CN106984161A - A kind of marine exhaust pollutant and ballast water integrated conduct method and device - Google Patents

A kind of marine exhaust pollutant and ballast water integrated conduct method and device Download PDF

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Publication number
CN106984161A
CN106984161A CN201710423188.4A CN201710423188A CN106984161A CN 106984161 A CN106984161 A CN 106984161A CN 201710423188 A CN201710423188 A CN 201710423188A CN 106984161 A CN106984161 A CN 106984161A
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water tank
cleaning solution
water
water pump
tank
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CN106984161B (en
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韩志涛
潘新祥
韩志伟
杨少龙
刘博俊
赵东升
郑德康
宋永惠
夏鹏飞
孙可朝
高孟秋
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Dalian Maritime University
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Dalian Maritime University
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/74General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/77Liquid phase processes
    • B01D53/78Liquid phase processes with gas-liquid contact
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/46Removing components of defined structure
    • B01D53/48Sulfur compounds
    • B01D53/50Sulfur oxides
    • B01D53/501Sulfur oxides by treating the gases with a solution or a suspension of an alkali or earth-alkali or ammonium compound
    • B01D53/502Sulfur oxides by treating the gases with a solution or a suspension of an alkali or earth-alkali or ammonium compound characterised by a specific solution or suspension
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/46Removing components of defined structure
    • B01D53/60Simultaneously removing sulfur oxides and nitrogen oxides
    • 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
    • C02F1/50Treatment of water, waste water, or sewage by addition or application of a germicide or by oligodynamic treatment
    • 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
    • C02F1/76Treatment of water, waste water, or sewage by oxidation with halogens or compounds of halogens
    • C02F1/766Treatment of water, waste water, or sewage by oxidation with halogens or compounds of halogens by means of halogens other than chlorine or of halogenated compounds containing halogen other than chlorine
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2251/00Reactants
    • B01D2251/10Oxidants
    • B01D2251/108Halogens or halogen compounds
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2251/00Reactants
    • B01D2251/30Alkali metal compounds
    • B01D2251/304Alkali metal compounds of sodium
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2251/00Reactants
    • B01D2251/40Alkaline earth metal or magnesium compounds
    • B01D2251/402Alkaline earth metal or magnesium compounds of magnesium
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2251/00Reactants
    • B01D2251/60Inorganic bases or salts
    • B01D2251/604Hydroxides
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2258/00Sources of waste gases
    • B01D2258/01Engine exhaust gases
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2258/00Sources of waste gases
    • B01D2258/01Engine exhaust gases
    • B01D2258/012Diesel engines and lean burn gasoline engines
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02TCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO TRANSPORTATION
    • Y02T10/00Road transport of goods or passengers
    • Y02T10/10Internal combustion engine [ICE] based vehicles
    • Y02T10/12Improving ICE efficiencies

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  • Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (AREA)
  • Environmental & Geological Engineering (AREA)
  • Analytical Chemistry (AREA)
  • Health & Medical Sciences (AREA)
  • Biomedical Technology (AREA)
  • General Chemical & Material Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Water Supply & Treatment (AREA)
  • Hydrology & Water Resources (AREA)
  • Organic Chemistry (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Treating Waste Gases (AREA)
  • Exhaust Gas After Treatment (AREA)

Abstract

The invention discloses a kind of marine exhaust pollutant and ballast water integrated conduct method and device, described device includes water pump I, oxidizer containing chlorine cabinet, alkali lye cabinet, fresh water tank, water pump VI, seawater pipe, hydrocyclone, sludge tank, water pump V, main washing lotion tube, water pump II, water tank, waste liquid storage cabinet, ballast tank, water pump III, main jet shower pipe, water pump IV, agitator, scrubbing tower, cooler, waste liquid discharge pipe, stop valve I, stop valve II, stop valve III, triple valve and stop valve IV.Marine exhaust pollutant disposal system proposed by the invention uses wet scrubbing technology, is divided into independent desulfurization, two kinds of different working modes of simultaneous SO_2 and NO removal, wherein independent desulphation mode can take two kinds of different wet scrubbing modes of enclosed and open type again.According to different emission requests of the trading limit to exhaust emission, free switching mode of operation and mode, operation are easy to operate, substantially increase the integrated level, reliability and flexibility of system.

Description

A kind of marine exhaust pollutant and ballast water integrated conduct method and device
Technical field
Prevention and control of air pollution and ballast water treatment technical field are caused the invention belongs to ship, and in particular to a kind of ship gives up Gas pollutant and ballast water integrated conduct method and device.
Background technology
In recent years, global Seaborne trade cause is continued to develop, and is transported using large-sized low-speed diesel engine as the ocean of power set The average tonnage of defeated ship is in increase, and quantity is declined slightly.In order to reduce cost of transportation, marine diesel typically uses oil Residue oil inferior in refining process is fuel, and its sulfur content is high, viscosity is big, carbon residue is higher, contains in the waste gas after burning There is substantial amounts of nitrogen oxides (NOx), oxysulfide (SOx), the multiple pollutant such as particulate matter (PM), to human health and big compression ring Border causes adverse effect.
In order to control the discharge of marine diesel exhaust emission, in recent years, domestic and international researcher is in marine diesel A large amount of R&D works are carried out in terms of exhaust gas treatment technology, it is proposed that many marine exhaust Pollutant Control Technologys.Such as:The patent No. 201620788920.9《A kind of selective-catalytic-reduction denitrified system》, denitration, but this method are carried out to flue gas using SCR method There are problems that big plant bulk, the escaping of ammonia, catalyst are easy, there is certain be stranded using upper in marine exhaust denitration It is difficult;The patent No. 201510721307.5《A kind of SNCR-SCR flue-gas denitration process》, propose the inexpensive feature of SNCR techniques Organically combined with the high denitration efficiency of SCR techniques, improve denitration efficiency, and escape ammonia amount is small, but this method is still suffered from and accounted for Big, the weak point such as investment operation cost height with space;The patent No. 201310116629.8《Sodium alkali chemical absorbing-non-thermal is put Electric simultaneous SO_2 and NO removal system》, by the way that non-thermal plasma electric discharge pre-oxidation is combined with soda absorption techniques, to reach ship Waste gas simultaneous SO_2 and NO removal purpose, but this method is present that plasma energy consumption is higher, the more low obvious problem of denitration efficiency.
At present, International Maritime Organization (IMO) is for SO in marine exhaustxAnd NOxEmission control require it is more and more stricter, Tailor MARPOL pacts supplemental provisions VI.How according to different navigation areas, the specific requirement of different operating modes, using difference Desulphurization denitration mode of operation and mode, how while emission request is met, realize the reduction of operation cost, and system Integrated level, reliability and the raising of flexibility, these problems turn into current Shipping industry urgent problem to be solved.Mesh Preceding existing marine exhaust wet scrubbing technology can have been realized to the SO in flue gasxHigh-efficiency desulfurization, such as soda seawater method, magnesium-based The wet scrubbing post-processing technology such as seawater method, they, as additive, are imitated using soda or magnesium hydroxide with good desulfurization Really, but these marine exhaust wet scrubbing technologies denitration effect it is unobvious.There is patent to propose to prepare strong oxygen using electrolytic seawater The property changed solution and strong alkali solution, while realizing to NO in marine exhaustx、SOx, the multiple pollutant such as particulate matter wet scrubbing Processing, but this method needs the higher electric energy of consumption, limits the feasibility of correlation technique.Also patent proposes using waste gas again The technology of circulation, that is, first pass through wet scrubbing mode and remove SOx, then make part handle after waste gas mixed with fresh air it is laggard Enter diesel engine, NO is reduced by the method for reducing burning chamber of diesel engine internal-combustion temperaturexGrowing amount, but the desulfurization effect of the technology Fruit depends on bypass exhaust amount, and can reduce the thermal efficiency of diesel engine, causes the increase of HC and CO discharge capacitys.
The content of the invention
Transport by sea ship is given up in the different navigating areas such as high sea, coastal waters and emission control area to meet MARPOL pacts Gas pollutant emission requirement, the problem of existing for above-mentioned technology, the present invention proposes a kind of marine exhaust pollutant and ballast water Integrated conduct method.This method is a kind of new wet scrubbing technology, is divided into independent desulfurization, two kinds of differences of simultaneous SO_2 and NO removal Mode of operation.Wherein independent desulphation mode can take two kinds of different wet scrubbing modes of enclosed and open type again.The technology can be real Now to NO in marine exhaustx、SOx, the multiple pollutant such as particulate matter efficient removal, while containing oxychloride using what is stored with ship The harmless treatment to ballast water can be achieved in agent.Based on this method, devise a set of marine exhaust pollutant and ballast water is integrated Processing unit.
The technological means that the present invention is used is as follows:
A kind of marine exhaust pollutant and ballast water integrated conduct method, with following steps:
S1, appropriate alkali lye, oxidizer containing chlorine, the aqueous solution is delivered in water tank by water pump respectively, after mixing To cleaning solution;
When carrying out desulphurization denitration processing to marine exhaust simultaneously, the ratio that the oxidizer containing chlorine accounts for the cleaning solution is big In 0;
When only carrying out desulfurization process to marine exhaust, the ratio that the oxidizer containing chlorine accounts for the cleaning solution is 0;
S2, the cleaning solution enter to scrubbing tower by water pump from scrubbing tower top inlet, then pass through the washing Showering washing device inside tower carries out atomizing spray from top to down, and marine exhaust to be clean is from scrubbing tower sidewall bottom air inlet Mouth enters scrubbing tower, is reacted with atomizing spray cleaning solution by inversely contacting, so that the processing to flue gas is realized, through washing Washing the waste gas after tower purification can be directly discharged in air through simple process;
Only marine exhaust is entered when carrying out desulphurization denitration processing to marine exhaust simultaneously or when using enclosed mode of washing Purify after the cleaning solution after waste gas is handled through cooler cooling and returned in water tank during row desulfurization process, in scrubbing tower, the water tank In cleaning solution remove solid impurity therein through hydrocyclone, the solution after processing is returned into water tank, and is divided The solid impurity separated out is disposed in sludge tank;
When only carrying out desulfurization process to marine exhaust using open type mode of washing, the washing in scrubbing tower after purification waste gas Liquid direct discharge into sea after the processing such as be simply aerated, remove slag, dilute;
S3, according to ballast water capacity in ballast tank, take appropriate oxidizer containing chlorine, add it in ballast tank, profit Kill bacterium, algae and the other microorganisms in ballast water with the strong oxidizing property of oxidizer containing chlorine, finally by selfdecomposition or Follow-up simple process eliminates oxidizer containing chlorine excessive in ballast water.
During handling marine exhaust, because the water in the water tank can be because of evaporation, except miscellaneous operation etc. Loss, it is necessary to persistently supplement the aqueous solution in use, and the liquid level of cleaning solution is in normal level in the holding water tank.
The step S2 is carried out to the particulate matter in marine exhaust simultaneously during wet scrubbing is carried out to marine exhaust Removing.
The alkali lye refers to include one kind or number in sodium hydroxide, sodium carbonate, sodium acid carbonate, magnesium hydroxide, magnesium carbonate Plant the aqueous solution of alkali compounds;
The oxidizer containing chlorine refers to include in sodium hypochlorite, sodium chlorite, sodium chlorate, sodium perchlorate, chlorine dioxide The aqueous solution of one or several kinds of chlorine-containing compounds;
The aqueous solution refers to fresh water or seawater.
The invention also discloses a kind of marine exhaust pollutant and ballast water Integrated Processing Unit, it is characterised in that:Including Water pump I, oxidizer containing chlorine cabinet, alkali lye cabinet, fresh water tank, water pump VI, seawater pipe, hydrocyclone, sludge tank, water pump V, master washes Wash liquid pipe, water pump II, water tank, waste liquid storage cabinet, ballast tank, water pump III, main jet shower pipe, water pump IV, agitator, scrubbing tower, Cooler, waste liquid discharge pipe, stop valve I, stop valve II, stop valve III, triple valve and stop valve IV;
The oxidizer containing chlorine cabinet is connected by the water pump I with the ballast tank;
The oxidizer containing chlorine cabinet is connected by the stop valve I with the main washing lotion tube;
The alkali lye cabinet is connected by the stop valve II with the main washing lotion tube;
The fresh water tank is connected by the stop valve III with the main washing lotion tube;
The main washing lotion tube is connected by the water pump II with the water tank cleaning solution import I at the top of the water tank;
Water tank cleaning solution outlet I at the top of the water tank is connected by the water pump III with the main jet shower pipe;
The scrubbing tower inside cavity is provided with Multi-layer sprinkling device, the inlet of the spray equipment and the main jet shower pipe Branch pipeline connection;
The scrubbing tower sidewall bottom is provided with exhaust gas inlet to be clean, and top is provided with waste gas outlet after purification, and bottom is provided with Cleaning solution after waste gas is purified to export;
The cooler cleaning solution import that cleaning solution outlet passes through the triple valve and the cooler after the purification waste gas Connection;
Cleaning solution outlet is connected by the triple valve with the waste liquid discharge pipe after the purification waste gas;The waste liquid row Outlet pipe can be by direct discharge into sea after cleaning solution simple process after purification waste gas;
The cooler be provided with refrigerant flow conduit, the cooler cooler cleaning solution outlet by the water pump IV with The water tank cleaning solution import II on the water tank top is connected;
The water tank inner bottom, which is provided with, makes the mixed uniformly agitator of cleaning solution in the water tank;
The water tank cleaning solution outlet II of the water tank side wall bottom passes through the water pump V and hydrocyclone side wall Connection;
The water tank cleaning solution of the outlet of hydrocyclone cleaning solution and the water tank top on the hydrocyclone top enters Mouth III is connected;
The solid impurity outlet of the hydrocyclone bottom is connected with the sludge tank;
The water tank cleaning solution outlet III of the water tank bottom is connected by the stop valve IV with the waste liquid storage cabinet;
The seawater pipe is connected by the water pump VI with the water tank cleaning solution import IV on the water tank top.
Compared with other marine exhaust treatment technologies, the present invention has advantages below:
1st, marine exhaust pollutant disposal system proposed by the invention uses wet scrubbing technology, is divided into individually de- Sulphur, two kinds of different working modes of simultaneous SO_2 and NO removal, wherein independent desulphation mode can take two kinds of enclosed and open type different again Wet scrubbing mode.According to different emission requests of the trading limit to exhaust emission, free switching mode of operation and side Formula, operation is easy to operate, substantially increases the integrated level, reliability and flexibility of system;
2nd, the wet scrubbing liquid in the present invention uses alkali lye, oxidizer containing chlorine respectively as desulfurizing agent and denitration oxidant, According to different navigation areas, the specific requirement of different operating modes, appropriate cleaning solution is chosen, marine exhaust integrated treatment is improved Economy, enhances the practicality of device;
3rd, the present invention using the strong oxidizing property of oxidizer containing chlorine stored with ship to the bacterium in ballast water, algae and its Its microorganism is handled, and can save the larger segregated ballast processing system of expensive, space-consuming, so as to improve ship The economy of operation.
The present invention can extensively be pushed away in ship prevention and control of air pollution and ballast water comprehensive treatment technique field for the foregoing reasons Extensively.
Brief description of the drawings
In order to illustrate more clearly about the embodiment of the present invention or technical scheme of the prior art, below will be to embodiment or existing There is the accompanying drawing used required in technology description to do simply to introduce, it should be apparent that, drawings in the following description are this hairs Some bright embodiments, for those of ordinary skill in the art, without having to pay creative labor, can be with Other accompanying drawings are obtained according to these accompanying drawings.
Fig. 1 is a kind of knot of marine exhaust pollutant and ballast water Integrated Processing Unit in embodiment of the invention Structure schematic diagram.
Embodiment
To make the purpose, technical scheme and advantage of the embodiment of the present invention clearer, below in conjunction with the embodiment of the present invention In accompanying drawing, the technical scheme in the embodiment of the present invention is clearly and completely described, it is clear that described embodiment is A part of embodiment of the present invention, rather than whole embodiments.Based on the embodiment in the present invention, those of ordinary skill in the art The every other embodiment obtained under the premise of creative work is not made, belongs to the scope of protection of the invention.
Embodiment 1
A kind of marine exhaust pollutant and ballast water integrated conduct method, when ship's navigation is in NOxWhen in emission control area, Need to carry out desulphurization denitration processing to marine exhaust simultaneously, with following steps:
S1, appropriate alkali lye, oxidizer containing chlorine, the aqueous solution is delivered in water tank by water pump respectively, after mixing To cleaning solution;
The alkali lye refers to include one kind or number in sodium hydroxide, sodium carbonate, sodium acid carbonate, magnesium hydroxide, magnesium carbonate Plant the aqueous solution of alkali compounds;
The oxidizer containing chlorine refers to include in sodium hypochlorite, sodium chlorite, sodium chlorate, sodium perchlorate, chlorine dioxide The aqueous solution of one or several kinds of chlorine-containing compounds;
The aqueous solution refers to fresh water or seawater.
S2, the cleaning solution enter to scrubbing tower by water pump from scrubbing tower top inlet, then pass through the washing Showering washing device inside tower carries out atomizing spray from top to down, and marine exhaust to be clean is from scrubbing tower sidewall bottom air inlet Mouth enters scrubbing tower, is reacted with atomizing spray cleaning solution by inversely contacting, so that the processing to flue gas is realized, through washing Washing the waste gas after tower purification can be directly discharged in air through simple process;The cleaning solution after waste gas is purified in scrubbing tower through cold But returned to after device cooling processing in water tank, the cleaning solution in the water tank removes solid impurity therein, place through hydrocyclone Solution after reason is returned into water tank, and the solid impurity isolated is disposed in sludge tank;
Main desulfurizing agent in the cleaning solution is alkali lye, and in scrubbing tower, desulfurizing agent is inversely contacted with waste gas to be clean And react, the chemical reaction being related to is as follows:
SO2(g)→SO2(l);
SO2(l)+2OH-(l)→SO3 2-(l)+H2O(l);
SO3(l)+2OH-(l)→SO4 2-(l)+H2O(l);
When the oxidizer containing chlorine is sodium hypochlorite, the main component of its effective chlorine is Cl2、HClO、ClO-, in washing In tower, inversely contact and react with waste gas to be clean, be related to desulfurization and denitrification reaction as follows:
SO2(g)→SO2(l);
SO2(l)+H2O(l)→H+(l)+HSO3 -(l);
SO2(l)+3OH-(l)→H2O(l)+SO3 2-(l);
HClO(l)+HSO3 -(l)→SO4 2-(l)+2H+(l)+Cl-(l);
ClO-(l)+HSO3 -(l)→SO4 2-(l)+H+(l)+Cl-(l);
NO(g)→NO(l);
When the oxidizer containing chlorine is sodium chlorite, the main component of its effective chlorine is ClO2 -、ClO2, the desulfurization being related to Denitration reaction is as follows:
SO2(g)→SO2(l);
SO2(l)+H2O(l)→H+(l)+HSO3 -(l);
SO2(l)+3OH-(l)→H2O(l)+SO3 2-(l);
ClO2 -(l)+2HSO3 -(l)→2SO4 2-(l)+2H+(l)+Cl-(l);
ClO2 -(l)+2SO3 2-(l)+2OH-→2SO4 2-(l)+2H2O(l)+Cl-(l);
NO(g)→NO(l);
2NO(l)+ClO2 -(l)→Cl-(l)+2NO2(l);
NO(l)+NO2+H2O(l)→2HNO2(l);
4NO(l)+ClO2 -(l)+4OH-(l)→4NO3 -(l)+Cl-(l)+2H2O(l);
4NO(l)+3ClO2 -(l)+2H2O(l)→4HNO3(l)+3Cl-(l);
5NO(l)+3ClO2(l)+4H2O(l)→5HNO3(l)+3HCl(l);
When the oxidizer containing chlorine is sodium chlorate, the main component of its effective chlorine is ClO3 -, the desulphurization denitration being related to is anti- Should be as follows:
SO2(g)→SO2(l);
SO2(l)+H2O(l)→H+(l)+HSO3 -(l);
SO2(l)+3OH-(l)→H2O(l)+SO3 2-(l);
2ClO3 -(l)+2HSO3 -(l)→2SO4 2-(l)+2H+(l)+Cl-(l);
ClO3 -(l)+SO3 2-(l)+2OH-(l)→2SO4 2-(l)+Cl-(l)+2H2O(l);
NO(g)→NO(l);
3NO(l)+ClO3 -(l)→3NO2(l)+Cl-(l);
3NO2(l)+ClO3 -(l)+OH-→3NO3 -(l)+Cl-(l)+H2O(l);
2NO(l)+ClO3 -(l)+2OH-→2NO3 -(l)+Cl-(l)+H2O(l);
S3, according to ballast water capacity in ballast tank, take appropriate oxidizer containing chlorine, add it in ballast tank, profit Kill bacterium, algae and the other microorganisms in ballast water with the strong oxidizing property of oxidizer containing chlorine, finally by selfdecomposition or Follow-up simple process eliminates oxidizer containing chlorine excessive in ballast water.
During handling marine exhaust, because the water in the water tank can be because of evaporation, except miscellaneous operation etc. Loss, it is necessary to persistently supplement the aqueous solution in use, and the liquid level of cleaning solution is in normal level in the holding water tank.
The step S2 is carried out to the particulate matter in marine exhaust simultaneously during wet scrubbing is carried out to marine exhaust Removing.
Embodiment 2
A kind of marine exhaust pollutant and ballast water integrated conduct method, when ship is in non-NOxWhen emission control area is navigated by water, Desulfurization process is carried out to marine exhaust using independent desulfurization mode of operation, independent desulphation mode is divided into enclosed and open type two again Kind of mode of washing, enclosed mode of washing is comprised the following steps that:
S1, appropriate alkali lye, the aqueous solution is delivered in water tank by water pump respectively, cleaning solution is obtained after mixing;
The alkali lye refers to include one kind or number in sodium hydroxide, sodium carbonate, sodium acid carbonate, magnesium hydroxide, magnesium carbonate Plant the aqueous solution of alkali compounds;
The aqueous solution refers to fresh water or seawater.
S2, the cleaning solution enter to scrubbing tower by water pump from scrubbing tower top inlet, then pass through the washing Showering washing device inside tower carries out atomizing spray from top to down, and marine exhaust to be clean is from scrubbing tower sidewall bottom air inlet Mouth enters scrubbing tower, is reacted with atomizing spray cleaning solution by inversely contacting, so that the processing to flue gas is realized, through washing Washing the waste gas after tower purification can be directly discharged in air through simple process;The cleaning solution after waste gas is purified in scrubbing tower through cold But returned to after device cooling processing in water tank, the chemical reaction that the process is related to is as follows:
SO2(g)→SO2(l);
SO2(l)+H2O(l)→H+(l)+HSO3 -(l);
SO2(l)+3OH-(l)→H2O(l)+SO3 2-(l);
Cleaning solution in the water tank removes solid impurity therein through hydrocyclone, and the solution after processing is returned again It is back in water tank, and the solid impurity isolated is disposed in sludge tank;
S3, according to ballast water capacity in ballast tank, take appropriate oxidizer containing chlorine, add it in ballast tank, profit Kill bacterium, algae and the other microorganisms in ballast water with the strong oxidizing property of oxidizer containing chlorine, finally by selfdecomposition or Follow-up simple process eliminates oxidizer containing chlorine excessive in ballast water.
The oxidizer containing chlorine refers to include in sodium hypochlorite, sodium chlorite, sodium chlorate, sodium perchlorate, chlorine dioxide The aqueous solution of one or several kinds of chlorine-containing compounds;
During handling marine exhaust, because the water in the water tank can be because of evaporation, except miscellaneous operation etc. Loss, it is necessary to persistently supplement the aqueous solution in use, and the liquid level of cleaning solution is in normal level in the holding water tank.
The step S2 is carried out to the particulate matter in marine exhaust simultaneously during wet scrubbing is carried out to marine exhaust Removing.
Embodiment 3
A kind of marine exhaust pollutant and ballast water integrated conduct method, when ship is in non-NOxWhen emission control area is navigated by water, Desulfurization process is carried out to marine exhaust using independent desulfurization mode of operation, independent desulphation mode is divided into enclosed and open type two again Kind of mode of washing, open type mode of washing is comprised the following steps that:
S1, appropriate alkali lye, the aqueous solution is delivered in water tank by water pump respectively, cleaning solution is obtained after mixing;
The alkali lye refers to include one kind or number in sodium hydroxide, sodium carbonate, sodium acid carbonate, magnesium hydroxide, magnesium carbonate Plant the aqueous solution of alkali compounds;
The aqueous solution refers to fresh water or seawater.
S2, the cleaning solution enter to scrubbing tower by water pump from scrubbing tower top inlet, then pass through the washing Showering washing device inside tower carries out atomizing spray from top to down, and marine exhaust to be clean is from scrubbing tower sidewall bottom air inlet Mouth enters scrubbing tower, is reacted with atomizing spray cleaning solution by inversely contacting, so that the processing to flue gas is realized, through washing Washing the waste gas after tower purification can be directly discharged in air through simple process;The cleaning solution after waste gas is purified in scrubbing tower to pass through Directly discharge into sea is simply aerated, removed slag, diluting etc. after processing;
S3, according to ballast water capacity in ballast tank, take appropriate oxidizer containing chlorine, add it in ballast tank, profit Kill bacterium, algae and the other microorganisms in ballast water with the strong oxidizing property of oxidizer containing chlorine, finally by selfdecomposition or Follow-up simple process eliminates oxidizer containing chlorine excessive in ballast water;
The oxidizer containing chlorine refers to include in sodium hypochlorite, sodium chlorite, sodium chlorate, sodium perchlorate, chlorine dioxide The aqueous solution of one or several kinds of chlorine-containing compounds.
During handling marine exhaust, because the water in the water tank can be because of evaporation, except miscellaneous operation etc. Loss, it is necessary to persistently supplement the aqueous solution in use, and the liquid level of cleaning solution is in normal level in the holding water tank.
The step S2 is carried out to the particulate matter in marine exhaust simultaneously during wet scrubbing is carried out to marine exhaust Removing.
Embodiment 4
As shown in figure 1, a kind of marine exhaust pollutant and ballast water Integrated Processing Unit, including water pump I 1, containing oxychloride Agent cabinet 2, alkali lye cabinet 3, fresh water tank 4, water pump VI 5, seawater pipe 6, hydrocyclone 7, sludge tank 8, water pump V 9, main washing lotion tube 10, water pump II 11, water tank 12, waste liquid storage cabinet 13, ballast tank 14, water pump III 15, main jet shower pipe 16, water pump IV 17, stirring Device 18, scrubbing tower 19, cooler 20 and waste liquid discharge pipe 21, stop valve I 22, stop valve II 23, stop valve III 24, triple valve 25 With stop valve IV 26;
The oxidizer containing chlorine cabinet 2 is connected by the water pump I 1 with the ballast tank 14;
The oxidizer containing chlorine cabinet 2 is connected by the stop valve I 22 with the main washing lotion tube 10;
The alkali lye cabinet 3 is connected by the stop valve II 23 with the main washing lotion tube 10;
The fresh water tank 4 is connected by the stop valve III 24 with the main washing lotion tube 10;
The main washing lotion tube 10 is connected by the water pump II 11 and the water tank cleaning solution import I at the top of water tank 12 It is logical;
The water tank cleaning solution outlet I at the top of water tank 12 is connected by the water pump III 15 with the main jet shower pipe 16;
The inside cavity of scrubbing tower 19 is provided with Multi-layer sprinkling device, and the inlet of the spray equipment drenches with the main jet The branch pipeline connection of pipe 16;
The sidewall bottom of scrubbing tower 19 is provided with exhaust gas inlet to be clean, and top is provided with waste gas outlet after purification, and bottom is set There is cleaning solution after purification waste gas to export;
The cooler cleaning solution that cleaning solution outlet passes through the triple valve 25 and the cooler 20 after the purification waste gas Inlet communication;
Cleaning solution outlet is connected by the triple valve 25 with the waste liquid discharge pipe 21 after the purification waste gas;
The cooler 20 is provided with refrigerant flow conduit, and the cooler cleaning solution outlet of the cooler 20 passes through the water pump IV 17 connect with the water tank cleaning solution import II on the top of water tank 12;
The inner bottom of water tank 12, which is provided with, makes the mixed uniformly agitator 18 of cleaning solution in the water tank 12;
The water tank cleaning solution outlet II of the side wall bottom of water tank 12 passes through the water pump V 9 and the hydrocyclone 7 Side wall connection;
The water tank cleaning solution of the outlet of hydrocyclone cleaning solution and the top of water tank 12 on the top of hydrocyclone 7 Import III is connected;
The solid impurity outlet of the bottom of hydrocyclone 7 is connected with the sludge tank 8;
The water tank cleaning solution outlet III of the bottom of water tank 12 passes through the stop valve IV 26 and the waste liquid storage cabinet 13 Connection;
The seawater pipe 6 is connected by the water pump VI 5 with the water tank cleaning solution import IV on the top of water tank 12.
When the stop valve I 22, stop valve II 23 get to connected state, the stop valve III 24 and the water pump VI 5 its One of be in connected state, oxidizer containing chlorine, alkali lye and the aqueous solution respectively from the oxidizer containing chlorine cabinet 2, alkali lye cabinet 3 with it is light Water tank 4 (seawater pipe 6) is delivered in the water tank 12 by water pump, after being well mixed by the stirring action of agitator 18 To cleaning solution, it is transported to by water pump III 15, the main jet shower pipe 16 in the scrubbing tower 19, while marine exhaust to be clean Exhaust gas inlet to be clean through the sidewall bottom of scrubbing tower 19 enters the scrubbing tower 19, inversely contacts and occurs with cleaning solution Reaction, realizes simultaneous SO_2 and NO removal, and waste gas goes out after the purification at the top of scrubbing tower 19 after the waste gas simple process after purification Mouth is directly discharged in air, and the cleaning solution after waste gas is purified in the scrubbing tower 19 and is cooled into the cooler 20 Processing, the cleaning solution after processing is returned in the water tank 12 through the water pump IV 17.In addition, appropriate oxidizer containing chlorine leads to Cross the water pump I 1 to be filled into the ballast tank 14, killed using the strong oxidizing property of oxidizer containing chlorine thin in ballast water Bacterium, algae and other microorganisms.Now, a kind of marine exhaust pollutant and ballast water Integrated Processing Unit are in simultaneously Desulphurization denitration mode of operation, can be to the NO in marine exhaustx、SOx, the multiple pollutant such as particulate matter and ballast water carry out General Office Reason;
When the stop valve I 22 gets to closed mode, stop valve II 23 gets to connected state, the stop valve III 24 and institute Stating water pump VI 5, one of them is in connected state, and alkali lye is with the aqueous solution respectively from the alkali lye cabinet 3 and fresh water tank 4 (seawater pipe 6) It is transported to by water pump in the water tank 12, obtains cleaning solution after being well mixed by the stirring action of agitator 18, pass through The water pump III 15, the main jet shower pipe 16 are transported in the scrubbing tower 19, while boat diesel engine waste gas warp to be clean The exhaust gas inlet to be clean of the sidewall bottom of scrubbing tower 19 enters the scrubbing tower 19, inversely contacts and occurs anti-with cleaning solution Answer, progress desulfurization process, waste gas outlet is direct after the purification at the top of scrubbing tower 19 after the waste gas simple process after purification It is discharged into air, and the cleaning solution after waste gas is purified in the scrubbing tower 19 and enters the cooler 20 progress cooling processing, Cleaning solution after processing is returned in the water tank 12 through the water pump IV 17.In addition, appropriate oxidizer containing chlorine passes through institute State water pump I 1 to be filled into the ballast tank 14, bacterium, the algae in ballast water are killed using the strong oxidizing property of oxidizer containing chlorine Class and other microorganisms.Now, a kind of marine exhaust pollutant and ballast water Integrated Processing Unit are independent in enclosed Desulfurization mode of operation, can be simultaneously to the SO in marine exhaustx, the multiple pollutant such as particulate matter and ballast water carry out integrated treatment;
When the stop valve I 22 gets to closed mode, stop valve II 23 gets to connected state, the stop valve III 24 and institute Stating water pump VI 5, one of them is in connected state, and alkali lye is with the aqueous solution respectively from the alkali lye cabinet 3 and fresh water tank 4 (seawater pipe 6) It is transported to by water pump in the water tank 12, obtains cleaning solution after being well mixed by the stirring action of agitator 18, pass through Water pump III 15, the main jet shower pipe 16 are transported in the scrubbing tower 19, while boat diesel engine waste gas to be clean is through described The exhaust gas inlet to be clean of the sidewall bottom of scrubbing tower 19 enters the scrubbing tower 19, inversely contacts and reacts with cleaning solution, Waste gas outlet is directly discharged after the purification at the top of scrubbing tower 19 after progress desulfurization process, the waste gas simple process after purification Into air, and the cleaning solution after waste gas is purified in the scrubbing tower 19 by being simply aerated, removing slag with after dilution processing, leading to Cross the triple valve 25 and the waste liquid discharge pipe 21 be directly discharged to it is big marine.In addition, appropriate oxidizer containing chlorine leads to Cross the water pump I 1 to be filled into the ballast tank 14, killed using the strong oxidizing property of oxidizer containing chlorine thin in ballast water Bacterium, algae and other microorganisms.Now, a kind of marine exhaust pollutant and ballast water Integrated Processing Unit are in open type Independent desulfurization mode of operation, can be simultaneously to the SO in marine exhaustx, the multiple pollutant such as particulate matter and ballast water carry out General Office Reason.
Finally it should be noted that:Various embodiments above is merely illustrative of the technical solution of the present invention, rather than its limitations;To the greatest extent The present invention is described in detail with reference to foregoing embodiments for pipe, it will be understood by those within the art that:Its according to The technical scheme described in foregoing embodiments can so be modified, or which part or all technical characteristic are entered Row equivalent substitution;And these modifications or replacement, the essence of appropriate technical solution is departed from various embodiments of the present invention technology The scope of scheme.

Claims (5)

1. a kind of marine exhaust pollutant and ballast water integrated conduct method, it is characterised in that with following steps:
S1, appropriate alkali lye, oxidizer containing chlorine, the aqueous solution is delivered in water tank by water pump respectively, washed after mixing Wash liquid;
When carrying out desulphurization denitration processing to marine exhaust simultaneously, the ratio that the oxidizer containing chlorine accounts for the cleaning solution is more than 0;
When only carrying out desulfurization process to marine exhaust, the ratio that the oxidizer containing chlorine accounts for the cleaning solution is 0;
S2, the cleaning solution enter to scrubbing tower by water pump from scrubbing tower top inlet, then by the scrubbing tower The showering washing device in portion carries out atomizing spray from top to down, and marine exhaust to be clean enters from scrubbing tower sidewall bottom air inlet Enter scrubbing tower, reacted with atomizing spray cleaning solution by inversely contacting, so that the processing to flue gas is realized, scrubbed tower Waste gas after purification can be directly discharged in air through simple process;
Only marine exhaust is taken off when carrying out desulphurization denitration processing to marine exhaust simultaneously or when using enclosed mode of washing Purify after the cleaning solution after waste gas is handled through cooler cooling and returned in water tank during sulphuring treatment, in scrubbing tower, in the water tank Cleaning solution removes solid impurity therein through hydrocyclone, and the solution after processing is returned into water tank, and is isolated Solid impurity be disposed in sludge tank;
When only carrying out desulfurization process to marine exhaust using open type mode of washing, the cleaning solution warp in scrubbing tower after purification waste gas Cross and be simply aerated, remove slag, diluting etc. after processing directly discharge into sea;
S3, according to ballast water capacity in ballast tank, take appropriate oxidizer containing chlorine, add it in ballast tank, using containing The strong oxidizing property of oxychloride agent kills bacterium, algae and the other microorganisms in ballast water, finally by selfdecomposition or follow-up Simple process eliminates oxidizer containing chlorine excessive in ballast water.
2. processing method according to claim 1, it is characterised in that:During handling marine exhaust, by Water in the water tank can lose because of evaporation, except miscellaneous operation etc., it is necessary to persistently supplement the aqueous solution in use, holding The liquid level of cleaning solution is in normal level in the water tank.
3. processing method according to claim 1, it is characterised in that:The step S2 is washed to marine exhaust progress wet method The particulate matter in marine exhaust is removed simultaneously during washing.
4. processing method according to claim 1, it is characterised in that:
The alkali lye refers to include one or several kinds of alkali in sodium hydroxide, sodium carbonate, sodium acid carbonate, magnesium hydroxide, magnesium carbonate The aqueous solution of property compound;
The oxidizer containing chlorine refers to include one kind in sodium hypochlorite, sodium chlorite, sodium chlorate, sodium perchlorate, chlorine dioxide Or the aqueous solution of several chlorine-containing compounds;
The aqueous solution refers to fresh water or seawater.
5. a kind of marine exhaust pollutant and ballast water Integrated Processing Unit, it is characterised in that:Including water pump I, oxidizer containing chlorine Cabinet, alkali lye cabinet, fresh water tank, water pump VI, seawater pipe, hydrocyclone, sludge tank, water pump V, main washing lotion tube, water pump II, water Cabinet, waste liquid storage cabinet, ballast tank, water pump III, main jet shower pipe, water pump IV, agitator, scrubbing tower, cooler, waste liquid discharge Pipe, stop valve I, stop valve II, stop valve III, triple valve and stop valve IV;
The oxidizer containing chlorine cabinet is connected by the water pump I with the ballast tank;
The oxidizer containing chlorine cabinet is connected by the stop valve I with the main washing lotion tube;
The alkali lye cabinet is connected by the stop valve II with the main washing lotion tube;
The fresh water tank is connected by the stop valve III with the main washing lotion tube;
The main washing lotion tube is connected by the water pump II with the water tank cleaning solution import I at the top of the water tank;
Water tank cleaning solution outlet I at the top of the water tank is connected by the water pump III with the main jet shower pipe;
The scrubbing tower inside cavity is provided with Multi-layer sprinkling device, the inlet of the spray equipment and point of the main jet shower pipe Pipeline connection;
The scrubbing tower sidewall bottom is provided with exhaust gas inlet to be clean, and top is provided with waste gas outlet after purification, and bottom is provided with purification Cleaning solution is exported after waste gas;
The cooler cleaning solution inlet communication that cleaning solution outlet passes through the triple valve and the cooler after the purification waste gas;
Cleaning solution outlet is connected by the triple valve with the waste liquid discharge pipe after the purification waste gas;
The cooler be provided with refrigerant flow conduit, the cooler cooler cleaning solution outlet by the water pump IV with it is described The water tank cleaning solution import II on water tank top is connected;
The water tank inner bottom, which is provided with, makes the mixed uniformly agitator of cleaning solution in the water tank;
The water tank cleaning solution outlet II of the water tank side wall bottom is connected by the water pump V with hydrocyclone side wall;
The water tank cleaning solution import III of the outlet of hydrocyclone cleaning solution and the water tank top on the hydrocyclone top Connection;
The solid impurity outlet of the hydrocyclone bottom is connected with the sludge tank;
The water tank cleaning solution outlet III of the water tank bottom is connected by the stop valve IV with the waste liquid storage cabinet;
The seawater pipe is connected by the water pump VI with the water tank cleaning solution import IV on the water tank top.
CN201710423188.4A 2017-06-07 2017-06-07 Comprehensive treatment method and device for ship waste gas pollutants and ballast water Active CN106984161B (en)

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Cited By (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107875855A (en) * 2017-11-14 2018-04-06 大连海事大学 A kind of boat diesel engine exhaust emission integrated conduct method and device
CN108392972A (en) * 2018-05-12 2018-08-14 德清县荣昌冷轧带钢有限公司 A kind of cold-rolled strip acid mist purifying device
CN110975611A (en) * 2019-10-18 2020-04-10 广州文冲船舶修造有限公司 Ship desulfurization system
WO2020143578A1 (en) * 2019-01-10 2020-07-16 彭斯干 Seagoing vessel clean sailing method and vessel
CN107754607B (en) * 2017-11-14 2021-05-14 大连海事大学 Comprehensive treatment method and device for exhaust gas of marine diesel engine
WO2021134925A1 (en) * 2019-12-30 2021-07-08 童裳慧 Semi-dry flue gas desulfurization and denitrification method
WO2021201795A1 (en) * 2020-04-03 2021-10-07 T.C. Piri Reis Universitesi Exhaust flue gas integrated treatment plant
CN113788135A (en) * 2021-08-17 2021-12-14 中船澄西船舶修造有限公司 Power supply disconnection and unhooking protection body system of desulfurization system for ship
CN114294078A (en) * 2022-01-04 2022-04-08 江南造船(集团)有限责任公司 Marine diesel engine exhaust gas cleaning system
IT202000024397A1 (en) * 2020-10-15 2022-04-15 Domenico Flagiello OXIDATIVE WET WASHING OF SOX AND NOX ARISING FROM COMBUSTION SMOKE USING SODIUM CHLORITE AQUEOUS SOLUTIONS.
CN115023280A (en) * 2020-08-12 2022-09-06 富士电机株式会社 Exhaust gas purification device

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN201923865U (en) * 2010-12-09 2011-08-10 赛温德罗有限公司 Ballast water treating system
CN102553428A (en) * 2012-01-10 2012-07-11 华北电力大学(保定) Absorption tower for desulfurization and denitrification combined with oxidant in forward-flow and back-flow spraying and method
US20160016109A1 (en) * 2013-02-22 2016-01-21 Marine Global Holding As Marine exhaust gas scrubber
CN105498535A (en) * 2015-12-01 2016-04-20 大连海事大学 Method and device for removing nitrogen oxide in waste gas of marine diesel engine by use of sodium chlorite seawater solution
CN105749722A (en) * 2016-04-18 2016-07-13 大连海事大学 Novel device and novel method for desulfurization washing of marine diesel exhaust
CN206823526U (en) * 2017-06-07 2018-01-02 大连海事大学 A kind of marine exhaust pollutant and ballast water Integrated Processing Unit

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN201923865U (en) * 2010-12-09 2011-08-10 赛温德罗有限公司 Ballast water treating system
CN102553428A (en) * 2012-01-10 2012-07-11 华北电力大学(保定) Absorption tower for desulfurization and denitrification combined with oxidant in forward-flow and back-flow spraying and method
US20160016109A1 (en) * 2013-02-22 2016-01-21 Marine Global Holding As Marine exhaust gas scrubber
CN105498535A (en) * 2015-12-01 2016-04-20 大连海事大学 Method and device for removing nitrogen oxide in waste gas of marine diesel engine by use of sodium chlorite seawater solution
CN105749722A (en) * 2016-04-18 2016-07-13 大连海事大学 Novel device and novel method for desulfurization washing of marine diesel exhaust
CN206823526U (en) * 2017-06-07 2018-01-02 大连海事大学 A kind of marine exhaust pollutant and ballast water Integrated Processing Unit

Cited By (14)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107754607B (en) * 2017-11-14 2021-05-14 大连海事大学 Comprehensive treatment method and device for exhaust gas of marine diesel engine
CN107875855A (en) * 2017-11-14 2018-04-06 大连海事大学 A kind of boat diesel engine exhaust emission integrated conduct method and device
CN108392972A (en) * 2018-05-12 2018-08-14 德清县荣昌冷轧带钢有限公司 A kind of cold-rolled strip acid mist purifying device
EP3909920A4 (en) * 2019-01-10 2022-09-21 Sigan Peng Seagoing vessel clean sailing method and vessel
WO2020143578A1 (en) * 2019-01-10 2020-07-16 彭斯干 Seagoing vessel clean sailing method and vessel
CN110975611A (en) * 2019-10-18 2020-04-10 广州文冲船舶修造有限公司 Ship desulfurization system
CN110975611B (en) * 2019-10-18 2021-11-23 广州文冲船舶修造有限公司 Ship desulfurization system
WO2021134925A1 (en) * 2019-12-30 2021-07-08 童裳慧 Semi-dry flue gas desulfurization and denitrification method
WO2021201795A1 (en) * 2020-04-03 2021-10-07 T.C. Piri Reis Universitesi Exhaust flue gas integrated treatment plant
CN115023280A (en) * 2020-08-12 2022-09-06 富士电机株式会社 Exhaust gas purification device
IT202000024397A1 (en) * 2020-10-15 2022-04-15 Domenico Flagiello OXIDATIVE WET WASHING OF SOX AND NOX ARISING FROM COMBUSTION SMOKE USING SODIUM CHLORITE AQUEOUS SOLUTIONS.
WO2022079596A1 (en) * 2020-10-15 2022-04-21 Boldrocchi S.R.L. Wet-oxidation scrubbing of sox and nox deriving from flue-gas using sodium chlorite aqueous solutions
CN113788135A (en) * 2021-08-17 2021-12-14 中船澄西船舶修造有限公司 Power supply disconnection and unhooking protection body system of desulfurization system for ship
CN114294078A (en) * 2022-01-04 2022-04-08 江南造船(集团)有限责任公司 Marine diesel engine exhaust gas cleaning system

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