CN109293111A - A kind of external source pollution abatement system - Google Patents

A kind of external source pollution abatement system Download PDF

Info

Publication number
CN109293111A
CN109293111A CN201811207209.XA CN201811207209A CN109293111A CN 109293111 A CN109293111 A CN 109293111A CN 201811207209 A CN201811207209 A CN 201811207209A CN 109293111 A CN109293111 A CN 109293111A
Authority
CN
China
Prior art keywords
reaction chamber
external source
abatement system
pollution abatement
source pollution
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
CN201811207209.XA
Other languages
Chinese (zh)
Inventor
蒋遂安
蒋东昇
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.)
Sichuan Andaer Environmental Protection Engineering Co Ltd
Original Assignee
Sichuan Andaer Environmental Protection Engineering 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 Sichuan Andaer Environmental Protection Engineering Co Ltd filed Critical Sichuan Andaer Environmental Protection Engineering Co Ltd
Priority to CN201811207209.XA priority Critical patent/CN109293111A/en
Publication of CN109293111A publication Critical patent/CN109293111A/en
Pending legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F9/00Multistage treatment of water, waste water or sewage
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/001Processes 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
    • C02F1/02Treatment of water, waste water, or sewage by heating
    • C02F1/04Treatment of water, waste water, or sewage by heating by distillation or evaporation
    • C02F1/048Purification of waste water by evaporation
    • 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
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/78Treatment of water, waste water, or sewage by oxidation with ozone
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/16Nitrogen compounds, e.g. ammonia
    • 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
    • C02F2101/32Hydrocarbons, e.g. oil
    • 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

Abstract

The invention discloses a kind of external source pollution abatement system, the external source pollution abatement system includes at least dirty water collecting tank, heat exchanger, steam generator and reaction chamber;The dirty water collecting tank is connected through heat exchanger with the steam generator, and the steam generator is connected with the reaction chamber, and the reaction chamber is also connected with ozone generator, and the reaction chamber is connected through high-pressure pump with the heat transfer medium import of heat exchanger heat exchange layer.By this external source pollution abatement system, the efficient process to carbon source in sewage and nitrogen source pollutant is realized, avoids in traditional wastewater processing method and new sludge or other wastes is led to the problem of using the means such as fermentation processing carbon source and nitrogen source pollutant process.

Description

A kind of external source pollution abatement system
Technical field
The present invention relates to a kind of sewage treatment systems, more particularly to for a kind of external source pollution control of sewage discharge process System.
Background technique
Water is important natural resources, economic resources, social resources and the Ecological basis element of social development, and water is in city township It shuttles and flows in village, for maintaining town ecological function and safety and stability to play a significant role.In Rapid-Urbanization and industry In the process of change, since cities and towns infrastructure seriously lags, Some Cities And Towns river becomes industrial wastewater, sanitary sewage and farmland The main thoroughfare of blowdown is concentrated in water-break, and pollutant discharge amount is big and spatial distribution is concentrated, and river dirt is only than high, self-purification of water energy Power is weak, be easy to cause anoxic and eutrophication, forms black and odorous water.City black and odorous water has become a kind of urban disease, owns Escape by luck almost without one in city.The improvement of China's black and odorous water can trace back to Suzhou River environment comprehensive in 1996 earliest Regulation.
In recent years, black and odorous water is administered gradually by the great attention of local government, and has carried out related practice.Though Right Shanghai, Beijing, Guangzhou, Jiangsu and zhejiang and other places have carried out beneficial exploration and practice in terms of black and odorous water improvement, still It eliminates city black and odorous water comprehensively in China, still suffers from some difficulties and problems.First is that the truth of a matter is unclear, lack The criterion and foundation clearly standardized.Second is that governing measure is single, systematicness is insufficient to restrict black and odorous water improvement effect.Three It is that the coordination system is not perfect, important content of the smelly water body treating of urban black as water harnessing, the quagmire of " Kowloon harness the river water do not control " Not yet break, resultant force of harnessing the river not yet is formed.The smelly water body treating of urban black is related to more administrative service divisions, pollutant emission supervision Management is related to environmental protection department, and sewage outfalls setting and river management are related to water conservancy (water utilities) department, the bases such as sewage network Facilities Construction is related to Zhu Jian department, other further relate to the authorities such as landscape, planning, soil, and management coordination difficulty is big.Fourth is that The unsound internal governance, and black and odorous water has the possibility of rebound.
EIAI black and odorous water original position governing system integrated technology is by the main water for flowing into river, Tang Ku, lake Source and section, Tang Ku, the upper, middle and lower water layer of water body in lake and bed mud carry out comprehensive improvement and restoration of the ecosystem in situ, allow Water environment is radicallyed reform, and the systematization integrated technology of the comprehensive radical cure of heavily contaminated black and odorous water is realized, by external source pollution abatement system (External sewage treatment system), endogenous improvement and repair system (Internal control and Repair system), artificial intelligence system (Artificial intelligence system) and comprehensive energy guarantee system System (Integrated energy security system) is constituted.And sewage and waste water is administered in external source pollution abatement system It is the most important thing therein, and traditional sewage disposal technology is all the route followed American-European countries in the last hundred years and processing Technology, is exactly AB method, A/O method, A/A/O method, CASS method, SBR method etc. among present promote, be also all activated sludge process and The improvement of biochemical method, sludge are the association products of existing sewage treatment.Therefore, it needs at the more environmentally-friendly efficient sewage of one kind Reason system.
Summary of the invention
It is an object of the invention to overcome the deficiencies of the prior art and provide a kind of external source pollution abatement system, the external sources Pollution abatement system includes at least dirty water collecting tank, heat exchanger, steam generator and reaction chamber;The dirty water collecting tank warp Heat exchanger is connected with the steam generator, and the steam generator is connected with the reaction chamber, and the reaction chamber is also connected with There is ozone generator, the reaction chamber is connected through high-pressure pump with the heat transfer medium import of heat exchanger heat exchange layer.
According to a preferred embodiment, the reaction chamber is cylindrical cavity structure, and steam generator is connected to instead Answer the appendix of room deeply to the reaction chamber middle part.
According to a preferred embodiment, the end of the appendix is equipped with spherical jet thrust, sets on the jet thrust There are several air nozzles away from the centre of sphere.
According to a preferred embodiment, be respectively equipped at the top and bottom of the reaction chamber the first intake section and second into Gas portion, first intake section and the second intake section are connected with the ozone generator respectively, first intake section and second Intake section is disc-shaped structure identical with reactor chamber internal diameter;First intake section is towards in the middle part of the reaction chamber Side be equipped with several first gas outlets, second intake section is being equipped with several the towards the side in the middle part of the reaction chamber Two gas outlets.
According to a preferred embodiment, the reaction chamber bottom is equipped with for being connected what tube body was connect with high-pressure pump Exhaust outlet.
According to a preferred embodiment, the heat transfer medium outlet of the heat exchanger heat exchange layer is equipped with gas-liquid separation Device, the gas-liquid separator are connected with water tank and gas collecting box respectively.
According to a preferred embodiment, filter is equipped between the dirty water collecting tank and the heat exchanger.
According to a preferred embodiment, the steam generator is also connected with concentrated solution collecting box.
Compared with the prior art, the advantages of the present invention are as follows: by this external source pollution abatement system, realize in sewage The efficient process of carbon source and nitrogen source pollutant, avoid in traditional wastewater processing method using fermentation etc. means processing carbon source and Nitrogen source pollutant process leads to the problem of new sludge or other wastes.
Detailed description of the invention
Fig. 1 is the structural diagram of the present invention;
Fig. 2 is reaction chamber structure schematic diagram in apparatus of the present invention;
In figure, 101- dirty water collecting tank, 102- filter, 103- heat exchanger, 104- steam generator, 105- reaction Room, 105a- appendix, 105b- jet thrust, the first intake section of 105c-, the first gas outlet 105d-, the second intake section of 105e-, The second gas outlet 105f-, 105g- exhaust outlet, 106- ozone generator, 107- high-pressure pump, 108- gas-liquid separator, 109- water Case, 110- gas collection case, 111- concentrated solution collecting box.
Specific embodiment
Illustrate embodiments of the present invention below by way of specific specific example, those skilled in the art can be by this specification Other advantages and efficacy of the present invention can be easily understood for disclosed content.The present invention can also be by addition different specific Embodiment is embodied or practiced, and the various details in this specification can also not carried on the back based on different viewpoints and application From carrying out various modifications or alterations under spirit of the invention.It should be noted that in the absence of conflict, following embodiment and Feature in embodiment can be combined with each other.
It should be noted that illustrating the basic structure that only the invention is illustrated in a schematic way provided in following embodiment Think, only shown in schema then with related component in the present invention rather than component count, shape and size when according to actual implementation Draw, when actual implementation kenel, quantity and the ratio of each component can arbitrarily change for one kind, and its assembly layout kenel It may also be increasingly complex.
Embodiment:
A kind of external source pollution abatement system, as depicted in figs. 1 and 2.The external source pollution abatement system includes at least sewage Collecting box 101, filter 102, heat exchanger 103, steam generator 104, reaction chamber 105, ozone generator 106, high-pressure pump 107, gas-liquid separator 108, water tank 109, gas collection case 110 and concentrated solution collecting box 111.
Preferably, the dirty water collecting tank 101 is connected through pipeline with the filter 102.The wherein dirty water collecting tank 101 for completing various types of sewage collectings.And the filtering to dirty impurities in water is completed via filter 102.Further Ground is equipped with the primary exclusion device such as sedimentation basin in the dirty water collecting tank 101.The filter 102 can be gravity mistake One of filter, vacuum filter and pressure filter or a variety of combination unit.
Preferably, the filter 102 is connected with the heat exchanger 103.Filter 102 is defeated by the sewage for completing filtering It send to heat exchanger 103 and completes the preliminary the pre-heat treatment of sewage.Further, the heat exchanger 103 is dividing wall type, mixing One of formula or heat storage exchanging apptss.It is completed in heat exchanger 103 to flowing through the heat exchanger by heat medium Sewage in 103 is preheated.Further, the heat medium is liquids and gases Hybrid Heating medium.The mixing adds The temperature of thermal medium is 100-400 DEG C.
Preferably, the heat exchanger 103 is connected through pipeline with the steam generator 104.For realizing it will preheat after Sewage send into steam generator 104 and be evaporated removal of impurities, wherein the impurity gone out mainly includes ammonia, methane and alcohols Equal organic matters.Preferably, the sewage after evaporation removal of impurities is dense saline solution.
Preferably, steam generator 104 is connected with reaction chamber 105 and concentrated solution collecting box 111 respectively through pipeline.Steam hair The impurity of gaseous state is passed through in reaction chamber 105 by raw device 104 through pipeline, and is completed by concentrated solution collecting box 111 to evaporation Treated sewage collecting that is to say the collection completed to dense saline solution.
Preferably, reaction chamber 105 is also connected with ozone generator 106.Ozone generator 106 is through tube body by the ozone of generation It is passed through in reaction chamber 105.It is high temperature of the organic matters such as water, ammonia, methane and alcohols in sewage in steam generator 104 Become the ozone that steam form enters in reaction chamber 105 and reaction chamber 105 under effect and redox reaction occurs, to make ammonia As nitrogen, organic gas becomes carbon dioxide and water, to complete the purified treatment to carbon source in sewage and nitrogen source pollutant.
Preferably, the reaction chamber 105 is cylindrical cavity structure, and steam generator 104 is connected to the defeated of reaction chamber 105 Tracheae 105a is deeply to 105 middle part of reaction chamber, so that being input to impurity gas in reaction chamber 105 through appendix 105a Body is directly in the ozone atmosphere in reaction chamber 105.
Further, the end of appendix 105a is equipped with spherical jet thrust 105b, and the jet thrust 105b is equipped with several Away from the air nozzle of the centre of sphere.By the air nozzle being set on the surface spherical jet thrust 105b, so that entering into appendix 105a Foreign gas in reaction chamber 105 can be rapidly and uniformly distributed in the reaction chamber, to promote foreign gas and ozone Reaction speed, improve reaction chamber 105 handle sewage in carbon source and nitrogen source pollutant rate.
Preferably, the first intake section 105c and the second intake section 105e are respectively equipped at the top and bottom of reaction chamber 105.It is described First intake section 105c and the second intake section 105e are connected with the ozone generator 106 respectively.Ozone gas via first into Gas portion 105c and the second intake section 105e enter in reaction chamber 105.
Further, the first intake section 105c and the second intake section 105e is identical as 105 cavity internal diameter of reaction chamber Disc-shaped structure.The first intake section 105c is being equipped with several first outlets towards the side at 105 middle part of reaction chamber Mouth 105d, the second intake section 105e are being equipped with several second gas outlets towards the side at 105 middle part of reaction chamber 105f.By the structure setting of the first intake section 105c and the second intake section 105e, enable ozone gas quickly and uniform Be distributed in reaction chamber 105, be conducive to promoted chemical reaction velocity, meanwhile, in reaction chamber 105 carry out redox Cheng Zhong, ozone air inflow is much larger than the carbon source of the offer of steam generator 104 and the air inflow of nitrogen source mixed vapour, thus into one Step guarantees that mixed vapour is thorough by reaction.
Meanwhile by the setting of steam generator 104 in external source pollution abatement system, realizes and pollute nitrogen source in sewage The evaporation of object and carbon source pollutant is gasified, and the ozone reaction with the enrichment in reaction chamber 105 in a gaseous form.By will be dirty The gasification of nitrogen source pollutant and organic pollutant in water is converted into gaseous state by liquid to realize pollutant, increases nitrogen The surface area of source pollutants and organic pollutant, thus increase nitrogen source pollutant and organic pollutant in reaction chamber 105 with The contact area of ozone.It is, by reacting between gas and gas, to increase reaction chamber 105 and imitated to the oxidation of mixed vapour Rate.And by the evaporation of steam generator 104, so that the mixed gas evaporated into reactor 106 is all high temperature Gas, so that redox reaction speed in reaction chamber 105 is further improved, to improve reaction chamber 105 to sewage Purification speed.
Preferably, the reaction chamber 105 is connected through high-pressure pump 107 with the heat transfer medium import of 103 heat exchange layer of heat exchanger. Further, 105 bottom of reaction chamber is equipped with the exhaust outlet 105g connecting for the tube body that is connected with high-pressure pump 107.Reacted room Steam after 105 reactions mainly contains carbon dioxide and nitrogen, and being almost higher than 97% is all vapor, by the mixing after reaction Steam is sent into heat exchanger 103 through high-pressure pump 106 and is used as heat source, recycles heat (mainly steam condensation heat), vapor condensation At liquid water, carbon dioxide and nitrogen are still gas, separate through gas-liquid separator 108 and are sent into water tank 109 and gas collecting box 110.The water tank is used to complete the recycling or outlet of condensed water.The gas collection case 110 is for completing gas medium Recycling or direct outlet.
By this external source pollution abatement system, the efficient process to carbon source in sewage and nitrogen source pollutant is realized, is avoided New sludge or other is generated using the means such as fermentation processing carbon source and nitrogen source pollutant process in traditional wastewater processing method The problem of waste.
A specific embodiment of the invention above described embodiment only expresses, the description thereof is more specific and detailed, but simultaneously Limitations on the scope of the patent of the present invention therefore cannot be interpreted as.It should be pointed out that for those of ordinary skill in the art For, without departing from the inventive concept of the premise, various modifications and improvements can be made, these belong to of the invention Protection scope.

Claims (8)

1. a kind of external source pollution abatement system, which is characterized in that the external source pollution abatement system includes at least dirty water collecting tank (101), heat exchanger (103), steam generator (104) and reaction chamber (105);
The dirty water collecting tank (101) is connected through heat exchanger (103) with the steam generator (104), the steam generation Device (104) is connected with the reaction chamber (105), and the reaction chamber (105) is also connected with ozone generator (106), the reaction Room (105) is connected through high-pressure pump (107) with the heat transfer medium import of heat exchanger (103) heat exchange layer.
2. external source pollution abatement system as described in claim 1, which is characterized in that the reaction chamber (105) is cylindric chamber Body structure, the appendix (105a) that steam generator (104) is connected to reaction chamber (105) go deep into the reaction chamber (105) Portion.
3. external source pollution abatement system as claimed in claim 2, which is characterized in that the end of the appendix (105a) is equipped with Spherical jet thrust (105b), the jet thrust (105b) are equipped with several air nozzles away from the centre of sphere.
4. external source pollution abatement system as claimed in claim 3, which is characterized in that at the top and bottom of the reaction chamber (105) It is respectively equipped with the first intake section (105c) and the second intake section (105e), first intake section (105c) and the second intake section (105e) is connected with the ozone generator respectively, and first intake section (105c) and the second intake section (105e) are and react The identical disc-shaped structure of room (105) cavity internal diameter;
First intake section (105c) is being equipped with several first gas outlets towards the side in the middle part of the reaction chamber (105) (105d), second intake section (105e) are being equipped with several second gas outlets towards the side in the middle part of the reaction chamber (105) (105f)。
5. external source pollution abatement system as described in claim 1, which is characterized in that reaction chamber (105) bottom, which is equipped with, to be used In the exhaust outlet (105g) that the tube body that is connected with high-pressure pump (107) is connect.
6. the external source pollution abatement system as described in one of claim 1 to 5, which is characterized in that the heat exchanger (103) is changed The heat transfer medium outlet of thermosphere be equipped with gas-liquid separator (108), the gas-liquid separator respectively with water tank (109) and gas collection Case (110) is connected.
7. external source pollution abatement system as claimed in claim 6, which is characterized in that the dirty water collecting tank (101) with it is described Filter (102) are equipped between heat exchanger (103).
8. external source pollution abatement system as claimed in claim 7, which is characterized in that the steam generator (104) also with it is dense Solution collecting box (111) is connected.
CN201811207209.XA 2018-10-17 2018-10-17 A kind of external source pollution abatement system Pending CN109293111A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201811207209.XA CN109293111A (en) 2018-10-17 2018-10-17 A kind of external source pollution abatement system

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201811207209.XA CN109293111A (en) 2018-10-17 2018-10-17 A kind of external source pollution abatement system

Publications (1)

Publication Number Publication Date
CN109293111A true CN109293111A (en) 2019-02-01

Family

ID=65162925

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201811207209.XA Pending CN109293111A (en) 2018-10-17 2018-10-17 A kind of external source pollution abatement system

Country Status (1)

Country Link
CN (1) CN109293111A (en)

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20070231224A1 (en) * 2006-03-29 2007-10-04 Horng Jiang Reaction furnace utilizing high-temp steam and recirculated heat source to separate mercury and crack dioxin and organic substances contained in waste
CN103721563A (en) * 2013-12-18 2014-04-16 浙江省环境保护科学设计研究院 Device and method for treating organic waste gas by catalysis and ozonation
CN204973527U (en) * 2015-07-30 2016-01-20 浙江飞龙管业有限公司 Exhaust treatment device of energy saving
CN106178882A (en) * 2016-09-09 2016-12-07 成都九十度工业产品设计有限公司 Ozone and the liquid collector of waste gas mixing reactor
CN108217790A (en) * 2018-01-16 2018-06-29 邹万清 A kind of municipal wastewater governing system

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20070231224A1 (en) * 2006-03-29 2007-10-04 Horng Jiang Reaction furnace utilizing high-temp steam and recirculated heat source to separate mercury and crack dioxin and organic substances contained in waste
CN103721563A (en) * 2013-12-18 2014-04-16 浙江省环境保护科学设计研究院 Device and method for treating organic waste gas by catalysis and ozonation
CN204973527U (en) * 2015-07-30 2016-01-20 浙江飞龙管业有限公司 Exhaust treatment device of energy saving
CN106178882A (en) * 2016-09-09 2016-12-07 成都九十度工业产品设计有限公司 Ozone and the liquid collector of waste gas mixing reactor
CN108217790A (en) * 2018-01-16 2018-06-29 邹万清 A kind of municipal wastewater governing system

Similar Documents

Publication Publication Date Title
CN105776706B (en) A kind of device and method of flue multistage evaporation processing desulfurization wastewater
CN103611377A (en) Gas purification pretreatment method and device
CN102351361B (en) Device and technology capable of combining high-salt content oil field sewage treatment and viscous oil recovery
CN108238706A (en) Oily sludge substep pyrolysis treatment systems and technique
CN203549850U (en) Organic waste gas comprehensive disposal system
CN205443212U (en) Garbage pyrolytic gasification flue gas processing system
CN111001277A (en) Hydrothermal or pyrohydrolysis tail gas resource utilization system and method
CN204661619U (en) The device that a kind of vertical high-temperature cracking static bed coal gasification raw gas is coal-tar middle oil
CN109293111A (en) A kind of external source pollution abatement system
ITCR20100004A1 (en) PLANT FOR THE TREATMENT OF BIOLOGICAL SLUDGE WITH RECOVERY OF RAW MATERIALS SECOND AND ENERGY
CN111517398A (en) Zero discharge system of flue gas desulfurization waste water
CN206142984U (en) System for recycle landfill leachate ammonia nitrogen
CN213506535U (en) Thermal power plant and municipal sewage treatment plant pollutant coprocessing's circular economy system
CN102795687B (en) Wastewater zero discharging evaporation system and process
CN205687755U (en) A kind of unpowered continuous anaerobism advanced treatment apparatus of domestic sewage of villages and small towns
CN205773920U (en) The biological treatment system of heat-engine plant desulfurized waste water
CN214032107U (en) Garbage transfer station leachate integrated treatment equipment
CN205347174U (en) Utilize plus sludge drying of living beings and processing apparatus that carbomorphism combined together
CN104773891A (en) Novel oil-refining wastewater comprehensive processing system and method
CN106277533A (en) A kind of system and method processing pulverized coal pyrolysis sewage
CN104108760B (en) A kind for the treatment of unit of oily(waste)water and treatment process thereof
CN108726769A (en) A kind of advanced treatment and reclamation method of flue gas desulfurization liquid
CN203959860U (en) A kind of phenol water disposal equipment
CN206553374U (en) Organic sludge thermal cracking gasification electricity generation system
CN105419827A (en) Oil sediment pyrolisis system of plasma double-pipe heat exchanger

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