CN107265747B - Catering industry wastewater oil removal treatment method - Google Patents

Catering industry wastewater oil removal treatment method Download PDF

Info

Publication number
CN107265747B
CN107265747B CN201710693201.8A CN201710693201A CN107265747B CN 107265747 B CN107265747 B CN 107265747B CN 201710693201 A CN201710693201 A CN 201710693201A CN 107265747 B CN107265747 B CN 107265747B
Authority
CN
China
Prior art keywords
oil
wastewater
tank
outlet
bonds
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Active
Application number
CN201710693201.8A
Other languages
Chinese (zh)
Other versions
CN107265747A (en
Inventor
朱辉
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Anhui Anfeng Environmental Technology Co., Ltd
Original Assignee
Anhui Anfeng Environmental Technology Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Anhui Anfeng Environmental Technology Co Ltd filed Critical Anhui Anfeng Environmental Technology Co Ltd
Priority to CN201710693201.8A priority Critical patent/CN107265747B/en
Publication of CN107265747A publication Critical patent/CN107265747A/en
Application granted granted Critical
Publication of CN107265747B publication Critical patent/CN107265747B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F9/00Multistage treatment of water, waste water or sewage
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/001Processes for the treatment of water whereby the filtration technique is of importance
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/24Treatment of water, waste water, or sewage by flotation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/281Treatment of water, waste water, or sewage by sorption using inorganic sorbents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/288Treatment of water, waste water, or sewage by sorption using composite sorbents, e.g. coated, impregnated, multi-layered
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/40Devices for separating or removing fatty or oily substances or similar floating material
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/4608Treatment of water, waste water, or sewage by electrochemical methods using electrical discharges
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/48Treatment of water, waste water, or sewage with magnetic or electric fields
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/66Treatment of water, waste water, or sewage by neutralisation; pH adjustment
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F2001/007Processes including a sedimentation step
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/34Organic compounds containing oxygen
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2301/00General aspects of water treatment
    • C02F2301/08Multistage treatments, e.g. repetition of the same process step under different conditions

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Water Treatment By Sorption (AREA)
  • Water Treatment By Electricity Or Magnetism (AREA)

Abstract

The invention discloses a catering industry wastewater oil removal treatment method, wherein wastewater sequentially passes through a buffer tank, a coarse grating, a micro-bubble air flotation oil adsorption device, an oil catalytic reforming desorption reactor, a pH value adjusting tank, a primary sedimentation tank, an organic rhodium catalytic reaction tank, a biological denitrification tank, a secondary sedimentation tank and a water purification tank. The method creatively utilizes the catalytic action of the pi-allyl nickel compound on oil molecules, when oil in the wastewater is adsorbed by the modified diatomite and is at the temperature of 200-250 ℃, under the catalysis of the pi-allyl nickel compound, C-H bonds in the oil molecules can be broken briefly and rapidly recombined to form C-C bonds or C-H bonds, the C-H bonds can be broken again, and the C-C bonds cannot be broken again due to the limited catalytic action of the pi-allyl nickel compound, so that the oil molecules with short carbon chains can be gradually synthesized into heavy oil molecules with long carbon chains.

Description

Catering industry wastewater oil removal treatment method
Technical Field
The invention relates to a method for removing oil from restaurant wastewater, and belongs to the field of wastewater treatment in environmental protection.
Background
Among domestic sewage, restaurant oily sewage is one of the main water bodies. A large amount of sewage containing a large amount of animal and vegetable oil is discharged in daily life of numerous restaurants, dining halls, food processing enterprises and residents, and if the sewage is not treated directly, the sewage can cause the blockage of pipelines, the turbidity and the putrefaction of water and the breeding of disease sources.
At present, the existing oil removing method for restaurant sewage comprises the following four methods.
(1) The physical method mainly comprises a filtration separation method and an air flotation separation method, but the physical method is only suitable for separating oil products with larger particles in the wastewater, the treatment efficiency is 60-80%, and the oil content in the effluent is about 100-200 mg/L. The fine oil droplets and emulsified oil in the wastewater are difficult to remove.
(2) The chemical method has the advantages of low equipment cost, good treatment effect and simple operation; the disadvantages are the need to continuously put chemical agents into the waste water, the high operating cost and the introduction of secondary pollution.
(3) The physical and chemical methods mainly comprise an air floatation method, an adsorption method, an electrochemical method, an ultrasonic separation method and the like, and generally have the advantages of strong adaptability and wide selectivity.
(4) The biochemical treatment method is to decompose complex organic matters into simple substances by utilizing the biochemical action of microorganisms, thereby converting toxic substances into non-toxic substances and purifying the oily sewage. The microorganism can use organic matter as nutrient substance, so that a part of the organic matter can be absorbed and converted into organic components in the microorganism body or proliferated into new microorganism, and the rest can be oxidized and decomposed into simple organic or inorganic matter by the microorganism.
Because the traditional treatment methods all have certain defects, the existing treatment technical route is needed to be got rid of, a new way for treating domestic sewage to remove oil is developed, and a brand new domestic sewage oil removal treatment technology is developed.
Disclosure of Invention
In order to solve the defects in the prior art, the invention provides a method for removing oil from restaurant wastewater, the restaurant wastewater enters a buffer pool through a wastewater pipeline, centralized collection and stabilization are carried out at the buffer pool, an outlet of the buffer pool is connected with a coarse grid through the wastewater pipeline, large-diameter solid matters in the restaurant wastewater are removed at the buffer pool, an outlet of the coarse grid is connected with a micro-bubble oil adsorption device through the wastewater pipeline, 9 ultra-fine bubble generators are arranged at the bottom of the micro-bubble oil adsorption device, a transversely placed pi-allyl nickel compound modified diatomite adsorption film can be accommodated above the liquid level of the device, a water inlet valve is arranged at the upper part of the left side of the device, a water outlet valve is arranged at the bottom of the right side of the device, the restaurant wastewater containing oil and primarily removing large-particle-diameter matters through the coarse grid enters the interior of the device through the water inlet valve at the, the device generates ultra-fine bubbles with the diameter less than 50 microns, the ultra-fine bubbles can carry oil molecules in the wastewater to float upwards together and enable the oil molecules to be adsorbed by a pi-allylnickel-containing compound modified diatomite adsorption film on the liquid surface, the right side wall of the device is connected with a high-temperature oil catalytic reforming desorption reactor, so that an aerogel felt heat-insulating layer is attached to the right side wall of the device, and a stainless steel mechanical arm and a ball-rotating bearing are arranged at the top end of the aerogel felt heat-insulating layer; the oil catalytic reforming desorption reactor is made of high-strength stainless steel, 5 electric heating blast fans are arranged at the bottom of the oil catalytic reforming desorption reactor, a set of stainless steel membrane frame is arranged in the oil catalytic reforming desorption reactor, 5 pi-allyl nickel compound modified diatomite adsorption membranes to be subjected to high-temperature treatment can be vertically placed on the membrane frame, and a heavy oil outlet is formed in the right side of the bottom of the oil catalytic reforming desorption reactor; the method comprises the following steps that a modified diatomite adsorption film containing pi-allylnickel compounds and completely adsorbing oil is grabbed by a stainless steel mechanical arm and is vertically placed on a stainless steel film frame in an oil catalytic heavy desorption reactor, 5 electric heating air blower fans at the bottom of the reactor start to work to generate high-temperature air at 200-250 ℃, under the catalysis of pi-allylnickel compounds, C-H bonds in oil molecules can be broken and rapidly combined into C-C bonds, and the C-C bonds can not be broken again, so that the oil molecules with short carbon chains can be gradually synthesized into heavy oil molecules with long carbon chains, and meanwhile, the heavy oil molecules can be desorbed from the modified diatomite adsorption film containing the pi-allylnickel compounds at high temperature and are discharged from a heavy oil outlet on the right side of the bottom of the reactor after being converged, and can be collected and reused in a centralized manner; the outlet of the micro-bubble air-floating oil adsorption device is connected with a pH value adjusting tank through a waste water pipeline, the pH value of the waste water is adjusted to be nearly neutral, the outlet of the pH value adjusting tank is connected with a primary sedimentation tank 6 through a waste water pipeline, the waste water is settled and clarified, the outlet of the primary sedimentation tank is connected with an organic rhodium catalytic reaction tank through a waste water pipeline, the outer layer of the organic rhodium catalytic polymerization reaction tank is wrapped by a tank body insulating protective layer, the right upper part of the reaction tank is provided with a water inlet valve, the left lower part of the reaction tank is provided with a water outlet valve, the central part of the tank body is provided with dichlorotetracarbonyl bis rhodium porous filler which is used as a polymerization reaction catalyst, the lower part of the filler layer is connected with a particulate matter discharge port, the right and left side wall plates are respectively provided with a high-pressure discharge electrode, the left and right sides of the bottom of, the high-voltage discharge electrodes perform high-voltage discharge once every 0.2s to generate a high-voltage electric arc, high energy generated by the high-voltage electric arc is absorbed by residual grease in the wastewater, C-H bonds in grease molecules are excited by energy to be in an unstable state, and are broken and recombined under the catalytic action of dichlorotetracarbonyl dirhodium, macromolecular polymerized particles are finally generated and are dispersed in the water in the form of suspended matters, and are discharged out of the reaction tank through a water outlet valve on the right side of the reaction tank to enter a secondary sedimentation tank, residual insoluble substances in the wastewater are completely removed, an outlet of the secondary sedimentation tank is connected with a water purification tank through a wastewater pipeline, and an outlet of the water purification tank discharges the purified effluent after treatment through the wastewater pipeline.
The effective volume of the micro-bubble air-float oil adsorption device is 155m3The superfine bubble generator can generate superfine bubbles with the diameter less than 50 μm, the normal working voltage is 20V, and the working life is generally 5000 h.
The volume of the oil catalytic reforming desorption reactor is 330m3The electric heating blower can generate hot air at 200-250 ℃, and the normal working voltage is 380V.
The area of the pi-allyl nickel compound modified diatomite adsorption film is 10.2m2The content of the pi-allylnickel compound was 16.6g/m2The purity of the pi-allylnickel compound was 95.2%.
The invention has the advantages that:
(1) the method gets rid of the existing restaurant wastewater oil purification treatment mode, creatively adopts a technical route combining physical means and a chemical method, fully utilizes the adsorption effect of the modified diatomite and the catalytic synthesis effect of the pi-allyl nickel compound, so that the oil in the restaurant wastewater is adsorbed and enriched and undergoes a synthesis reaction to generate usable heavy oil, and the removal efficiency of the oil reaches 99.8 percent.
(2) The invention utilizes hot air as a heating source and adopts a mode of dispersing the pi-allyl nickel compound in the modified diatomite, so that the synthetic reaction is more completely carried out, the reaction efficiency is improved, and the processing capacity of the whole system is improved.
(3) The modified diatomite adsorption film used in the invention is regenerated after the thermal desorption process, and can be reused for adsorbing oil in wastewater, thereby realizing the reutilization of materials and greatly reducing the operation cost.
(4) The invention has the advantages of simple and easy principle, lower design and construction cost, better treatment effect and low operation and maintenance cost, and is beneficial to large-scale popularization and application.
Drawings
FIG. 1 is a schematic diagram of the apparatus of the present invention.
In the figure: 1-a buffer tank, 2-a coarse grid, 3-a microbubble air-floating oil adsorption device, 4-an oil catalytic reforming desorption reactor, 5-a pH value adjusting tank, 6-a primary sedimentation tank, 7-an organic rhodium catalytic reaction tank, 8-a secondary sedimentation tank and 9-a water purification tank;
FIG. 2 is a schematic diagram of a micro-bubble air-flotation oil adsorption device and an oil catalytic reforming desorption reactor.
32-a superfine bubble generator, 33-superfine bubbles, 34-a stainless steel mechanical arm, 35-a ball rotating bearing, 36-a water inlet valve and 37-a water outlet valve; 41-aerogel felt thermal insulation layer, 42-pi-allyl nickel compound modified diatomite adsorption film, 43-stainless steel film frame, 44-electric heating blower fan and 45-heavy oil outlet.
FIG. 3 is a schematic diagram of a high-pressure discharge organorhodium catalytic polymerization reactor.
71-high-voltage discharge electrode, 72-dichlorotetracarbonyldirhodium porous filler, 73-tank body insulating protective layer, 74-water inlet valve, 75-water outlet valve, 76-stirring paddle and 77-particle discharge port.
Detailed Description
As shown in figure 1, restaurant wastewater oil removal treatment method, oily restaurant wastewater enters a buffer tank 1 through a wastewater pipeline, centralized collection and preliminary stable adjustment are carried out, an outlet of the buffer tank 1 is connected with a coarse grating 2 through a wastewater pipeline, large-diameter solid matters in the restaurant wastewater are removed, an outlet of the coarse grating 2 is connected with a micro-bubble oil adsorption device 3 through a wastewater pipeline, a pi-allyl nickel compound-containing modified diatomite adsorption membrane 42 in the micro-bubble oil adsorption device 3 can be grabbed by a stainless steel mechanical arm 34 after oil is completely adsorbed, the membrane is sent to an oil catalytic reforming desorption reactor 4, heavy oil generated in the oil catalytic reforming desorption reactor 4 is discharged from a heavy oil outlet 45 and recycled, meanwhile, an outlet of the micro-bubble oil adsorption device 3 is connected with a pH value adjusting tank 5 through a wastewater pipeline, the pH value of the wastewater is adjusted to be nearly neutral, the outlet of the pH value adjusting tank 6 is connected with a primary sedimentation tank 6 through a waste water pipeline, the waste water is settled and clarified, and the outlet of the primary sedimentation tank 6 is connected with an organic rhodium catalytic reaction tank through a waste water pipeline7, polymerizing residual grease in the sewage into water-insoluble particles through high-voltage discharge catalysis, connecting the particles to a secondary sedimentation tank 8 through a wastewater pipeline, completely removing residual insoluble substances in the wastewater, connecting an outlet of the secondary sedimentation tank 8 to a water purification tank 9 through a wastewater pipeline, and discharging the treated purified effluent through a wastewater pipeline from an outlet of the water purification tank 9; wherein, the microbubble air-float oil adsorption device 3 is made of high-strength glass fiber reinforced plastic, and the effective volume is 155m39 superfine bubble generators 32 are arranged at the bottom of the device and can generate superfine bubbles 33 with the diameter less than 50 mu m, a transversely placed pi-allyl nickel compound modified diatomite adsorption film 42 with the area of 10.2m can be accommodated above the liquid level of the device2The content of the pi-allylnickel compound was 16.6g/m2The purity of the pi-allyl nickel compound is 95.2 percent, a water inlet valve 36 is arranged at the upper part of the left side of the device, a water outlet valve 37 is arranged at the bottom of the right side of the device, the right side wall of the device is connected with a high-temperature oil catalytic reforming desorption reactor 4, so an aerogel felt heat-insulating layer 41 is attached to the right side wall of the device, and a stainless steel mechanical arm 34 and a ball rotating bearing 35 are arranged at the top end of the aerogel felt heat-insulating layer 41; wherein, the oil catalytic reforming desorption reactor 4 is made of high-strength stainless steel and has a volume of 330m3The bottom of the device is provided with 5 electric heating blast fans 44 which can generate hot air at the temperature of 200-250 ℃, a set of stainless steel membrane frame 43 is arranged in the device, 5 pi-allyl nickel compound modified diatomite adsorption membranes 42 to be subjected to high-temperature treatment can be vertically placed on the membrane frame, and the right side of the bottom of the device is provided with a heavy oil outlet 45; restaurant wastewater containing oil and primarily removing large-particle-size substances through a coarse grating 2 enters the interior of a microbubble air-floating oil adsorption device 3 through a water inlet valve 36 at the upper left part of the device, 9 ultrafine bubble generators 32 start to work to generate ultrafine bubbles 33 with the diameter smaller than 50 microns, the ultrafine bubbles 33 can carry oil molecules in the wastewater to float upwards together and be adsorbed by a pi-allyl nickel compound-containing modified diatomite adsorption film 42 above the liquid surface, the pi-allyl nickel compound-containing modified diatomite adsorption film 42 which completely adsorbs the oil is grabbed by a stainless steel mechanical arm 34 and is vertically placed on a stainless steel film frame 43 in an oil catalytic heavy desorption reactor 4, 5 parts of electrothermal blowing fans 44 at the bottom of the reactor start to work to produce oilGenerating high-temperature air at 200-250 ℃, and under the catalysis of the pi-allyl nickel compound, the C-H bonds in oil molecules can be broken briefly and quickly recombined to form C-C bonds or C-H bonds, the C-H bonds can be broken again, and the C-C bonds can not be broken again due to the limited catalytic action of the pi-allyl nickel compound, so that the oil molecules with short carbon chains can be gradually synthesized into heavy oil molecules with long carbon chains. Meanwhile, heavy oil molecules are desorbed from the pi-allyl nickel compound-containing modified diatomite adsorption film 42 at high temperature, and are discharged from a heavy oil discharge port 45 on the right side of the bottom of the reactor after being converged, so that the heavy oil molecules can be collected and reused in a centralized manner. The outer layer of the high-voltage discharge organic rhodium catalytic polymerization reaction tank 7 is wrapped by a tank body insulating protective layer 73, the inner part of the high-voltage discharge organic rhodium catalytic polymerization reaction tank is of a silicon carbide ceramic structure, and the effective volume of the reaction tank is 133m3The right upper part of the reaction tank is provided with a water inlet valve 74, the left lower part is provided with a water outlet valve 75, the central part of the tank body is provided with a dichlorotetracarbonyldirhodium porous filler 72 serving as a polymerization reaction catalyst, the pore diameter of the filler is 5.2mm, and the specific surface area is 6.5cm2The lower part of the packing layer is connected with a particle discharge port 77, a high-voltage discharge electrode 71 is respectively arranged in the right middle of the left side wall plate and the right side wall plate, a stirring paddle 76 is respectively arranged on the left side and the right side of the bottom of the reaction tank, sewage enters the reaction tank through a water inlet valve 74 of a high-voltage discharge organic rhodium catalytic polymerization reaction tank 7, the high-voltage discharge electrodes 71 carry out high-voltage discharge once at an interval of 0.1s, the discharge voltage range is 8500-15000V, a high-voltage electric arc which traverses the left side and the right side of the tank body can be generated in the reaction tank, high energy generated by the high-voltage electric arc is absorbed by grease substances in the wastewater, C-H bonds in grease molecules are excited by energy to be in an unstable state, C-H bonds are broken and recombined under the surface catalytic action of dichlorotetracarbonyl rhodium, finally macromolecule polymerization particles are generated and, and is discharged out of the reaction tank through a water outlet valve at the right side of the reaction tank and enters a tertiary sedimentation tank 8.
A microbubble air-float oil adsorption device 3 with an effective volume of 275m3The ultra-fine bubble generator 32 can generate ultra-fine bubbles 33 with the diameter less than 50 μm, the normal working voltage is 20V, and the working life is generally 5000 h. Volume of oil catalytic reforming desorption reactor 4Is 330m3The device can contain 5 pieces of vertically placed pi-allyl nickel compound modified diatomite adsorption films 42 to be subjected to high-temperature treatment, an electric heating air blower 44 can generate hot air at the temperature of 200-250 ℃, and the working voltage is 380V. The area of the pi-allyl nickel compound-modified diatomite adsorption film 42 is 10.2m2The content of the pi-allylnickel compound was 16.6g/m2The purity of the pi-allylnickel compound was 95.2%.
The restaurant wastewater treated by the system has the oil removal efficiency of 99.8 percent.

Claims (1)

1. A restaurant wastewater oil removal treatment method is characterized in that restaurant wastewater enters a cache pool through a wastewater pipeline, centralized collection and stabilization are carried out at the cache pool, an outlet of the cache pool is connected with a coarse grating through the wastewater pipeline, large-diameter solid matters in the wastewater are removed at the cache pool, an outlet of the coarse grating is connected with a micro-bubble air-flotation oil adsorption device through the wastewater pipeline, 9 ultra-fine bubble generators are arranged at the bottom of the micro-bubble air-flotation oil adsorption device, a transversely placed pi-allyl nickel compound modified diatomite adsorption film can be accommodated above the liquid level of the device, a water inlet valve is arranged at the upper part of the left side of the micro-bubble air-flotation oil adsorption film, a water outlet valve is arranged at the bottom of the right side of the micro-bubble air-flotation oil adsorption device, wastewater containing oil and primarily removing large-diameter matters through the coarse grating enters the interior of the device through the water inlet valve at the, the ultrafine bubbles carry oil molecules in the wastewater to float upwards together and are adsorbed by a modified diatomite adsorption film containing pi-allylnickel compounds above the liquid surface, the right side wall of the device is connected with a high-temperature oil catalytic reforming desorption reactor, so that an aerogel felt heat-insulating layer is attached to the right side wall of the device, and a stainless steel mechanical arm and a ball-rotating bearing are arranged at the top end of the aerogel felt heat-insulating layer; the oil catalytic reforming desorption reactor is made of high-strength stainless steel, 5 electric heating blast fans are arranged at the bottom of the oil catalytic reforming desorption reactor, a set of stainless steel membrane frame is arranged in the oil catalytic reforming desorption reactor, 5 pi-allyl nickel compound modified diatomite adsorption membranes to be subjected to high-temperature treatment are vertically placed on the membrane frame, and a heavy oil outlet is formed in the right side of the bottom of the oil catalytic reforming desorption reactor; pi-allyl nickel compound-containing modified silicon capable of completely adsorbing oilThe method comprises the following steps that an algae soil adsorption film is grabbed by a stainless steel mechanical arm and is vertically placed on a stainless steel film frame in an oil catalytic heavy desorption reactor, 5 electric heating air blower fans at the bottom of the reactor start to work to generate high-temperature air at 200-250 ℃, under the catalysis of a pi-allyl nickel compound, C-H bonds in oil molecules are broken and rapidly combined into C-C bonds, and the C-C bonds are not broken again, so that the oil molecules with short carbon chains are gradually synthesized into heavy oil molecules with long carbon chains, and meanwhile, the heavy oil molecules are desorbed from a pi-allyl nickel compound modified diatomite adsorption film at high temperature and are discharged from a heavy oil outlet on the right side of the bottom of the reactor after being converged, and are collected and reused; the outlet of the micro-bubble air-floating oil adsorption device is connected with a pH value adjusting tank through a waste water pipeline, the pH value of the waste water is adjusted to be nearly neutral, the outlet of the pH value adjusting tank is connected with a primary sedimentation tank through a waste water pipeline, the waste water is settled and clarified, the outlet of the primary sedimentation tank is connected with an organic rhodium catalytic polymerization reaction tank through a waste water pipeline, the outer layer of the organic rhodium catalytic polymerization reaction tank is wrapped by a tank body insulating protective layer, the right upper part of the reaction tank is provided with a water inlet valve, the left lower part of the reaction tank is provided with a water outlet valve, the central part of the tank body is provided with dichlorotetracarbonyl bis rhodium porous filler which is used as a polymerization reaction catalyst, the lower part of the filler layer is connected with a particulate matter discharge port, the right and left side wall plates are respectively provided with a high-pressure discharge electrode, the left and right sides of the bottom of, high-voltage discharge is carried out by the high-voltage discharge electrode every 0.2s to generate a high-voltage electric arc, high energy generated by the high-voltage electric arc is absorbed by residual grease in the wastewater, C-H bonds in grease molecules are excited by energy to be in an unstable state and are broken and recombined under the catalytic action of dichlorotetracarbonyl dirhodium to finally generate macromolecular polymerized particles which are dispersed in the water in the form of suspended matters and are discharged out of the reaction tank through a water outlet valve at the lower left part of the reaction tank to enter a secondary sedimentation tank, residual insoluble substances in the wastewater are completely removed, an outlet of the secondary sedimentation tank is connected with a water purification tank through a wastewater pipeline, and a purified water after treatment is discharged through the wastewater pipeline from an outlet of the water purification tankDischarging water; wherein the effective volume of the micro-bubble air-float oil adsorption device is 155m3The superfine bubble generator can generate superfine bubbles with the diameter less than 50 mu m, and the working voltage is 20V; the volume of the oil catalytic reforming desorption reactor is 330m3The electric heating blower fan generates hot air at 200-250 ℃, and the working voltage is 380V.
CN201710693201.8A 2016-01-14 2016-01-14 Catering industry wastewater oil removal treatment method Active CN107265747B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201710693201.8A CN107265747B (en) 2016-01-14 2016-01-14 Catering industry wastewater oil removal treatment method

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
CN201710693201.8A CN107265747B (en) 2016-01-14 2016-01-14 Catering industry wastewater oil removal treatment method
CN201610021497.4A CN105461148B (en) 2016-01-14 2016-01-14 A kind of food and drink waste water oil removal treatment method

Related Parent Applications (1)

Application Number Title Priority Date Filing Date
CN201610021497.4A Division CN105461148B (en) 2016-01-14 2016-01-14 A kind of food and drink waste water oil removal treatment method

Publications (2)

Publication Number Publication Date
CN107265747A CN107265747A (en) 2017-10-20
CN107265747B true CN107265747B (en) 2020-08-07

Family

ID=55599374

Family Applications (4)

Application Number Title Priority Date Filing Date
CN201710694011.8A Active CN107285530B (en) 2016-01-14 2016-01-14 Waste water oil-removing treatment method
CN201610021497.4A Active CN105461148B (en) 2016-01-14 2016-01-14 A kind of food and drink waste water oil removal treatment method
CN201710693201.8A Active CN107265747B (en) 2016-01-14 2016-01-14 Catering industry wastewater oil removal treatment method
CN201710693317.1A Active CN107417018B (en) 2016-01-14 2016-01-14 Waste water oil removing method

Family Applications Before (2)

Application Number Title Priority Date Filing Date
CN201710694011.8A Active CN107285530B (en) 2016-01-14 2016-01-14 Waste water oil-removing treatment method
CN201610021497.4A Active CN105461148B (en) 2016-01-14 2016-01-14 A kind of food and drink waste water oil removal treatment method

Family Applications After (1)

Application Number Title Priority Date Filing Date
CN201710693317.1A Active CN107417018B (en) 2016-01-14 2016-01-14 Waste water oil removing method

Country Status (1)

Country Link
CN (4) CN107285530B (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107285530B (en) * 2016-01-14 2020-07-31 杭州富阳通讯塑料厂 Waste water oil-removing treatment method
US11325057B2 (en) * 2019-09-30 2022-05-10 Donald Nevin Sedimentary trap
CN110927353A (en) * 2019-12-11 2020-03-27 中国环境科学研究院 Rural domestic sewage measurement system

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103113003A (en) * 2013-03-11 2013-05-22 南京紫都环保科技有限公司 Complete equipment and process for processing coal tar wastewater
CN107285530A (en) * 2016-01-14 2017-10-24 朱辉 A kind of waste water oil removal treatment method

Family Cites Families (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0615106A (en) * 1992-01-20 1994-01-25 Yoshihide Shibano Method for removing oil content in liquid
CN101602531B (en) * 2009-07-16 2011-07-20 华南理工大学 Electrochemical method of oil removal of wastewater produced in oil extraction by polymer flooding displacement
CN103601337A (en) * 2013-10-15 2014-02-26 常州思宇环保材料科技有限公司 Device for removing washing agent from restaurant wastewater
CN103508641B (en) * 2013-10-28 2015-02-04 波鹰(厦门)科技有限公司 High-fat food processing wastewater treatment method
CN104628192B (en) * 2013-11-12 2016-05-25 中国石油化工股份有限公司 A kind of processing method of oily waste water
CN104386848B (en) * 2014-09-25 2016-02-24 昆明理工大学 A kind of method processing organotin factory effluent
CN104291532B (en) * 2014-10-27 2016-03-23 南京格洛特环境工程股份有限公司 A kind of 2-Naphthol production wastewater treatment method and apparatus
CN104310715B (en) * 2014-11-04 2016-04-27 唐山金利海生物柴油股份有限公司 A kind for the treatment of process of biodiesel wastewater
CN204675930U (en) * 2015-05-13 2015-09-30 陕西孚嘉石化科技有限公司 A kind of swash plate electricity flocculation skid mounted equipment processing oil field compression fracture water
CN105130096B (en) * 2015-07-16 2018-03-20 江西省宏丰塑胶有限公司 A kind of chemical engineering sewage advanced treatment system

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103113003A (en) * 2013-03-11 2013-05-22 南京紫都环保科技有限公司 Complete equipment and process for processing coal tar wastewater
CN107285530A (en) * 2016-01-14 2017-10-24 朱辉 A kind of waste water oil removal treatment method
CN107417018A (en) * 2016-01-14 2017-12-01 朱辉 A kind of waste water deoiling method

Also Published As

Publication number Publication date
CN107417018B (en) 2020-07-21
CN107265747A (en) 2017-10-20
CN107285530A (en) 2017-10-24
CN107417018A (en) 2017-12-01
CN107285530B (en) 2020-07-31
CN105461148B (en) 2017-11-07
CN105461148A (en) 2016-04-06

Similar Documents

Publication Publication Date Title
CN107265747B (en) Catering industry wastewater oil removal treatment method
CN105347561A (en) Integrated device for purifying phenol-containing geothermal water
CN107399871A (en) A kind of Waste Water Treatment of co-oxidation
CN105502858B (en) A kind of processing method of oil-containing heavy metal industrial effluent
CN107381981B (en) Treatment method for removing mineral oil in wastewater
CN105565554A (en) Food waste oil removing treatment method
CN208612477U (en) A kind of regenerating active carbon system for adsorbing biodegradable pollutant saturation
CN107522361B (en) A kind of advanced treatment system removing waste water mineral oil in fluid
CN204588911U (en) A kind of stagewise water treatment recycling equipment
CN107857403B (en) Food and beverage waste water deoiling processing system
CN108423928A (en) A kind of processing system of purified industrial waste water
CN213231883U (en) Device for treating wastewater based on physical adsorption coupling photo-Fenton oxidation technology
CN214327369U (en) Oily wastewater treatment system
CN201447401U (en) Dreg, water and oil segregator
CN112979085A (en) Emulsification type high-oil-content wastewater treatment system and method
CN105330089A (en) Waste water treatment equipment
CN107285548A (en) Cold plasma fusion technology sewage disposal system and method
CN217746416U (en) Odor purification device of small sewage treatment equipment
CN108751607A (en) It is a kind of to utilize wind and solar energy water treatment facilities
CN215049542U (en) Integrated emergency treatment device for landfill leachate
CN105858793B (en) A kind of adsorbing-oxidising three-phase fluid bed reactor for administering industrial wastewater
CN202829791U (en) Apparatus for combination treatment of domestic sewage through air floatation technology and biotechnology
CN112209530A (en) Oily wastewater treatment system
CN105502770A (en) Domestic sewage deoiling system
CN105236667A (en) Closed treatment method for wood-tar processing wastewater

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
TA01 Transfer of patent application right

Effective date of registration: 20200708

Address after: 311400 Qiaotou, Songxi village, Xindeng Town, Fuyang District, Hangzhou City, Zhejiang Province

Applicant after: Hangzhou Fuyang communication plastic factory

Address before: Jinjiang Anhai Town, Fujian province Quanzhou City Road 362261 success No. 1 room 324

Applicant before: Zhu Hui

TA01 Transfer of patent application right
TA01 Transfer of patent application right

Effective date of registration: 20200715

Address after: Room 2602, B-1, Dongyi Financial Plaza, 169 Funan Road, Luyang District, Hefei City, Anhui Province 230000

Applicant after: Anhui Anfeng Environmental Technology Co., Ltd

Address before: 311400 Qiaotou, Songxi village, Xindeng Town, Fuyang District, Hangzhou City, Zhejiang Province

Applicant before: Hangzhou Fuyang communication plastic factory

TA01 Transfer of patent application right
GR01 Patent grant
GR01 Patent grant