | 连云港佑源医药设备制造有限公司 | 一种集成压力式在线灭菌生产线 |
US10919249B2 (en) | 2016-02-19 | 2021-02-16 | Albert Mardikian | Apparatus for pressing and dehydrating of waste |
EP3417224B1 (en) * | 2016-02-19 | 2021-03-24 | Regreen Technologies, Inc. | System for processing waste |
CN105693310B (zh) * | 2016-04-20 | 2022-04-19 | 常州市苏风机械有限公司 | 超高温有机肥发酵设备搅拌装置 |
US9630888B1 (en) | 2016-05-17 | 2017-04-25 | B.A.M.2 Waste Water Consulting, Ptr. | Sanitary waste treatment method |
US10246380B2 (en) | 2016-05-17 | 2019-04-02 | B.A.M.2 Waste Water Consulting, Ptr. | Solid waste treatment method |
CN106040723A (zh) * | 2016-07-19 | 2016-10-26 | 苏州鸿本机械制造有限公司 | 一种厨余垃圾处理机的除臭系统 |
CN106070595A (zh) * | 2016-07-28 | 2016-11-09 | 合肥三伍机械有限公司 | 一种可燃油废气处理的谷物干燥机 |
CN106259882A (zh) * | 2016-07-28 | 2017-01-04 | 合肥三伍机械有限公司 | 一种可采用燃气的干燥机供热系统 |
CN106076552B (zh) * | 2016-07-29 | 2019-04-09 | 上海恒晔生物科技有限公司 | 耙刀刀片以及耙刀组件 |
CN106216358B (zh) * | 2016-07-29 | 2021-05-28 | 上海恒晔生物科技有限公司 | 齿轮驱动式滚筒装置和生化处理设备、系统及处理方法 |
CN106216359A (zh) * | 2016-08-04 | 2016-12-14 | 江苏菲力环保工程有限公司 | 一种有机废弃物资源化设备系统 |
WO2018026747A1 (en) | 2016-08-05 | 2018-02-08 | Rti International | Liquid waste treatment system |
WO2018031280A1 (en) * | 2016-08-08 | 2018-02-15 | Rti International | Solid waste treatment system |
CN106119096B (zh) * | 2016-08-31 | 2019-06-25 | 无锡托普搅拌设备有限公司 | 一种模块式高效干式厌氧发酵罐及其发酵处理方法 |
CN106140799B (zh) * | 2016-09-14 | 2018-03-09 | 中国科学院广州能源研究所 | 一种餐厨垃圾源头分类及预处理系统 |
CN106223093B (zh) * | 2016-09-19 | 2018-08-14 | 三峡大学 | 废纸重渣分离装置 |
CN106440738A (zh) * | 2016-09-30 | 2017-02-22 | 焦作市真节能干燥设备研发有限公司 | 多组扬料式二级滚筒烘干机 |
CN106440762A (zh) * | 2016-09-30 | 2017-02-22 | 焦作市真节能干燥设备研发有限公司 | 组合式滚筒内部扬料装置 |
CN106546087B (zh) * | 2016-10-31 | 2019-04-23 | 程建中 | 节能环保转筒式烘干机 |
CN106734100B (zh) * | 2016-12-28 | 2019-03-26 | 徐州方博环保设备有限公司 | 一种动物无害化处理设备 |
IL249923B (en) | 2017-01-03 | 2018-03-29 | Shohat Tsachi | Smart trash can |
CN106495373A (zh) * | 2017-01-06 | 2017-03-15 | 贵州大学 | 一种煤矿井下防爆可移动饮用水净化装置 |
CN107062267A (zh) * | 2017-01-13 | 2017-08-18 | 安徽未名鼎和环保有限公司 | 一种智能化垃圾焚烧处理进气控制系统 |
CN107052022A (zh) * | 2017-01-17 | 2017-08-18 | 绿华环保科技股份有限公司 | 一种有机废弃物智能化处理系统及资源化处理方法 |
CN108423962B (zh) * | 2017-02-14 | 2020-12-29 | 湖南省环境保护科学研究院 | 一种改善污泥脱水性能的方法 |
CN106914473A (zh) * | 2017-04-10 | 2017-07-04 | 东华理工大学 | 含有气体的固废物处理系统 |
CN107213715A (zh) * | 2017-07-12 | 2017-09-29 | 红安方达环保工程有限公司 | 一种长袋低压脉冲袋式除尘器 |
CN109351750A (zh) * | 2017-08-08 | 2019-02-19 | 江苏中科君达物联网股份有限公司 | 一种油气田固废环保处理一体机系统 |
CN107655310A (zh) * | 2017-09-30 | 2018-02-02 | 江苏金石研磨有限公司 | 一种天然气供热陶瓷微珠快速烘干系统 |
CN107744734B (zh) * | 2017-10-16 | 2021-04-23 | 中国核动力研究设计院 | 一种放射性废树脂射流搅拌装置 |
KR101823961B1 (ko) * | 2017-11-02 | 2018-03-14 | 도요엔지니어링코리아 주식회사 | 순환증기 재가열 슬러지 건조시스템 |
CN107702476B (zh) * | 2017-11-10 | 2022-09-30 | 上海艺迈实业有限公司 | 一种用于餐厨废弃物处理的余热回收利用装置及工艺流程 |
CN108159873B (zh) * | 2018-01-11 | 2020-04-17 | 浙江中寰环保科技有限公司 | 一种餐饮垃圾臭气处理系统及其处理方法 |
CN108435755B (zh) * | 2018-03-16 | 2019-11-26 | 张言敏 | 医疗废弃物回收处理装置 |
CN108686248B (zh) * | 2018-04-11 | 2020-07-28 | 重庆市长寿区可又可食品有限公司 | 食品加工车间除味装置 |
CN108620226B (zh) * | 2018-04-21 | 2021-03-26 | 青岛福创环境科技有限公司 | 一种生活垃圾清洁化分选砂石、玻璃、陶瓷的装置 |
CN108687110B (zh) * | 2018-05-14 | 2021-01-22 | 陈加宏 | 一种医疗废物分阶段粉碎处理的防泄漏装置 |
CN108704559B (zh) * | 2018-05-25 | 2024-03-26 | 合肥汇智新材料科技有限公司 | 一种注射成型用混合搅拌装置 |
CN108613264A (zh) * | 2018-06-08 | 2018-10-02 | 珠海市众澄天地科技有限公司 | 一种负离子空气净化器 |
WO2019237328A1 (zh) * | 2018-06-15 | 2019-12-19 | 世界家庭用具制品厂有限公司 | 一种用餐厨废料制备生物柴油的方法 |
CN108741117B (zh) * | 2018-06-19 | 2020-06-30 | 湖南金昇茶油科技发展有限公司 | 一种油茶脱壳机 |
CN108639480B (zh) * | 2018-06-21 | 2024-02-09 | 重庆耐德生态科技有限公司 | 一种餐厨垃圾一级破袋系统 |
CN108889769A (zh) * | 2018-07-06 | 2018-11-27 | 南京西普环保科技有限公司 | 一种厨余垃圾处理系统及厨余机 |
CN209508172U (zh) * | 2018-08-13 | 2019-10-18 | 湖南叶林环保科技有限公司 | 有机危废热解气净化系统 |
CN110885259A (zh) * | 2018-08-15 | 2020-03-17 | 浙江宝成机械科技有限公司 | 一种餐厨垃圾的高温好氧发酵处理设备 |
CN109158042B (zh) * | 2018-09-07 | 2021-05-25 | 南通黄海药械有限公司 | 一种具有自动配比功能的农药喷洒混合装置 |
CN109433788B (zh) * | 2018-10-29 | 2020-03-20 | 青岛大学附属医院 | 医疗废物环保处理装置 |
CN109367876B (zh) * | 2018-12-05 | 2024-01-26 | 青岛博世达包装机械有限公司 | 面包胚自动直入理料线 |
US20220049200A1 (en) * | 2018-12-10 | 2022-02-17 | Sung Min Lee | Apparatus for producing fermented soybean meal |
CN109454095A (zh) * | 2018-12-27 | 2019-03-12 | 江苏泓润生物质能科技有限公司 | 一种用于源头预处理后餐厨废弃物的料仓 |
CN109609235A (zh) * | 2019-01-02 | 2019-04-12 | 镇江市中运城市环境治理有限公司 | 一种垃圾环保再生煤的生产工艺 |
CN109679841A (zh) * | 2019-01-16 | 2019-04-26 | 杭州裕登农业技术开发有限公司 | 一种卧式发酵罐 |
CN110053878B (zh) * | 2019-03-28 | 2024-01-30 | 浙江海洋大学 | 一种用于实验室的水泥存取装置 |
CN110064291B (zh) * | 2019-05-07 | 2021-09-24 | 中冶华天工程技术有限公司 | 集成式低浓度恶臭废气处理装置 |
CN110452031A (zh) * | 2019-09-23 | 2019-11-15 | 上海洁鹿环保科技有限公司 | 餐余垃圾处理设备 |
CN110698013A (zh) * | 2019-10-29 | 2020-01-17 | 北京汉能清源科技有限公司 | 协同分布式深度处理市政污泥和餐厨垃圾的方法和系统 |
CN110777895A (zh) * | 2019-11-11 | 2020-02-11 | 长沙凯天工研院环保服务有限公司 | 一种餐厨垃圾处理系统 |
CN110885168A (zh) * | 2019-12-19 | 2020-03-17 | 天津滨海新区塘沽环科新河污水处理有限公司 | 活性污泥无害化、资源化处理系统及其工艺 |
CN111635774B (zh) * | 2020-04-22 | 2021-03-23 | 生态环境部华南环境科学研究所 | 一种农业有机固体废物多级热解装置 |
KR102234951B1 (ko) * | 2020-05-13 | 2021-04-01 | 주식회사 네오디아 | 음식물 폐기물의 미세 파쇄 및 선별 장치 |
CN111559821A (zh) * | 2020-05-25 | 2020-08-21 | 杭州蒙杜环保科技有限公司 | 一种具有尾气净化功能的厨余污水处理装置 |
CN111842414A (zh) * | 2020-06-30 | 2020-10-30 | 北京中科工匠科技有限公司 | 餐厨垃圾分布式处置系统及方法 |
CN111807675B (zh) * | 2020-07-04 | 2021-04-09 | 上海和惠生态环境科技有限公司 | 油泥破包三相分离工艺及油泥破包设备 |
CN112024569B (zh) * | 2020-07-31 | 2023-12-05 | 浙江天地环保科技股份有限公司 | 一种封闭式易腐有机废弃物生物处理自动化集成系统及方法 |
CN112007396B (zh) * | 2020-08-18 | 2022-04-15 | 上海洁海环境建设发展有限公司 | 车辆泔水收集回收方法及系统 |
CN112013698B (zh) * | 2020-09-04 | 2021-09-21 | 河北工程大学 | 一种基于煤矿矿井排风余热的送风加热设备 |
CN112923712A (zh) * | 2020-11-19 | 2021-06-08 | 南昌航空大学 | 一种用于餐厨垃圾干燥的餐厨垃圾干燥机 |
CN112594696B (zh) * | 2020-12-16 | 2022-11-11 | 陕西厚亿节能环保新材料科技有限公司 | 一种小型节能绿色固废处理系统 |
CN112781971B (zh) * | 2020-12-31 | 2023-02-10 | 南京信息工程大学 | 一种低温凝固浓缩收集气溶胶装置及其运行方法 |
CN112811673B (zh) * | 2021-02-04 | 2022-12-06 | 苏州易思达环保科技有限公司 | 一种电镀废水处理池 |
CN112923662B (zh) * | 2021-03-01 | 2021-11-16 | 中国科学院过程工程研究所 | 一种两段式分离干燥装置及固废分离干燥方法 |
CN113105996B (zh) * | 2021-03-10 | 2023-07-07 | 长沙工研院环保有限公司 | 一种水力气力联动浮选餐厨垃圾厌氧发酵处理系统 |
CN112759443B (zh) * | 2021-03-15 | 2024-02-02 | 河北省农业机械化研究所有限公司 | 一种农业废弃物快速均匀发酵处理装置 |
CN113004066A (zh) * | 2021-03-26 | 2021-06-22 | 启迪城市环境服务集团有限公司 | 一种厨余垃圾快速处理设备及方法 |
CN113778036B (zh) * | 2021-09-27 | 2022-04-05 | 广州天幕信息科技有限公司 | 餐厨垃圾处理智能管理和控制方法及系统 |
CN113578179B (zh) * | 2021-09-30 | 2021-12-14 | 广东预防医学健康研究院(有限合伙) | 一种药物分析用预混合搅拌装置 |
CN114314763B (zh) * | 2021-12-14 | 2023-05-02 | 安徽元琛环保科技股份有限公司 | 一种环保型三维粒子电极的制备方法及制备的电极 |
CN114198988B (zh) * | 2021-12-29 | 2022-10-25 | 双胞胎(集团)股份有限公司 | 一种用于家畜饲料原料的脱水系统 |
WO2023139421A1 (en) * | 2022-01-24 | 2023-07-27 | Ariunbat Tserendash | Complex device and method for pyrolysis of organic raw materials and organic wastes |
CN114650708B (zh) * | 2022-03-01 | 2023-08-15 | 深圳市凌心科技有限公司 | 一种工业自动控制系统装置制造用高效降温设备 |
CN114702089B (zh) * | 2022-04-12 | 2023-03-31 | 中国神华煤制油化工有限公司 | 污水汽提塔的降液管溢流堰扰动装置及污水汽提塔 |
CN114698307B (zh) * | 2022-04-27 | 2023-01-20 | 广东科学技术职业学院 | 一种高效节能的plc电气控制柜 |
CN114577154B (zh) * | 2022-04-28 | 2022-07-15 | 广东环达工程检测有限公司 | 一种管道涂层厚度检测装置及其检测方法 |
CN115073217B (zh) * | 2022-06-17 | 2023-07-14 | 四川琳宸生物能源科技有限公司 | 一种具有降盐功能的餐厨垃圾制备有机肥系统及方法 |
CN115385476B (zh) * | 2022-08-22 | 2024-01-26 | 湖南仁和环境股份有限公司 | 一种餐厨垃圾发酵沼液除臭装置及方法 |
CN115608744B (zh) * | 2022-09-29 | 2023-06-02 | 广州市晶科电器有限公司 | 一种餐厨垃圾转化饲料设备 |
CN115414833B (zh) * | 2022-11-07 | 2023-03-21 | 中科微针(北京)科技有限公司 | 一种用于粘性溶液的制备以及消泡装置 |
US11939878B1 (en) | 2022-12-15 | 2024-03-26 | Ge Infrastructure Technology Llc | Turbomachine component having self-breaking supports |
US11920794B1 (en) | 2022-12-15 | 2024-03-05 | Ge Infrastructure Technology Llc | Combustor having thermally compliant bundled tube fuel nozzle |
CN116274259A (zh) * | 2023-05-16 | 2023-06-23 | 国家电投集团科学技术研究院有限公司 | 微型厨余垃圾处理系统和方法 |
CN117282516A (zh) * | 2023-11-24 | 2023-12-26 | 福建美天环保科技有限公司 | 一种餐厨垃圾破碎分离装置 |
Citations (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2003164831A (ja) * | 2001-12-03 | 2003-06-10 | Hayakawa Kankyo Kenkyusho:Kk | 超臨界水によるゴミ・廃棄物処理システムおよび発電システム |
JP2004168589A (ja) * | 2002-11-20 | 2004-06-17 | Kenjiro Tsuyuri | ゴミの焼却、焼却後の廃ガスの集塵・中和・触媒の反応装置及び触媒後の肥料化プラント並びにその構造 |
CN1631559A (zh) * | 2004-12-27 | 2005-06-29 | 徐晓军 | 生活垃圾湿式强化氧化消解的处理方法 |
US20090288938A1 (en) * | 2006-12-20 | 2009-11-26 | Jesus Eduardo Rodriguez Hernandez | System and method for obtaining hydrocarbons from organic and inorganic solid waste |
CN101130194B (zh) * | 2007-09-14 | 2010-04-14 | 苏州市洁净废植物油回收有限公司 | 餐余垃圾综合处理回收再利用的方法 |
CN101612630B (zh) * | 2009-06-24 | 2010-09-08 | 北京国宗元投资有限公司 | 生活垃圾无害化资源化实时处理方法和系统 |
CN101837366A (zh) * | 2010-05-17 | 2010-09-22 | 北京昊业怡生科技有限公司 | 餐厨垃圾集中处理的方法 |
Family Cites Families (93)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS5312902B2 (zh) * | 1972-03-27 | 1978-05-06 | ||
CH588052A5 (zh) * | 1975-04-01 | 1977-05-31 | Kunz W Ag Maschinen Und Appara | |
US5104047A (en) * | 1990-08-21 | 1992-04-14 | Simmons Leonard E | Wet process recovery system for solid waste |
CN2176820Y (zh) * | 1993-11-30 | 1994-09-14 | 天津市大港区振东玻璃钢厂 | 酸雾吸收器 |
JP2560202B2 (ja) * | 1994-03-17 | 1996-12-04 | 三井鉱山株式会社 | 開袋機 |
CN2224719Y (zh) * | 1995-03-03 | 1996-04-17 | 南通通德工程有限公司 | 复式固液分离机 |
SE506488C2 (sv) * | 1995-03-30 | 1997-12-22 | Liss Ola Lindkvist | Metod och apparat för sönderdelning av material som ska komposteras |
CN1146482A (zh) * | 1995-09-29 | 1997-04-02 | 上海赢得实业总公司 | 微乳化生物合成柴油 |
JPH09174098A (ja) * | 1995-12-28 | 1997-07-08 | Ebara Corp | 有機性汚泥の減量化法 |
CN1155452A (zh) * | 1996-06-03 | 1997-07-30 | 北京绿色环境工程技术研究所 | 一种垃圾发酵前分选回收装置 |
JPH1066951A (ja) * | 1996-08-28 | 1998-03-10 | Keihanna Kankyo Kk | 有機質廃棄物の炭化方法及び装置 |
JP3411482B2 (ja) * | 1997-10-01 | 2003-06-03 | 住友重機械工業株式会社 | ゴミ焼却炉における排ガス処理装置の運転方法 |
JPH11169628A (ja) * | 1997-12-15 | 1999-06-29 | Kyoei Sangyo Kk | 燃焼炉の排ガス処理方法及びその装置 |
JP2000015233A (ja) * | 1998-06-30 | 2000-01-18 | Toto Ltd | 厨芥処理装置および厨芥処理装置の運転方法 |
CN2358998Y (zh) * | 1998-11-06 | 2000-01-19 | 赵石林 | 生活垃圾湿式分选处理机 |
JP2001187375A (ja) * | 1999-10-22 | 2001-07-10 | Aichi Electric Co Ltd | 有機廃棄物の処理方法および処理装置 |
JP2002143896A (ja) * | 2000-11-15 | 2002-05-21 | Kiyomoto Iron & Machinery Works Co Ltd | 有機系廃棄物並びに下水汚泥若しくは畜糞又は下水汚泥及び畜糞の処理方法 |
CN2455257Y (zh) * | 2000-12-28 | 2001-10-24 | 西安交通大学 | 放电等离子体空气灭菌净化机 |
CN2483387Y (zh) * | 2001-06-13 | 2002-03-27 | 天诚环保生化科技股份有限公司 | 厨余有机废弃物的处理机 |
BE1014261A3 (nl) * | 2001-06-20 | 2003-07-01 | Organic Waste Systems Naamloze | Werkwijze en inrichting voor het anaeroob vergisten van organisch materiaal. |
CN2527567Y (zh) * | 2002-01-17 | 2002-12-25 | 谢照仁 | 热风双重加热厨余发酵机 |
KR100453932B1 (ko) * | 2002-02-07 | 2004-10-26 | 구경신 | 건설폐기물의 수조식 골재선별 처리장치 |
US6979426B2 (en) * | 2002-03-15 | 2005-12-27 | Biodiesel Industries | Biodiesel production unit |
CN2574791Y (zh) * | 2002-09-25 | 2003-09-24 | 天津百利珀金斯环保设备有限公司 | 垃圾破袋处理装置 |
JP2004136169A (ja) * | 2002-10-16 | 2004-05-13 | Aizawa Seisakusho:Kk | 複動式連続生ごみ処理装置 |
CN1206189C (zh) * | 2003-01-23 | 2005-06-15 | 湖南大学 | 厌氧好氧一体式堆肥反应装置 |
CN2618688Y (zh) * | 2003-04-17 | 2004-06-02 | 四川省环能科技实业有限公司 | 多功能垃圾分选机 |
CN1212494C (zh) * | 2003-05-15 | 2005-07-27 | 南海市华星光电实业有限公司 | 一种室内空气的净化方法及装置 |
CN2644943Y (zh) * | 2003-09-05 | 2004-09-29 | 宋勇 | 一种可通新鲜空气的空调器 |
CN2659549Y (zh) * | 2003-09-28 | 2004-12-01 | 赵石林 | 生活垃圾有机物湿式分离机 |
CN2655913Y (zh) * | 2003-10-31 | 2004-11-17 | 罗炳灿 | 等离子体空气灭菌净化器 |
JP4398270B2 (ja) * | 2004-02-03 | 2010-01-13 | 新日鉄エンジニアリング株式会社 | 植物繊維を含む有機土の処理方法及び有機土処理装置 |
JP2006044956A (ja) * | 2004-07-30 | 2006-02-16 | Yuasa Sangyo:Kk | 有機肥料の製造方法 |
CN2731377Y (zh) * | 2004-09-22 | 2005-10-05 | 陈奇森 | 气流式干燥机 |
CN100435959C (zh) * | 2004-09-24 | 2008-11-26 | 邓连松 | 风扫环磨机 |
CN100441966C (zh) * | 2004-10-14 | 2008-12-10 | 北京工业大学 | 立式光催化空气净化器 |
US7171762B2 (en) * | 2004-10-19 | 2007-02-06 | Gala Industries, Inc. | Self-cleaning centrifugal pellet dryer and method thereof |
KR20060117617A (ko) * | 2005-05-13 | 2006-11-17 | 차순용 | 폐기물 건조장치 |
CN2844810Y (zh) * | 2005-09-02 | 2006-12-06 | 上海山水路桥机械设备有限公司 | 三筒烘干机 |
JP4771257B2 (ja) * | 2005-11-28 | 2011-09-14 | 株式会社松尾工業所 | 廃食用油精製装置 |
JP3892893B1 (ja) * | 2006-03-24 | 2007-03-14 | 寺尾 義典 | 廃食用油の処理装置 |
CN2911573Y (zh) * | 2006-04-25 | 2007-06-13 | 岳邦富 | 单级干燥滚筒和多级干燥滚筒及其新型高湿物料烘干机 |
CN101134610A (zh) * | 2006-08-28 | 2008-03-05 | 上海科林环保工程技术有限公司 | 餐厅含油废水净化处理装置 |
US20100284854A1 (en) * | 2007-01-03 | 2010-11-11 | John Lee Edwards | Radicals on eradication surfaces |
CN101011593A (zh) * | 2007-02-02 | 2007-08-08 | 上海福缘电子有限公司 | 具有高浓度负离子辐射的空气净化器 |
CN201037141Y (zh) * | 2007-03-20 | 2008-03-19 | 赵山山 | 全天候高效沼气发生器 |
CN201055804Y (zh) * | 2007-04-27 | 2008-05-07 | 广州德润环保科技发展有限公司 | 立式可腐有机垃圾的破碎与脱水装置 |
CN201044896Y (zh) * | 2007-05-22 | 2008-04-09 | 宁波大学 | 一种油柜式全自动柴油动态乳化装置 |
CN101219331B (zh) * | 2007-09-28 | 2010-12-08 | 泉州市天龙环境工程有限公司 | 燃煤锅炉烟气脱硫除尘净化系统 |
CN101219824A (zh) * | 2007-11-20 | 2008-07-16 | 无锡林信环保工程有限公司 | 曝气流化床微电解装置 |
CN201176436Y (zh) * | 2008-02-01 | 2009-01-07 | 李尚云 | 沼气发酵罐 |
CN101284280A (zh) * | 2008-04-30 | 2008-10-15 | 北京恒业村科技有限公司 | 小型垃圾物料分选装置 |
CN101722172A (zh) * | 2008-10-16 | 2010-06-09 | 王志成 | 生活垃圾综合分选机 |
CN101429480A (zh) * | 2008-12-18 | 2009-05-13 | 新疆西域牧歌农业科技有限公司 | 一种秸秆混合原料发酵产沼气的方法及装置 |
CN201366110Y (zh) * | 2009-01-09 | 2009-12-23 | 镇江同盛环保设备工程有限公司 | 气固两相臭气净化装置 |
US20100267102A1 (en) * | 2009-04-16 | 2010-10-21 | Feed Resource Recovery, Inc. | Waste distribution, conversion, and utilization |
CN101920041A (zh) * | 2009-06-11 | 2010-12-22 | 张俊杰 | 垃圾站综合性消毒、除臭及污水净化循环利用系统 |
CN201439395U (zh) * | 2009-06-22 | 2010-04-21 | 北京昊业怡生科技有限公司 | 破袋机 |
CN101618391A (zh) * | 2009-07-15 | 2010-01-06 | 无锡汉神电气有限公司 | 一种催化氧化式有机垃圾的处理系统 |
CN101717716B (zh) * | 2009-09-28 | 2012-07-25 | 浙江科峰生物技术有限公司 | 自动链带式固态发酵反应装置及其自动固态发酵的方法 |
CN201618489U (zh) * | 2009-11-04 | 2010-11-03 | 煤炭科学研究总院杭州环境保护研究所 | 一种化工废气喷淋旋流组合净化装置 |
CN102060577B (zh) * | 2009-11-18 | 2013-08-14 | 余福华 | 一种将泔水处理成有机肥料的设备 |
CN201596564U (zh) * | 2010-02-03 | 2010-10-06 | 天津德为环保工程设备有限公司 | 城市生活垃圾资源化分选装置 |
CN201653092U (zh) * | 2010-03-24 | 2010-11-24 | 楼生友 | 静音式节能干燥机 |
CN101816874B (zh) * | 2010-05-12 | 2011-11-23 | 华南再生资源(中山)有限公司 | 燃料裂解炉尾气处理系统 |
CN101962599A (zh) * | 2010-05-28 | 2011-02-02 | 王金华 | 利用地沟油提炼工业油脂的成套设备及方法 |
CN201728222U (zh) * | 2010-07-16 | 2011-02-02 | 林敏� | 餐厨垃圾综合处理机 |
CN101955382B (zh) * | 2010-08-16 | 2012-09-19 | 广州农冠生物科技有限公司 | 一种餐厨垃圾处理方法及其处理系统 |
CN101906355B (zh) * | 2010-08-30 | 2012-02-01 | 北京昊业怡生科技有限公司 | 一种利用餐厨垃圾回收油制取生物柴油的方法 |
CN101921049B (zh) * | 2010-09-21 | 2012-01-25 | 同济大学 | 一种城市污泥及有机质干法厌氧发酵产沼气的方法及装置 |
CN102151683A (zh) * | 2010-12-02 | 2011-08-17 | 北京工商大学 | 餐厨垃圾湿热—发酵综合无害化和资源化处理系统 |
CN201880472U (zh) * | 2010-12-06 | 2011-06-29 | 张步芳 | 一种工业燃煤锅炉烟气脱硫除尘装置 |
CN102093949A (zh) * | 2010-12-08 | 2011-06-15 | 江南大学 | 一种多功能生物固体发酵罐 |
CN102072628A (zh) * | 2010-12-29 | 2011-05-25 | 东莞市英豪机械有限公司 | 立式脱水设备 |
CN102125925A (zh) * | 2010-12-30 | 2011-07-20 | 东莞市东力环保设备有限公司 | 一种餐厨垃圾处理装置 |
CN102151687A (zh) * | 2010-12-31 | 2011-08-17 | 东莞市东力环保设备有限公司 | 一种零排放的餐厨垃圾处理装置 |
WO2012117145A1 (en) * | 2011-02-28 | 2012-09-07 | Kumera Oy | Method and apparatus for drying moist material |
CN102690134B (zh) * | 2011-03-21 | 2014-12-24 | 焦社杰 | 餐厨垃圾资源化处理方法及其处理系统 |
CN102211107B (zh) * | 2011-03-24 | 2013-02-27 | 天津农学院 | 餐厨废弃物无害化资源化处理设备 |
CN102728600A (zh) * | 2011-04-11 | 2012-10-17 | 张希曾 | 一种餐厨垃圾综合处理方法 |
CN202081098U (zh) * | 2011-05-05 | 2011-12-21 | 郑州蓝德环保科技有限公司 | 干法湿法联合发酵秸秆的加工装置 |
CN102218441B (zh) * | 2011-05-11 | 2013-08-21 | 中山市泰帝科技有限公司 | 一种餐厨垃圾的固液分离装置及方法 |
CN102295997B (zh) * | 2011-07-07 | 2013-09-04 | 严正华 | 一种厨余废弃油脂处理方法及系统 |
CN102441557B (zh) * | 2011-10-21 | 2013-11-06 | 中国科学院过程工程研究所 | 一种好氧-厌氧联合固态发酵装置及发酵方法 |
CN102357517A (zh) * | 2011-11-16 | 2012-02-22 | 上海野马环保设备工程有限公司 | 生活垃圾破碎、压实一体化处理系统 |
CN202322431U (zh) * | 2011-11-29 | 2012-07-11 | 四川深蓝环保科技股份有限公司 | 一种餐厨废物的油脂分离回收装置 |
CN202465702U (zh) * | 2011-12-16 | 2012-10-03 | 成都德通环境工程有限公司 | 一种用于餐厨垃圾处理的两步厌氧发酵装置 |
CN102631982A (zh) * | 2012-04-24 | 2012-08-15 | 张伟铭 | 一种生活垃圾新型水分选系统 |
CN102671924A (zh) * | 2012-05-29 | 2012-09-19 | 陈文才 | 餐饮垃圾综合回收利用的方法 |
WO2014079171A1 (zh) * | 2012-11-23 | 2014-05-30 | 华南再生资源(中山)有限公司 | 富氧微乳化混合生物柴油的制作方法及装置 |
CN203295470U (zh) * | 2013-01-31 | 2013-11-20 | 华南再生资源(中山)有限公司 | 富氧微乳化混合生物柴油的制作装置 |
CN203183865U (zh) * | 2013-01-31 | 2013-09-11 | 华南再生资源(中山)有限公司 | 尾气处理系统 |
CN203228968U (zh) * | 2013-01-31 | 2013-10-09 | 华南再生资源(中山)有限公司 | 一种餐厨垃圾承装塑料袋分瓣割破装置 |
-
2013
- 2013-01-31 WO PCT/CN2013/071230 patent/WO2014079171A1/zh active Application Filing
- 2013-01-31 WO PCT/CN2013/071204 patent/WO2014079165A1/zh active Application Filing
- 2013-01-31 WO PCT/CN2013/071225 patent/WO2014079169A1/zh active Application Filing
- 2013-01-31 CN CN2013200551166U patent/CN203124393U/zh not_active Withdrawn - After Issue
- 2013-01-31 CN CN201310038171.9A patent/CN103084049B/zh not_active Expired - Fee Related
- 2013-01-31 CN CN201320054411XU patent/CN203316248U/zh not_active Withdrawn - After Issue
- 2013-01-31 CN CN201310038252.9A patent/CN103071666B/zh not_active Expired - Fee Related
- 2013-01-31 WO PCT/CN2013/071237 patent/WO2014079173A1/zh active Application Filing
- 2013-01-31 WO PCT/CN2013/071228 patent/WO2014079170A1/zh active Application Filing
- 2013-01-31 CN CN201310037324.8A patent/CN103072726B/zh not_active Expired - Fee Related
- 2013-01-31 CN CN201310038148.XA patent/CN103056151B/zh not_active Expired - Fee Related
- 2013-01-31 CN CN201310037944.1A patent/CN103056022B/zh not_active Expired - Fee Related
- 2013-01-31 WO PCT/CN2013/071209 patent/WO2014079166A1/zh active Application Filing
- 2013-01-31 CN CN201310038136.7A patent/CN103115477B/zh not_active Expired - Fee Related
- 2013-01-31 CN CN201310038186.5A patent/CN103056152B/zh not_active Expired - Fee Related
- 2013-01-31 WO PCT/CN2013/071210 patent/WO2014079167A1/zh active Application Filing
- 2013-01-31 CN CN2013200551772U patent/CN203128526U/zh not_active Expired - Fee Related
- 2013-01-31 CN CN2013200551768U patent/CN203124394U/zh not_active Expired - Fee Related
- 2013-01-31 CN CN2013200552991U patent/CN203124395U/zh not_active Withdrawn - After Issue
- 2013-01-31 CN CN2013200551753U patent/CN203323492U/zh not_active Withdrawn - After Issue
- 2013-01-31 CN CN201310038156.4A patent/CN103074131B/zh not_active Expired - Fee Related
- 2013-01-31 CN CN2013200542519U patent/CN203124392U/zh not_active Withdrawn - After Issue
- 2013-01-31 WO PCT/CN2013/071235 patent/WO2014079172A1/zh active Application Filing
- 2013-01-31 WO PCT/CN2013/071217 patent/WO2014079168A1/zh active Application Filing
- 2013-01-31 CN CN201310038212.4A patent/CN103060100B/zh not_active Expired - Fee Related
- 2013-01-31 CN CN201310038166.8A patent/CN103055650B/zh not_active Expired - Fee Related
- 2013-02-16 SG SG11201503980RA patent/SG11201503980RA/en unknown
- 2013-02-16 KR KR1020157013923A patent/KR20150105299A/ko not_active Application Discontinuation
- 2013-02-16 RU RU2015123832A patent/RU2015123832A/ru not_active Application Discontinuation
- 2013-02-16 WO PCT/CN2013/000146 patent/WO2014079135A1/zh active Application Filing
- 2013-07-09 HK HK13108008.8A patent/HK1180713A1/zh not_active IP Right Cessation
- 2013-07-09 HK HK13108009A patent/HK1180714A1/zh not_active IP Right Cessation
- 2013-07-09 HK HK13108011.3A patent/HK1180631A1/zh not_active IP Right Cessation
- 2013-07-09 HK HK13108005.1A patent/HK1180636A1/zh not_active IP Right Cessation
- 2013-07-09 HK HK13108013.1A patent/HK1180761A1/zh not_active IP Right Cessation
- 2013-07-09 HK HK13108004.2A patent/HK1180639A1/zh not_active IP Right Cessation
- 2013-07-09 HK HK13108006.0A patent/HK1180640A1/zh not_active IP Right Cessation
- 2013-07-09 HK HK13108010.4A patent/HK1180641A1/zh not_active IP Right Cessation
- 2013-07-09 HK HK13108012.2A patent/HK1180657A1/zh not_active IP Right Cessation
Patent Citations (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2003164831A (ja) * | 2001-12-03 | 2003-06-10 | Hayakawa Kankyo Kenkyusho:Kk | 超臨界水によるゴミ・廃棄物処理システムおよび発電システム |
JP2004168589A (ja) * | 2002-11-20 | 2004-06-17 | Kenjiro Tsuyuri | ゴミの焼却、焼却後の廃ガスの集塵・中和・触媒の反応装置及び触媒後の肥料化プラント並びにその構造 |
CN1631559A (zh) * | 2004-12-27 | 2005-06-29 | 徐晓军 | 生活垃圾湿式强化氧化消解的处理方法 |
US20090288938A1 (en) * | 2006-12-20 | 2009-11-26 | Jesus Eduardo Rodriguez Hernandez | System and method for obtaining hydrocarbons from organic and inorganic solid waste |
CN101130194B (zh) * | 2007-09-14 | 2010-04-14 | 苏州市洁净废植物油回收有限公司 | 餐余垃圾综合处理回收再利用的方法 |
CN101612630B (zh) * | 2009-06-24 | 2010-09-08 | 北京国宗元投资有限公司 | 生活垃圾无害化资源化实时处理方法和系统 |
CN101837366A (zh) * | 2010-05-17 | 2010-09-22 | 北京昊业怡生科技有限公司 | 餐厨垃圾集中处理的方法 |
Cited By (8)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US10823404B1 (en) | 2016-03-11 | 2020-11-03 | Pyrodyne Thermal, LLC | Materials handling system for feed injection to thermal kiln retorts |
CN105712756A (zh) * | 2016-04-20 | 2016-06-29 | 常州市苏风机械有限公司 | 一种超高温有机肥发酵设备 |
CN110813997A (zh) * | 2019-11-26 | 2020-02-21 | 浙江任我行教育科技有限公司 | 一种纺织废料处理装置 |
CN111875664A (zh) * | 2020-07-31 | 2020-11-03 | 程红梅 | 一种小分子肽分离装置 |
CN112676298A (zh) * | 2020-11-13 | 2021-04-20 | 广东省建筑设计研究院有限公司 | 一种厨余垃圾与市政污泥、粪便的协同处理系统及方法 |
US20230142466A1 (en) * | 2021-11-05 | 2023-05-11 | Shenzhen Guanke Technologies Co., Ltd | Grating structure and uv light |
WO2024063256A1 (ko) * | 2022-09-20 | 2024-03-28 | 삼성전자주식회사 | 음식물 쓰레기 처리기 |
RU217262U1 (ru) * | 2022-12-21 | 2023-03-24 | Татьяна Сергеевна Макарова | Устройство для переработки пластиковых отходов 3D-печати в пластиковый филамент |
Also Published As
Similar Documents
Publication | Publication Date | Title |
---|---|---|
WO2014079135A1 (zh) | 餐厨垃圾全方位处理的集成化装备及产物制造方法 | |
TWM517030U (zh) | 餐廚垃圾全方位處理的集成化裝備 | |
CN101947538B (zh) | 废弃纸、塑及其复合材料资源化回收系统 | |
CN111036643A (zh) | 一种餐厨垃圾、生活垃圾与污水厂污泥协同处理的方法 | |
CN101561143A (zh) | 一种生活垃圾焚烧发电前的预处理方法 | |
CN104438296A (zh) | 一种干法水泥回转窑协同处理生活垃圾系统及处理方法 | |
CN110899292A (zh) | 一种垃圾发电协同处理餐厨垃圾系统及方法 | |
CN2880295Y (zh) | 餐饮垃圾综合处理系统 | |
CN113042503A (zh) | 一种餐厨垃圾分解发酵实现完全资源化的方法 | |
CN204276506U (zh) | 一种干法水泥回转窑协同处理生活垃圾系统 | |
CN107900069A (zh) | 一种生活垃圾资源化的方法及系统 | |
WO2006089766A1 (de) | Verfahren und reaktor zur biologischen aufbereitung von organik enthaltenden abfallstoffen | |
CN113843265A (zh) | 一种船用餐厨垃圾处理系统及方法 | |
CN109761652A (zh) | 一种微生物法高效垃圾堆肥装置及垃圾处理方法 | |
KR20180038406A (ko) | 유기성 폐기물 발효 소멸장치 | |
CN112044914B (zh) | 厨余垃圾分离降解系统及方法 | |
WO2021129845A1 (zh) | 一种餐厨垃圾再生处理系统 | |
CN104293408A (zh) | 一种餐厨垃圾资源化处理方法 | |
CN108787705B (zh) | 城市生活垃圾处理工艺方法 | |
CN114178294A (zh) | 一种厨余垃圾全资源化利用方法 | |
DE102006009165A1 (de) | Verfahren und Reaktor zur biologischen Aufbereitung von Organik enthaltenden Abfallstoffen | |
CN108126972B (zh) | 一种餐厨垃圾的一体化破碎处理装置 | |
CN206858390U (zh) | 一种污泥能源化改性系统 | |
CN207362033U (zh) | 一种污泥排放处理装置 | |
CN112871985B (zh) | 一种餐厨垃圾的破碎处理装置 |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
121 | Ep: the epo has been informed by wipo that ep was designated in this application |
Ref document number: 13856476 Country of ref document: EP Kind code of ref document: A1 |
|
NENP | Non-entry into the national phase |
Ref country code: DE |
|
ENP | Entry into the national phase |
Ref document number: 20157013923 Country of ref document: KR Kind code of ref document: A |
|
ENP | Entry into the national phase |
Ref document number: 2015123832 Country of ref document: RU Kind code of ref document: A |
|
122 | Ep: pct application non-entry in european phase |
Ref document number: 13856476 Country of ref document: EP Kind code of ref document: A1 |