CN107249716A - Exhaust gas treatment device and exhaust gas treatment method - Google Patents
Exhaust gas treatment device and exhaust gas treatment method Download PDFInfo
- Publication number
- CN107249716A CN107249716A CN201680011095.4A CN201680011095A CN107249716A CN 107249716 A CN107249716 A CN 107249716A CN 201680011095 A CN201680011095 A CN 201680011095A CN 107249716 A CN107249716 A CN 107249716A
- Authority
- CN
- China
- Prior art keywords
- activated carbon
- mercury
- mercury concentration
- quantity delivered
- exhaust
- 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
Links
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation 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
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/46—Removing components of defined structure
- B01D53/64—Heavy metals or compounds thereof, e.g. mercury
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation 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
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
- B01D53/81—Solid phase processes
- B01D53/83—Solid phase processes with moving reactants
Landscapes
- Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- Environmental & Geological Engineering (AREA)
- Health & Medical Sciences (AREA)
- Biomedical Technology (AREA)
- Analytical Chemistry (AREA)
- General Chemical & Material Sciences (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Treating Waste Gases (AREA)
- Waste-Gas Treatment And Other Accessory Devices For Furnaces (AREA)
Abstract
The problem of the present invention is to provide:Reliably absorption removes the mercury in the exhaust from stove, even if the mercury concentration in exhaust changes, and the exhaust gas treatment device and method of activated carbon can also be supplied with amounts of activated carbon adaptable therewith.Exhaust gas treatment device, the downstream position relative to the stove (1) is arranged to the dust collect plant (4) that the exhaust containing mercury from stove (1) carries out dust removal process, it is also provided with to the activated carbon feedway (3) that the exhaust flow path being vented from stove (1) guiding dust collect plant (4) is blown into activated carbon, wherein, it is provided with and determines the mercury densimeter (5) of the mercury concentration in exhaust in the downstream of dust collect plant (4), including:According to the measured value of mercury densimeter (5), so that the mercury concentration in the exhaust in the downstream of above-mentioned dust collect plant (4) is the mode below setting value, the control device (7) being controlled while activated carbon quantity delivered is maintained into defined minimum value.
Description
Technical field
The present invention relates to smelt factory etc. from castoff burning facility, cement manufacturing works, thermal power plant, nonferrous metal
Various factories discharge the exhaust containing mercury processing unit and exhaust gas treatment method.
Background technology
After the exhaust or mercury-containing wastes discharged from cement kiln, nonferrous metal smelting furnace are burned in incinerator
Sometimes with mercury in the exhaust of discharge, if being directly released in air, then it can cause atmosphere pollution and turn into problem.Then,
It is desirable to remove the mercury in exhaust.
In addition, " the Minamata treaty on mercury " was passed through in 2013, worldwide mercury management reinforcing action is entered
OK.After the treaty valid, discharge limitation object facility for mercury and suppress the countermeasure of mercury discharge in research.Discharge and limit as mercury
Object facility processed, can enumerate coal thermal power plant, coal fired boiler, nonferrous metal smelting facility, castoff burning facility, cement system
Make facility.In such a case, to effectively removing the demand day from the processing method of the mercury in the exhaust of these facilities discharge
Benefit is surging.
For example, as the general removing method from the mercury in the exhaust of incinerator or boiler furnace discharge, special
Known following methods in sharp document 1,2:The bag collector or electric that dedusting is carried out to the dust in exhaust is oriented to that will be vented
In the pipeline of dust arrester, relative to the activated carbon that bag collector etc. is blown into granular in upstream side position, mercury is set to be adsorbed in this
Activated carbon, reinstates bag collector etc. with dust one by the activated carbon for having adsorbed mercury and carries out dust, so as to be removed from exhaust.
Following methods are used in addition, also having:Prepare pre- in the calcium hydroxide that the sour gas in being vented is removed for neutralizing
The mixed powder of activated carbon is first mixed with, the mixed powder is blown into the exhaust in pipeline in the upstream side of bag collector, will be adsorbed
The activated carbon of the reaction product and mercury of sour gas and calcium hydroxide reinstates bag collector etc. with dust one and carries out dust,
So as to handle.In this way, after the mercury in exhaust is tightly held by activated carbon, carrying out dust to remove with bag collector etc..
System is removed Patent Document 2 discloses the mercury in exhaust, wherein, in the flue of the exhaust circulation containing mercury
Way sets dust arrester, and the flue in the upstream side of dust arrester sets up the activated carbon feeding device of input activated carbon, in exhaust
Mercury concentration instantaneously largely puts into activated carbon when exceeding normal concentration.
Prior art literature
Patent document
Patent document 1:Japanese Unexamined Patent Publication 2010-221085
Patent document 2:Japanese Unexamined Patent Publication 2014-213308.
The content of the invention
The invention problem to be solved
Depending on the raw material kind smelted in the discarded species or cement kiln of burning disposal in incinerator, nonferrous metal smelting furnace
Class, produces the mercury concentration temporarily elevated variation in exhaust sometimes.In this case, in order to maintain from chimney discharge row
Low mercury concentration in gas, it is necessary to be always blown into the quantity delivered for the activated carbon being blown into pipeline in large quantities, or, into pipeline
, it is necessary to always be blown into the quantity delivered of mixed powder in large quantities during the mixed powder that supply calcium hydroxide and activated carbon are pre-mixed.
If in this way, imagination temporarily elevated mercury concentration and activated carbon or mixed powder are always supplied into pipeline in large quantities,
Then in the most period in addition to the above-mentioned temporary transient period, cause oversupply activated carbon and mixed powder,
The usage amount for producing activated carbon or mixed powder is huge, the problem of pump-down process expense increases, or the amount of the dust etc. of dust is huge,
The problem of dust removal process expense increases.In mercury removing system in exhaust described in patent document 2, the mercury concentration only in exhaust
Activated carbon is put into during more than normal concentration, to adsorb the mercury accumulated on the filter cloth in removing dust arrester, therefore can be avoided unhelpful
Activated carbon use, but there is following worry:Only it is instantaneous input activated carbon, it is impossible to activated carbon is sufficiently formed on filter cloth
Layer, it is impossible to which absorption removes mercury.
In view of such situation, problem of the invention is to provide exhaust gas treatment device and exhaust gas treatment method, its is reliable
Ground absorption removes the mercury in exhaust, even if the mercury concentration in exhaust changes, and can also be supplied with amounts of activated carbon adaptable therewith
To activated carbon.
Means for solving the problems
According to the present invention, above-mentioned problem is solved by following exhaust gas treatment devices and its method.
[exhaust gas treatment device]
Exhaust gas treatment device the first invention described as follows, the second invention and the 3rd invention in the present invention are constituted like that, any
Person can solve above-mentioned problem.
The first inventions of < >
Exhaust gas treatment device, including:To by fire grate go out containing mercury exhaust carry out dust removal process dust collect plant, and to will row
The exhaust flow path that gas is oriented to dust collect plant from stove is blown into the activated carbon feedway of activated carbon, it is characterised in that including:In dust
The downstream of device determines the downstream mercury densimeter of the mercury concentration in exhaust, and the activated carbon of control activated carbon feedway is supplied
To the control device of amount, control device control activated carbon quantity delivered so that activated carbon quantity delivered is being maintained into defined minimum
While being worth the above, according to the mercury concentration measurement of downstream mercury densimeter, make in the exhaust in downstream of above-mentioned dust collect plant
Mercury concentration for below setting value.
The second inventions of < >
Exhaust gas treatment device, including:To by fire grate go out containing mercury exhaust carry out dust removal process dust collect plant, and to will row
The exhaust flow path that gas is oriented to dust collect plant from stove is blown into the activated carbon feedway of activated carbon, it is characterised in that including:In stove
Downstream and the upstream side mercury densimeter of the mercury concentration in the measure exhaust of the upstream side of dust collect plant, and control activated carbon supply dress
The control device for the activated carbon quantity delivered put, control device control activated carbon quantity delivered so that maintained by activated carbon quantity delivered
While more than defined minimum value, according to the mercury concentration measurement of upstream side mercury densimeter, make under above-mentioned dust collect plant
The mercury concentration in the exhaust of side is swum for below setting value.
The invention > of < the 3rd
Exhaust gas treatment device, including:To by fire grate go out containing mercury exhaust carry out dust removal process dust collect plant, and to will row
The exhaust flow path that gas is oriented to dust collect plant from stove is blown into the activated carbon feedway of activated carbon, it is characterised in that including:In stove
The upstream side mercury densimeter of downstream and the mercury concentration in the measure exhaust of the upstream side of dust collect plant, the downstream in dust collect plant
The control for determining the downstream mercury densimeter of the mercury concentration in exhaust and the activated carbon quantity delivered of control activated carbon feedway is filled
Put, control device control activated carbon quantity delivered so that while as defined in maintaining activated carbon quantity delivered more than minimum value,
According to the mercury concentration measurement of upstream side mercury densimeter and the mercury concentration measurement of downstream mercury densimeter, make above-mentioned dust collect plant
Downstream exhaust in mercury concentration for below setting value.
In first to the 3rd invention, control device is preferably in the mercury concentration of upstream side mercury densimeter or downstream mercury densimeter
When measured value is more than regulation mercury concentration, the mode that activated carbon quantity delivered is remained into defined maximum is controlled.
Although as the mercury concentration of time average and it is less high mercury concentration temporarily drastically raise when, if according to the Gao Gongnong
The substantial amounts of activated carbon of degree supply, then cause glut activated carbon in the time behind.Such excessive supply can pass through
It is above-mentioned to be controlled to prevent in the way of maximum as defined in activated carbon quantity delivered is remained.
In addition, in the first invention, control device can be in the downstream of the dust collect plant based on downstream mercury densimeter
Mercury concentration measurement in exhaust is advance relative to the ratio of the mercury concentration set point in the exhaust in the downstream of dust collect plant
When more than the ratio of determination, the mode that activated carbon quantity delivered is remained into defined maximum is controlled, above-mentioned true in advance
Fixed ratio is defined in the range of 0.4 ~ 0.8.By doing so it is possible, scope of the above-mentioned predetermined ratio 0.4 ~ 0.8
Interior, the opportunity that activated carbon quantity delivered is remained into defined maximum is determined.The reasons why so determining is because of above-mentioned pre-
The ratio first determined caused supply to exceed necessary big carbon content active, due to activated carbon is excessively used at generation than 0.4 hour
The problem of reason cost increases, in addition, when above-mentioned predetermined ratio is bigger than 0.8, activated carbon quantity delivered is not enough, it is impossible to fully
Absorption removes mercury, the problem of generation can not reduce to mercury concentration below mercury concentration set point.
In addition, in the second invention, control device can be in the upstream side of the dust collect plant based on upstream side mercury densimeter
Mercury concentration measurement in exhaust is advance relative to the ratio of the mercury concentration set point in the exhaust in the downstream of dust collect plant
When more than the ratio of determination, the mode that activated carbon quantity delivered is remained into defined maximum is controlled, above-mentioned true in advance
Fixed ratio is defined in the range of 20 ~ 200.By doing so it is possible, above-mentioned predetermined ratio is in the range of 20 ~ 200,
The opportunity that activated carbon quantity delivered is remained into defined maximum is determined.The reasons why so determining is because of above-mentioned advance
The ratio of determination caused supply to exceed necessary substantial amounts of activated carbon, due to activated carbon is excessively used at generation than 20 hours
The problem of reason cost increases, in addition, when above-mentioned predetermined ratio is bigger than 200, activated carbon quantity delivered is not enough, it is impossible to fully
Absorption removes mercury, the problem of generation can not reduce to mercury concentration below mercury concentration set point.
In addition, in the 3rd invention, control device can be in the downstream of the dust collect plant based on downstream mercury densimeter
Mercury concentration measurement in exhaust is dense relative to the downstream mercury of the mercury concentration set point in the exhaust in the downstream of dust collect plant
Spend ratio be predetermined ratio more than when, or the dust collect plant based on upstream side mercury densimeter upstream side exhaust in
Mercury concentration measurement is relative to the upstream side mercury concentration rate of the mercury concentration set point in the exhaust in the downstream of dust collect plant
When more than predetermined ratio, the mode that activated carbon quantity delivered is remained into defined maximum is controlled, above-mentioned pre-
The downstream mercury concentration rate first determined is defined in the range of 0.4 ~ 0.8, above-mentioned predetermined upstream side mercury concentration ratio
Rate is defined in the range of 20 ~ 200.By doing so it is possible, first, above-mentioned predetermined downstream mercury ratio is 0.4 ~ 0.8
In the range of, the opportunity that activated carbon quantity delivered is remained into defined maximum is determined.So determine the reasons why be because,
Above-mentioned predetermined downstream mercury concentration rate caused supply to exceed necessary substantial amounts of activated carbon, due to mistake than 0.4 hour
Amount produces the problem of processing cost increases using activated carbon, in addition, in above-mentioned predetermined downstream mercury concentration rate ratio
0.8 it is big when, activated carbon quantity delivered is not enough, it is impossible to which fully absorption removes mercury, and generation can not reduce to mercury concentration the setting of mercury concentration
The problem of value is following.In addition, second, above-mentioned predetermined upstream side mercury concentration rate is in the range of 20 ~ 200, by activity
The opportunity that charcoal quantity delivered remains defined maximum is determined.The reasons why so determining is because of above-mentioned predetermined
Upstream side mercury concentration rate caused supply to exceed necessary substantial amounts of activated carbon than 20 hours, due to being excessively used activated carbon
Processing cost is produced the problem of increase, in addition, when above-mentioned predetermined upstream side mercury concentration rate is bigger than 200, activated carbon
Quantity delivered is not enough, it is impossible to which fully absorption removes mercury, the problem of generation can not reduce to mercury concentration below mercury concentration set point.
In addition, in the first to the 3rd invention, control device will can blow as the activated carbon relative to processing extraction flow
The defined minimum value for entering the activated carbon quantity delivered that weight is determined is set as 10 ~ 200mg/Nm3It is controlled.So make activity
The defined minimum value of charcoal quantity delivered is in 10 ~ 200mg/Nm3Scope, the mercury concentration in exhaust is set as in the scope when low
The value of low scope, is set as the value of high scope when mercury concentration is high.When mercury concentration ratio setting in exhaust is low, by work
Property charcoal quantity delivered remains defined minimum value, so as in the bag collector of dust collect plant, always be formed with activated carbon
Adsorption layer, therefore, when discharge contains the exhaust than the mercury of above-mentioned setting high concentration, due to preformed above-mentioned adsorption layer
Absorption removing effect and the absorption removing of the activated carbon that is now blown into effect, also can rapidly and reliably adsorb removing mercury, make
The mercury concentration of exhaust after dust is substantially low concentration.If minimum value is less than 10mg/Nm as defined in above-mentioned3, then filled in dust
It is difficult to the adsorption layer for being sufficiently formed activated carbon in the bag collector put, so it is improper, if minimum value as defined in above-mentioned is more than
200mg/Nm3, then activated carbon quantity delivered become excessive, cost increases, so uneconomical.
In addition, in the first to the 3rd invention, control device will can blow as the activated carbon relative to processing extraction flow
The defined maximum for entering the activated carbon quantity delivered that weight is determined is set as 300 ~ 1000mg/Nm3It is controlled.So make work
The setting maximum of property charcoal quantity delivered is in 300 ~ 1000mg/Nm3Scope, the mercury concentration in exhaust is set as the scope when low
In low scope value, be set as the value of high scope when mercury concentration is high.If above-mentioned setting maximum is less than 300mg/Nm3,
Then generation activated carbon can not adsorb the bad of the mercury in removing exhaust sometimes, so it is improper, if above-mentioned setting maximum is more than
1000mg/Nm3, then activated carbon quantity delivered become excessive, cost increases, so uneconomical.
In addition, in the first to the 3rd invention, the increase on activated carbon quantity delivered from minimum value to maximum, control device
Mercury concentration measurement that can be in exhaust from zero or less than can determination limit minimum value value to the first regulation mercury concentration model
Enclose, activated carbon is supplied on the basis of the activated carbon quantity delivered of defined minimum value, above-mentioned first is reached in mercury concentration measurement
Provide after mercury concentration, with the increase of mercury concentration measurement, activated carbon quantity delivered is linearly increased from defined minimum value,
When mercury concentration measurement reaches the second regulation mercury concentration, make the quantity delivered that activated carbon quantity delivered is defined maximum, it is dense in mercury
Spend after the above-mentioned second regulation mercury concentration of measured value arrival, relative to the increase of mercury concentration measurement, with its defined maximum
Activated carbon quantity delivered is remained constant.
In addition, in the first to the 3rd invention, the increase on activated carbon quantity delivered from minimum value to maximum, control device
Mercury concentration measurement that can also be in exhaust from zero or less than can determination limit minimum value value to the first regulation mercury concentration
Scope, supplies activated carbon, in mercury concentration on the basis of using defined minimum value as the activated carbon quantity delivered of the first quantity delivered
When measured value reaches above-mentioned first regulation mercury concentration, activated carbon quantity delivered is increased into defined second quantity delivered step by step,
Mercury concentration measurement reaches the scope untill the second regulation mercury concentration, and activated carbon quantity delivered is remained into perseverance with the second quantity delivered
It is fixed, in addition, when mercury concentration measurement reaches the second regulation mercury concentration, defined 3rd supply is increased to activated carbon quantity delivered
The mode of amount, with the increase of mercury concentration measurement, repeats increase activated carbon quantity delivered, in the increase of activated carbon quantity delivered step by step
To after defined maximum, relative to the increase of mercury concentration measurement, activated carbon quantity delivered is protected with its defined maximum
Hold to be constant.
As noted above, the mercury concentration measurement in exhaust makes activated carbon quantity delivered increase from minimum value to maximum
Greatly, so as to do not occur because of the quantity delivered governor motion of activated carbon feedway it is bad in the case of, successfully control live
Property charcoal quantity delivered.
[exhaust gas treatment method]
Exhaust gas treatment method the 4th invention described as follows, the 5th invention and the 6th invention in the present invention are constituted like that, any
Person can solve above-mentioned problem.
The invention > of < the 4th
Exhaust gas treatment method, methods described carries out dust removal process with dust collect plant to the exhaust containing mercury gone out by fire grate, by work
Property charcoal from activated carbon feedway be blown into will be vented from stove be oriented to dust collect plant exhaust flow path, it is characterised in that including:In collection
The downstream of dirt device determines the determination step of the mercury concentration in exhaust with downstream mercury densimeter, and controls work with control device
Property charcoal feedway activated carbon quantity delivered rate-determining steps, activated carbon quantity delivered is controlled in rate-determining steps so that by activity
While charcoal quantity delivered is maintained more than defined minimum value, according to the mercury concentration measurement of downstream mercury densimeter, make above-mentioned
Mercury concentration in the exhaust in the downstream of dust collect plant is below setting value.
The invention > of < the 5th
Exhaust gas treatment method, methods described carries out dust removal process with dust collect plant to the exhaust containing mercury gone out by fire grate, by work
Property charcoal from activated carbon feedway be blown into will be vented from stove be oriented to dust collect plant exhaust flow path, it is characterised in that including:In stove
Downstream and dust collect plant upstream side with upstream side mercury densimeter determine exhaust in mercury concentration determination step, and with control
Activated carbon quantity delivered is controlled in the rate-determining steps of the activated carbon quantity delivered of device control activated carbon feedway processed, rate-determining steps,
So that while as defined in maintaining activated carbon quantity delivered more than minimum value, being surveyed according to the mercury concentration of upstream side mercury densimeter
Definite value, make above-mentioned dust collect plant downstream exhaust in mercury concentration for below setting value.
The invention > of < the 6th
Exhaust gas treatment method, methods described carries out dust removal process with dust collect plant to the exhaust containing mercury gone out by fire grate, by work
Property charcoal be blown into from activated carbon feedway from activated carbon feedway and will be vented the exhaust flow path that dust collect plant is oriented to from stove, it is special
Levy and be, including:Mercury concentration in determining exhaust with upstream side mercury densimeter in the downstream of stove and the upstream side of dust collect plant
While the downstream of dust collect plant with downstream mercury densimeter determine exhaust in mercury concentration determination step, and with control
Activated carbon quantity delivered is controlled in the rate-determining steps of the activated carbon quantity delivered of device control activated carbon feedway, rate-determining steps, is made
Obtain while as defined in maintaining activated carbon quantity delivered more than minimum value, according to the mercury concentration mensuration of upstream side mercury densimeter
Value and downstream mercury densimeter mercury concentration measurement, make above-mentioned dust collect plant downstream exhaust in mercury concentration for setting
Value is following.
In 4th to the 6th invention, rate-determining steps are preferably in the mercury concentration of upstream side mercury densimeter or downstream mercury densimeter
When measured value is more than regulation mercury concentration, the mode that activated carbon quantity delivered is remained into defined maximum is controlled.
Although as the mercury concentration of time average and it is less high mercury concentration temporarily drastically raise when, if according to the high mercury concentration
Substantial amounts of activated carbon is supplied, then causes glut activated carbon in the time behind.Such excessive supply can be by upper
State and be controlled to prevent in the way of maximum as defined in activated carbon quantity delivered is remained.
In addition, in the 4th invention, rate-determining steps can be in the downstream of the dust collect plant based on downstream mercury densimeter
Mercury concentration measurement in exhaust is advance relative to the ratio of the mercury concentration set point in the exhaust in the downstream of dust collect plant
When more than the ratio of determination, the mode that activated carbon quantity delivered is remained into defined maximum is controlled, above-mentioned true in advance
Fixed ratio is defined in the range of 0.4 ~ 0.8.By doing so it is possible, scope of the above-mentioned predetermined ratio 0.4 ~ 0.8
Interior, the opportunity that activated carbon quantity delivered is remained into defined maximum is determined.The reasons why so determining is because of above-mentioned pre-
The ratio first determined caused supply to exceed necessary substantial amounts of activated carbon, and produced due to activated carbon is excessively used than 0.4 hour
The problem of processing cost increases, in addition, when above-mentioned predetermined ratio is bigger than 0.8, activated carbon quantity delivered is not enough, it is impossible to fill
Absorption is divided to remove mercury, the problem of generation can not reduce to mercury concentration below mercury concentration set point.
In addition, in the 5th invention, rate-determining steps can be in the upstream side of the dust collect plant based on upstream side mercury densimeter
Mercury concentration measurement in exhaust is advance relative to the ratio of the mercury concentration set point in the exhaust in the downstream of dust collect plant
When more than the ratio of determination, the mode that activated carbon quantity delivered is remained into defined maximum is controlled, above-mentioned true in advance
Fixed ratio is defined in the range of 20 ~ 200.By doing so it is possible, above-mentioned predetermined ratio is in the range of 20 ~ 200,
The opportunity that activated carbon quantity delivered is remained into defined maximum is determined.The reasons why so determining is because of above-mentioned advance
The ratio of determination caused supply to exceed necessary substantial amounts of activated carbon, due to activated carbon is excessively used at generation than 20 hours
The problem of reason cost increases, in addition, when above-mentioned predetermined ratio is bigger than 200, activated carbon quantity delivered is not enough, it is impossible to fully
Absorption removes mercury, the problem of generation can not reduce to mercury concentration below mercury concentration set point.
In addition, in the 6th invention, rate-determining steps can be in the downstream of the dust collect plant based on downstream mercury densimeter
Mercury concentration measurement in exhaust is dense relative to the downstream mercury of the mercury concentration set point in the exhaust in the downstream of dust collect plant
Spend ratio be predetermined ratio more than when, or the dust collect plant based on upstream side mercury densimeter upstream side exhaust in
Mercury concentration measurement is relative to the upstream side mercury concentration rate of the mercury concentration set point in the exhaust in the downstream of dust collect plant
When more than predetermined ratio, the mode that activated carbon quantity delivered is remained into defined maximum is controlled, above-mentioned pre-
The downstream mercury concentration rate first determined is defined in the range of 0.4 ~ 0.8, above-mentioned predetermined upstream side mercury concentration ratio
Rate is defined in the range of 20 ~ 200.By doing so it is possible, first, above-mentioned predetermined downstream mercury ratio is 0.4 ~ 0.8
In the range of, the opportunity that activated carbon quantity delivered is remained into defined maximum is determined.So determine the reasons why be because,
Above-mentioned predetermined downstream mercury concentration rate caused supply to exceed necessary substantial amounts of activated carbon, due to mistake than 0.4 hour
Amount produces the problem of processing cost increases using activated carbon, in addition, in above-mentioned predetermined downstream mercury concentration rate ratio
0.8 it is big when, activated carbon quantity delivered is not enough, it is impossible to which fully absorption removes mercury, and generation can not reduce to mercury concentration the setting of mercury concentration
The problem of value is following.In addition, second, above-mentioned predetermined upstream side mercury concentration rate is in the range of 20 ~ 200, by activity
The opportunity that charcoal quantity delivered remains defined maximum is determined.The reasons why so determining is because of above-mentioned predetermined
Upstream side mercury concentration rate caused supply to exceed necessary substantial amounts of activated carbon than 20 hours, due to being excessively used activated carbon
Processing cost is produced the problem of increase, in addition, when above-mentioned predetermined upstream side mercury concentration rate is bigger than 200, activated carbon
Quantity delivered is not enough, it is impossible to abundant Adsorption of Mercury, the problem of generation can not reduce to mercury concentration below mercury concentration set point.
In addition, in the 4th to the 6th invention, rate-determining steps will can blow as the activated carbon relative to processing extraction flow
The defined minimum value for entering the activated carbon quantity delivered that weight is determined is set as 10 ~ 200mg/Nm3It is controlled.So make activity
The defined minimum value of charcoal quantity delivered is in 10 ~ 200mg/Nm3Scope, the mercury concentration in exhaust is set as in the scope when low
The value of low scope, is set as the value of high scope when mercury concentration is high.In this way, the mercury concentration ratio setting in exhaust is low
When, activated carbon quantity delivered is remained into defined minimum value, so as in the bag collector of dust collect plant, always be formed with work
Property charcoal adsorption layer, therefore, discharge containing the high concentration mercury higher than above-mentioned setting concentration exhaust when, due to being pre-formed
Above-mentioned adsorption layer absorption removing effect and the absorption removing of the activated carbon that is now blown into effect, also can rapidly and reliably inhale
Attached removing mercury, the mercury concentration for making the exhaust after dust is substantially low concentration.If minimum value is less than 10mg/Nm as defined in above-mentioned3,
Then it is difficult to the adsorption layer for being sufficiently formed activated carbon in the bag collector of dust collect plant, so it is improper, if as defined in above-mentioned
Minimum value is more than 200mg/Nm3, then activated carbon quantity delivered become excessive, cost increases, so uneconomical.
In addition, in the 4th to the 6th invention, rate-determining steps will can blow as the activated carbon relative to processing extraction flow
The defined maximum for entering the activated carbon quantity delivered that weight is determined is set as 300 ~ 1000mg/Nm3It is controlled.So make work
The setting maximum of property charcoal quantity delivered is in 300 ~ 1000mg/Nm3Scope, the mercury concentration in exhaust is set as the scope when low
In low scope value, be set as the value of high scope when mercury concentration is high.If above-mentioned setting maximum is less than 300mg/Nm3,
Then generation activated carbon can not adsorb the bad of the mercury in removing exhaust sometimes, so it is improper, if above-mentioned setting maximum is more than
1000mg/Nm3, then activated carbon quantity delivered become excessive, cost increases, so uneconomical.
In addition, in the 4th to the 6th invention, the increase on activated carbon quantity delivered from minimum value to maximum, rate-determining steps
Mercury concentration measurement that can be in exhaust from zero or less than can determination limit minimum value value to the first regulation mercury concentration model
Enclose, activated carbon is supplied on the basis of the activated carbon quantity delivered of defined minimum value, above-mentioned first is reached in mercury concentration measurement
Provide after mercury concentration, with the increase of mercury concentration measurement, activated carbon quantity delivered is linearly increased from defined minimum value,
When mercury concentration measurement reaches the second regulation mercury concentration, make the quantity delivered that activated carbon quantity delivered is defined maximum, it is dense in mercury
Spend after the above-mentioned second regulation mercury concentration of measured value arrival, relative to the increase of mercury concentration measurement, with its defined maximum
Activated carbon quantity delivered is remained constant.
In addition, in the 4th to the 6th invention, the increase on activated carbon quantity delivered from minimum value to maximum, rate-determining steps
Can also exhaust mercury concentration measurement from zero or less than can determination limit minimum value value to first regulation mercury concentration model
Enclose, activated carbon is supplied on the basis of using defined minimum value as the activated carbon quantity delivered of the first quantity delivered, surveyed in mercury concentration
When definite value reaches above-mentioned first regulation mercury concentration, activated carbon quantity delivered is increased into defined second quantity delivered step by step, in mercury
Concentration measurement reach second provide mercury concentration untill scope, activated carbon quantity delivered is remained with the second quantity delivered it is constant,
In addition, when mercury concentration measurement reaches the second regulation mercury concentration, defined 3rd quantity delivered is increased to activated carbon quantity delivered
Mode, with the increase of mercury concentration measurement, increase activated carbon quantity delivered is repeated step by step, is increased in activated carbon quantity delivered
After defined maximum, relative to the increase of mercury concentration measurement, activated carbon quantity delivered is kept with its defined maximum
To be constant.
It is as noted above, according to the mercury concentration measurement of exhaust, activated carbon quantity delivered is increased from minimum value to maximum,
So as to do not occur because of the quantity delivered governor motion of activated carbon feedway it is bad in the case of, successfully control activated carbon
Quantity delivered.
According to such present invention, in the first invention and the 4th invention, in the downstream of dust collect plant, mercury densimeter is used
Determine based on activated carbon mercury absorption remove after exhaust in real-time mercury concentration to adjust activated carbon quantity delivered, so as to
Activated carbon quantity delivered is adjusted in the case of without excessive and deficiency, it is below the setting value allowed to make the mercury concentration.
In second invention and the 5th invention, in the downstream of stove and the upstream side of dust collect plant, determined with mercury densimeter
Mercury concentration, activated carbon quantity delivered is adjusted according to the measured value, so that the mercury concentration in the exhaust in the downstream of dust collect plant is appearance
Perhaps below setting value.When mercury concentration in the exhaust from stove there occurs variation, determined before exhaust inflow dust collection device
Mercury concentration, according to the measured value, rapidly can be adjusted to appropriate amount by activated carbon quantity delivered, can be relative to mercury concentration
In the case that variation does not produce delay, the mercury concentration in reliably making the exhaust discharged from chimney is below the setting value allowed.
In addition, in the 3rd invention and the 6th invention, in the upstream side in the downstream of stove and dust collect plant mercury densimeter
While determining mercury concentration, mercury concentration also is determined with mercury densimeter in the downstream of dust collect plant, according to the measured value of both
Activated carbon quantity delivered is adjusted, the mercury concentration for making the downstream of dust collect plant is below the setting value allowed.According to the downstream of stove
And the mercury concentration measurement of the upstream side of dust collect plant, the control of the base value of activated carbon quantity delivered is determined, in addition, according to collection
The mercury concentration measurement in the downstream of dirt device, activated carbon quantity delivered relative to base value increase and decrease the mode of regulation, is mended
Fill control activated carbon quantity delivered.By so doing, can more may be used in the case where the variation relative to mercury concentration does not postpone
Mercury concentration in making the exhaust discharged from chimney by ground is below the setting value allowed.
In first invention and the 4th invention, the real-time mercury concentration in the downstream of dust collect plant is determined, therefore reliably
Mercury concentration in making the exhaust discharged from chimney is changed for the mercury concentration below setting value, but in the exhaust from stove
When, relative to the variation, the regulation of activated carbon quantity delivered is with delay.On the other hand, in the second invention and the 5th invention,
The upstream side of dust collect plant determines mercury concentration, therefore also can rapidly be tackled for above-mentioned variation.In addition, the 3rd invention and
In 6th invention, mercury concentration is determined in the upstream side of dust collect plant, and mercury concentration is determined in the downstream of dust collect plant, according to this
Both measured value regulation activated carbon quantity delivereds, in the case of not postponing in the variation relative to mercury concentration, more
Mercury concentration in reliably making the exhaust discharged from chimney is below the setting value allowed.
Invention effect
So according to the present invention, the mercury concentration in the position finding exhaust in the downstream of dust collect plant, or in dust collect plant
Upstream side determine, or determined in the upstream side of dust collect plant and downstream, amounts of activated carbon maintained into defined minimum
While being worth the above, the quantity delivered for the activated carbon being blown into is adjusted according to mercury concentration measurement, therefore, in the exhaust discharged from chimney
Mercury concentration reliably for below setting, and no excess and it is not enough in the case of supply activated carbon, can suppress living
While the usage amount of property charcoal, the attenuating of pump-down process expense is realized.
Brief description of the drawings
Fig. 1 shows first embodiment of the invention device, and (A) is its structural representation, and (B) is activated carbon feedway
Structural representation.
Fig. 2 is the structural representation of second embodiment of the invention device.
Fig. 3 is the structural representation of third embodiment of the invention device.
Fig. 4 (A) ~ (H) shows the adoptable various patterns of relation as mercury concentration and activated carbon quantity delivered in exhaust.
Fig. 5 is the figure for the relation for showing the chimney mercury concentration used in embodiments of the invention and activated carbon quantity delivered.
Fig. 6 is the pass for showing the bag collector entrance mercury concentration used in embodiments of the invention and activated carbon quantity delivered
The figure of system.
Embodiment
Hereinafter, embodiment of the present invention is illustrated with reference to the accompanying drawings.
In the present embodiment as shown below, as the stove of exhaust of the discharge containing mercury, with regard to the burning of burning waste
Stove is illustrated, but the invention is not restricted to this, can be gone out as the various fire grates from cement kiln, nonferrous metal smelting furnace etc.
The exhaust containing mercury processing unit and processing method use.
For the exhaust of the incinerator from burning waste, by the bag collector set for dust
Trip position is blown into activated carbon into exhaust flow path, can suppress the mercury concentration in the downstream of bag collector in extremely low concentration water
It is flat, but conventional, due to discarding the variation of species and amount, the mercury concentration in the exhaust from incinerator changes, and is
Situation that defence temporarily rises in the downstream mercury concentration of bag collector is vented, it is necessary to be always blown into activated carbon in large quantities
Processing cost increases.Then, in the present embodiment, mercury concentration is determined with mercury densimeter, according to the mercury concentration of measure, to exhaust
It is blown into stream without excessive and not enough amounts of activated carbon.The form of the preferred METHOD FOR CONTINUOUS DETERMINATION of mercury densimeter.
The first embodiments of < >
In Fig. 1 of the schematic structure of display the present embodiment device, the exhaust from incinerator 1 is being oriented to chimney 6
In exhaust flow path, boiler 2 and the bag collector 4 as dust collect plant are configured from upstream side, there is provided in bag collector 4
Upstream position be blown into exhaust flow path for adsorb remove exhaust in mercury activated carbon activated carbon feedway 3 and control
Its control device 7 is made, is also provided with determining row in the downstream of the bag collector 4 i.e. outlet of bag collector 4 or chimney 6
The mercury densimeter 5 of mercury concentration in gas, above-mentioned mercury densimeter 5 is connected to the control device 7 so that the measure of the mercury densimeter 5
Value is sent to above-mentioned control device 7 as output signal.
In described the present embodiment device, in the exhaust in the downstream that bag collector 4 is determined with mercury densimeter 5
Mercury concentration.
The measured value of mercury densimeter 5 is sent to control device 7, the measured value and predetermined regulation mercury concentration value ratio
Compared with to control activated carbon feedway 3.
When the above-mentioned regulation mercury concentration value of the mercury concentration ratio of measure is high, increase activated carbon quantity delivered.Supplied in increase activated carbon
After amount, when lasting mercury concentration is the state below above-mentioned regulation mercury concentration value, entered in the way of lowering activated carbon quantity delivered
Row control.
Specifically, above-mentioned activated carbon feedway 3 has:The feed hopper 3A of activated carbon is accommodated, feed hopper 3A's
The distribution member 3B for the rotated versions that lower part outlet is set, and in the valve or adjustable plate 3C set further below.Described
In activated carbon feedway 3, the command signal for carrying out self-control device 7, rotating speed, the valve of regulation distribution member 3B rotation are received
Aperture and adjustable plate 3C aperture at least one, be supplied to adjusting the quantity delivered of activated carbon in above-mentioned exhaust flow path.
The second embodiments of < >
The present embodiment shown in Fig. 2 is compared with the first already described embodiment, and the allocation position of only mercury densimeter 5 is different, its
He is identical.Therefore, in Fig. 2, for the position common with the position of Fig. 1 the first embodiment, additional identical symbol, so that
The description thereof will be omitted.
In the present embodiment, as seen in Figure 2, the mercury that mercury densimeter 5 is configured in following position findings are vented is dense
Degree:The downstream of incinerator 1 and the upstream side of bag collector 4, the activated carbon of activated carbon feedway 3 are blown into the upstream of position
The position of side.In the present embodiment, the mercury concentration and activity that locate is held according to the data of accumulation by control device 7
The relation of charcoal quantity delivered and the mercury concentration of the downstream position of bag collector 4.It therefore, it can determine and be blown into position in activated carbon
The mercury concentration of upstream side, the mercury concentration in the downstream of bag collector 4 is estimated by the mercury concentration measurement and activated carbon quantity delivered.
That is, the mercury concentration measurement of the upstream side of position is blown into according to above-mentioned activated carbon by control device 7, presumption bag collector 4
The mercury concentration in downstream, can be obtained in order that the presumption mercury concentration is the work required for below predetermined regulation mercury concentration value
Property charcoal quantity delivered, so as to control the activated carbon quantity delivered of activated carbon feedway 3.As a result, making under bag collector 4
The mercury concentration of trip is below regulation mercury concentration value.
In described the present embodiment, when the mercury concentration in the exhaust from incinerator 1 changes, because mercury is dense
Degree 5 activated carbon in the downstream of incinerator 1 and activated carbon feedway 3 of meter is blown into the position finding and inspection of the upstream side of position
Survey the variation of the mercury concentration, it is possible to the reply of activated carbon quantity delivered is rapidly adjusted, therefore can be in no time
The mercury concentration in the exhaust in chimney is securely maintained below setting value in the case of delay.In Fig. 2 illustrated example
In, the mercury concentration mensuration position of mercury densimeter 5 is blown into the upstream side of position in activated carbon, but not limited to this, can also be in bag
The upstream side of formula dust arrester 4 and the activated carbon are blown into the downstream of position.
The embodiment > of < the 3rd
The present embodiment shown in Fig. 3 is compared with the second embodiment above, except the activated carbon in activated carbon feedway 3
Outside the first mercury densimeter 5A for being blown into the configuration of the upstream side of position, it is also provided with the downstream of bag collector 4 i.e. pocket type
The outlet of dust arrester 4 or chimney 6 determine the second mercury densimeter 5B of the mercury concentration in exhaust, the second mercury densimeter 5B measure
Value is sent to control device 7 as output signal.It is identical with the second embodiment in addition to this point.Therefore, in Fig. 3, for
The common position in the position of Fig. 2 the second embodiment, additional identical symbol, so that the description thereof will be omitted.
In the present embodiment, as shown in Figure 3, except the work of the activated carbon feedway 3 in foregoing second embodiment
Property charcoal be blown into the upstream side of position configuration the first mercury densimeter 5A outside, be also provided with second in the outlet of bag collector 4
Mercury densimeter 5B.As the second embodiment, the of the upstream side of position is blown into according to the activated carbon of activated carbon feedway 3
One mercury densimeter 5A measured value controls the base value of activated carbon quantity delivered, and then the second mercury of the outlet according to bag collector 4
Densimeter 5B measured value, supplements the control of the measured value based on the first mercury densimeter 5A, so as to increase and decrease activated carbon quantity delivered
Mode control.
The first mercury densimeter 5A that the upstream side of position is blown into from the activated carbon in activated carbon feedway 3 detects that mercury is dense
Measured value increased phenomenon (being referred to as measured value peak) in a short time is spent, to the second mercury concentration of the outlet in bag collector 4
Meter 5B detects mercury concentration measurement peak, and therefore existence time delay, position is blown into the activated carbon of activated carbon feedway 3
The mercury concentration measurement peak of upstream side when fully calming down, may also detect mercury concentration mensuration in the outlet of bag collector 4
It is worth peak.Then, the second mercury densimeter 5B is set, controls activated carbon to supply according to the mercury concentration measurement of the outlet of bag collector 4
To amount, so that the control of the measured value based on the first mercury densimeter 5A is supplemented, can be by the mercury concentration in the exhaust in chimney more
Reliably it is reduced to below setting value.
In embodiment of the present invention, control device can also be supplied according to the mercury concentration measurement and activated carbon of mercury densimeter
To the predetermined corresponding relation of amount, activated carbon quantity delivered is controlled.It is used as predetermined mercury concentration measurement and activated carbon
The corresponding relation of quantity delivered, can apply various schemes.
Can be the row with measure as predetermined mercury concentration measurement and the corresponding relation of activated carbon quantity delivered
The increase of mercury concentration in gas, activated carbon quantity delivered is progressively increased to since defined minimum value the correspondence of defined maximum
The scheme of relation.As the defined minimum value of activated carbon quantity delivered, it can also be arranged during the operating of exhaust is discharged from incinerator 1
When mercury concentration in gas is extremely low, activated carbon is always blown into the quantity delivered of the minimum value as minimum, so that it is determined that can be by
Mercury concentration in exhaust in chimney securely maintains the value of the activated carbon quantity delivered below setting value.With in exhaust, mercury is dense
The increase of measured value is spent, activated carbon quantity delivered is gradually increased since defined minimum value, supplied relative to mercury concentration in exhaust
Activated carbon to appropriate amount.In the scheme for the corresponding relation for gradually increasing activated carbon quantity delivered since defined minimum value
In, with the increase of mercury concentration, activated carbon quantity delivered can be linearly increased, multiple stages can also be divided to increase step by step,
The scheme of various corresponding relations can be used.As the means of the quantity delivered of regulation activated carbon, activated carbon is adjusted alone or in combination and is supplied
Aperture to the rotating speed of rotation of the rotated versions distribution member of device, the aperture of valve and adjustable plate etc., it is preferred to use with this
The adjustable range of a little governor motions is mutually fitted with control characteristic (being carried out continuously or carrying out stage by stage such as the increase and decrease of quantity delivered)
The scheme for the corresponding relation answered.
The example of the various schemes of mercury concentration measurement and the corresponding relation of activated carbon quantity delivered is shown in Fig. 4.
Scheme shown in Fig. 4 (A) is following scheme:The mercury concentration from exhaust measured value from zero or less than can determination limit
The value of minimum value is supplied to the scope of predetermined regulation mercury concentration on the basis of the activated carbon quantity delivered of defined minimum value
To activated carbon, when the measured value of mercury concentration reaches above-mentioned regulation mercury concentration, activated carbon quantity delivered is steppingly increased into rule
Fixed maximum, in addition, for the increase of mercury concentration in exhaust, activated carbon quantity delivered is kept into permanent in its defined maximum
It is fixed.The program is that, when the measured value of mercury concentration is lower than regulation mercury concentration, it is defined minimum value to make activated carbon quantity delivered, than
When providing that mercury concentration is high, the corresponding relation for making activated carbon quantity delivered be defined maximum can use simple controlling organization control
Preparing active carbon quantity delivered.
Scheme shown in Fig. 4 (B) is following scheme:In exhaust the measured value of mercury concentration from zero or less than can determination limit most
The value of small value is to the first scope for providing mercury concentration, on the basis of the activated carbon quantity delivered (the first quantity delivered) of defined minimum value
Upper supply activated carbon, when the measured value of mercury concentration reaches above-mentioned first regulation mercury concentration, steppingly by activated carbon quantity delivered
Second quantity delivered as defined in increasing to, relative to the increase of mercury concentration in exhaust, activated carbon quantity delivered is protected with the second quantity delivered
Hold to be constant, in addition, when the measured value of mercury concentration reaches second and provides mercury concentration, activated carbon quantity delivered is increased into regulation
The 3rd quantity delivered mode, with the increase of mercury concentration in exhaust, increase activated carbon quantity delivered is repeated with the trickle stage,
Activated carbon quantity delivered is increased to after defined maximum, relative to the increase of mercury concentration in exhaust, with its defined maximum
Activated carbon quantity delivered is remained constant.With the increase of mercury concentration in exhaust, by activated carbon quantity delivered from defined minimum value
Defined maximum is increased to step by step, so as to be controlled relative to mercury concentration in exhaust so that by the confession of activated carbon
Give more appropriate amount supply.
Scheme shown in Fig. 4 (C) is following scheme:It is linear from defined minimum value with the increase of mercury concentration in exhaust
Ground increases activated carbon quantity delivered.In addition, the case shown in Fig. 4 (D) is following scheme:The measured value of mercury concentration reaches rule in exhaust
Determine the scope untill mercury concentration, with the increase of mercury concentration in exhaust, activated carbon supply is linearly increased from defined minimum value
Amount, in the above-mentioned defined exhaust of measured value arrival of mercury concentration during mercury concentration, it is defined maximum to make activated carbon quantity delivered
Quantity delivered, increased in activated carbon quantity delivered as defined in after maximum, relative to the increase of mercury concentration in exhaust, advised with it
Fixed maximum remains activated carbon quantity delivered constant.In case shown in Fig. 4 (C), (D), with the increasing of mercury concentration in exhaust
Plus, continuously increase activated carbon quantity delivered from defined minimum value, so as to relative to entering in exhaust mercury concentration very fine
Row control, activated carbon is supplied with appropriate amount.
Scheme shown in Fig. 4 (E) is following scheme:In exhaust the measured value of mercury concentration from zero or less than can determination limit most
The value of small value supplies activity to the scope of the first regulation mercury concentration on the basis of the activated carbon quantity delivered of defined minimum value
Charcoal, after the measured value of mercury concentration reaches above-mentioned first regulation mercury concentration, with the increase of mercury concentration in exhaust, from it is defined most
Small value linearly increases activated carbon quantity delivered, when the measured value of mercury concentration reaches the second regulation mercury concentration, supplies activated carbon
Measure as the quantity delivered of defined maximum, increased in activated carbon quantity delivered as defined in after maximum, relative to mercury in exhaust
The increase of concentration, is remained activated carbon quantity delivered with its defined maximum constant.Scheme shown in Fig. 4 (E) is to be combined with
Fig. 4 (A) and the scheme shown in (C) scheme, have feature, the effect of respective scheme concurrently.
Scheme shown in Fig. 4 (F) is following scheme:In exhaust the measured value of mercury concentration from zero or less than can determination limit most
The value of small value is to the first scope for providing mercury concentration, on the basis of the activated carbon quantity delivered (the first quantity delivered) of defined minimum value
Upper supply activated carbon, after the measured value of mercury concentration reaches above-mentioned first regulation mercury concentration, with the increase of mercury concentration in exhaust,
Activated carbon quantity delivered is linearly increased from the first quantity delivered, the second quantity delivered corresponding to the second regulation mercury concentration is increased to, this
Afterwards relative to the increase of mercury concentration in exhaust, activated carbon quantity delivered is remained with the second quantity delivered it is constant, in addition, reaching the
During three regulation mercury concentration, activated carbon quantity delivered is linearly increased from the second quantity delivered, is increased to corresponding to the 4th regulation mercury concentration
The 3rd quantity delivered, thereafter relative to the increase of mercury concentration in exhaust, activated carbon quantity delivered is remained into perseverance with the 3rd quantity delivered
It is fixed, relative to the increase of mercury concentration in such exhaust, repeat activated carbon quantity delivered remaining constant and increase, in activated carbon
Quantity delivered increase to as defined in after maximum, relative to the increase of mercury concentration in exhaust, with its defined maximum by activity
Charcoal quantity delivered remains constant.Scheme shown in Fig. 4 (F) is the scheme for being combined with Fig. 4 (B) and the scheme shown in (D), is had concurrently each
From scheme feature, effect.
Scheme shown in Fig. 4 (G) is following scheme:Phase untill the measured value of mercury concentration reaches regulation mercury concentration in exhaust
Between, with the increase of mercury concentration in exhaust, activated carbon quantity delivered is linearly increased from defined minimum value, in the measure of mercury concentration
When value reaches above-mentioned regulation mercury concentration, activated carbon quantity delivered is steppingly increased into defined maximum, in activated carbon supply
Amount is increased to after defined maximum, relative to the increase of mercury concentration in exhaust, is supplied activated carbon with its defined maximum
Remained to amount constant.This is following corresponding relation:The measured value of the mercury concentration regulation more moderate than relatively in exhaust
Value it is low when, with the increase of mercury concentration in exhaust, activated carbon quantity delivered is continuously increased from defined minimum value, so as to
Relative to being controlled in exhaust, activated carbon, the measured value of mercury concentration in exhaust are supplied with appropriate amount mercury concentration very fine
When the regulation mercury concentration more moderate than relatively is high, it is defined maximum to make activated carbon quantity delivered, can effectively utilize regulation
Multiple means of the quantity delivered of activated carbon, activated carbon quantity delivered is controlled with appropriate amount.
Scheme shown in Fig. 4 (H) is following scheme:The first regulation mercury concentration of measured value arrival of mercury concentration is in exhaust
During only, with the increase of mercury concentration in exhaust, activated carbon quantity delivered is linearly increased from defined minimum value, in mercury concentration
When measured value reaches above-mentioned first regulation mercury concentration, it is defined first quantity delivered to make activated carbon quantity delivered, in the survey of mercury concentration
Definite value reach second provide mercury concentration untill during, activated carbon quantity delivered is remained with defined first quantity delivered it is constant,
When the measured value of mercury concentration reaches above-mentioned second regulation mercury concentration, activated carbon quantity delivered is steppingly increased into defined maximum
Value, increased in activated carbon quantity delivered as defined in after maximum, relative to the increase of mercury concentration in exhaust, with as defined in it most
Big value remains activated carbon quantity delivered constant.Scheme shown in Fig. 4 (H) is to be combined in the scheme shown in Fig. 4 (G) in following
The scheme of appearance:In exhaust the measured value of mercury concentration for moderate defined scope relatively (from the first regulation mercury concentration to
The scope of second regulation mercury concentration) in, activated carbon quantity delivered is remained with the first regulation quantity delivered constant, can be controlled
System, the supply of activated carbon is supplied with more appropriate amount.
In addition, in control device according to the mercury concentration measurement for predefining mercury densimeter and the correspondence of activated carbon quantity delivered
When relation controls activated carbon quantity delivered, the side of predetermined mercury concentration measurement and the corresponding relation of activated carbon quantity delivered is used as
The scheme of case or following corresponding relation:Mercury concentration is zero or determining less than mercury densimeter in the exhaust of measure
When limiting minimum value or be lower than predetermined setting, without the supply of activated carbon, mercury concentration ratio zero or it can be surveyed in exhaust
When fixed limit minimum value or high predetermined setting, with the increase of mercury concentration in exhaust, gradually increase activated carbon quantity delivered.
In addition, when the increase of mercury concentration in exhaust increases activated carbon quantity delivered, can linearly increase, can also be step by step
Increase.
In addition, as the scheme beyond above-mentioned corresponding relation, can also corresponding relation as follows scheme:In the exhaust of measure
Middle mercury concentration be zero or less than mercury densimeter can determination limit minimum value or it is lower than predetermined first regulation mercury concentration when, no
Carry out activated carbon supply, in exhaust mercury concentration ratio zero or can determination limit minimum value or it is predetermined first regulation mercury concentration
High and lower than the predetermined second regulation mercury concentration scope, with the increase of mercury concentration in exhaust, gradually increases activated carbon
Quantity delivered, the measured value of the mercury concentration scope higher than the above-mentioned second regulation mercury concentration in exhaust, it is rule to make activated carbon quantity delivered
Fixed quantity delivered keeps constant.In addition, when the increase of mercury concentration in exhaust increases activated carbon quantity delivered, can be linear
Ground increase, can also increase step by step.
In the present invention, activity is being controlled according to the mercury concentration and the corresponding relation of activated carbon quantity delivered that predefine in being vented
During charcoal quantity delivered, the increase for the activated carbon quantity delivered from its minimum value to maximum uses various schemes, and this gives in Fig. 4
To illustrate, and minimum value and defined maximum as defined in how determining, as one example, just increased using Fig. 4 (E) scheme
The situation of big activated carbon quantity delivered is as described below.That is, mercury concentration measurement and the corresponding relation of activated carbon quantity delivered is as follows
Scheme.The program is:In exhaust the measured value of mercury concentration from zero or less than can determination limit minimum value value to first regulation
The scope of mercury concentration, supplies activated carbon, in the measured value of mercury concentration on the basis of the activated carbon quantity delivered of defined minimum value
Reach after above-mentioned first regulation mercury concentration, with the increase of mercury concentration in exhaust, activity is linearly increased from defined minimum value
Charcoal quantity delivered, when the measured value of mercury concentration reaches the second regulation mercury concentration, it is defined maximum to make activated carbon quantity delivered
Quantity delivered, after activated carbon quantity delivered increases to defined maximum, relative to the increase of mercury concentration in exhaust, is provided with it
Maximum activated carbon quantity delivered is remained it is constant.
Inventor is used to determine using the exhaust gas treatment device shown in Fig. 2 during processing to carrying out the exhaust containing mercury
All conditions of minimum value and defined maximum are studied as defined in stating.In the research, measure dust collect plant entrance (on
Swim side) exhaust in mercury concentration, for the mercury concentration in the exhaust in the mercury concentration measurement and the downstream of dust collect plant
The situation that the ratio (upstream side mercury concentration rate) of setting value changes in the range of 20 times ~ 200 times, is simulated based on activated carbon
Mercury adsorbs removing process, has obtained the defined minimum value of activated carbon quantity delivered and the proper range of defined maximum.For
Above-mentioned upstream side mercury concentration rate, will divide into multiple stages between 20 times ~ 200 times, changes successively, each in each differentiation scope
Appropriate scope is obtained to defined minimum value and defined maximum.The result of gained is as shown in table 1.
In table 1, such as prediction contains above-mentioned upstream side mercury concentration rate for 100 times less than 120 times of scope
The exhaust of mercury from fire grate go out when, as relative to processing extraction flow activated carbon be blown into the activated carbon quantity delivered that weight is determined
Defined minimum value be set as 60 ~ 200mg/Nm3, the defined maximum of activated carbon quantity delivered is set as 300 ~ 1000mg/
Nm3。
[table 1]
In the table 1, for each differentiation scope of above-mentioned upstream side mercury concentration rate, the lower limit of defined minimum value correspond to than
The low situation of mercury concentration measurement or the situation higher than the mercury concentration set point in the downstream of dust collect plant in exhaust, it is defined
The upper limit of minimum value corresponds to the mercury concentration in the situation higher than mercury concentration measurement in exhaust or the downstream than dust collect plant
The low situation of setting value.
In addition, in table 1, for each differentiation scope of above-mentioned upstream side mercury concentration rate, the lower limit of defined maximum
Corresponding to than the low situation of mercury concentration measurement or the feelings higher than the mercury concentration set point in the downstream of dust collect plant in exhaust
Condition, the upper limit of defined maximum corresponds to the situation higher than mercury concentration measurement in exhaust or the downstream than dust collect plant
The low situation of mercury concentration set point.
In this way, the defined minimum value of setting activated carbon quantity delivered, so that activated carbon is attached to the pocket type of dust collect plant
Dust arrester to be sufficiently formed adsorption layer in advance, when discharging the exhaust of the mercury containing high concentration, can be by the work that has been formed
Property charcoal adsorption layer and the activated carbon being now blown into rapidly adsorb removing mercury, and mercury concentration can be reduced to substantially low concentration.
In addition, the defined maximum of setting activated carbon quantity delivered, so as to fully adsorb the mercury for removing high concentration,
And without the glut of activated carbon.
Hereinafter, it will illustrate on embodiments of the invention together with comparative example.
Embodiment
Carry out mercury to the exhaust discharged from incinerator with the exhaust gas treatment device shown in Fig. 1 ~ Fig. 3 removes place to go
Reason, it is thus identified that effect.For the exhaust discharged from incinerator, the capacity from chimney is 10000Nm3/ h, chimney
Mercury concentration is calculated as 50 μ g/Nm with 1 time average in interior exhaust3Below.Additionally, it is desirable to by mercury concentration measurement in the short time
Maximum mercury concentration instantaneous value (being referred to as peak measured value) in the phenomenon inside sharply increased is suppressed to low.Activated carbon quantity delivered (mg/
Nm3) it is blown into weight determination as the activated carbon relative to processing extraction flow.
The peak measured value of the mercury concentration of bag collector entrance in embodiment, comparative example, the peak of the mercury concentration of chimney are surveyed
Definite value is shown in table 2.
< comparative examples >
In the exhaust flow path of bag collector upstream side, with relative to capacity (Nm3/ h) it is always the quantity delivered of constant basis
50mg/Nm3Activated carbon is blown into, the mercury concentration in the exhaust of usual time chimney is 5 μ g/Nm3Below-dry.Depending on being supplied to
The variation of rubbish property in incinerator, sometimes the mercury concentration of bag collector entrance change, the mercury concentration of chimney rises.
Maximum 90 μ g/Nm are observed in chimney3The peak measured value of-dry mercury concentration.
The > of < embodiments 1
Using the exhaust gas treatment device shown in Fig. 1 in embodiment 1, the processing of the exhaust containing mercury has been carried out.It is used as dust collect plant
Downstream, determine chimney exhaust in mercury concentration, utilize the chimney mercury concentration and the correspondence of activated carbon quantity delivered shown in Fig. 5
Relation obtains activated carbon quantity delivered, has supplied activated carbon.As shown in figure 5, in the μ g/Nm of chimney mercury concentration ratio 103When-dry is low, make
Activated carbon quantity delivered is the constant 50mg/Nm as minimum value3, in the μ g/Nm of chimney mercury concentration ratio 103- dry height and 40 μ g/ of ratio
Nm3When-dry is low, activated carbon quantity delivered is gradually increased with the increase of mercury concentration, in the μ g/Nm of chimney mercury concentration ratio 403- dry is high
When, it is the constant 500mg/Nm as maximum to make activated carbon quantity delivered3。
Depending on the variation of the rubbish property supplied, the mercury concentration of bag collector entrance changes, but most
In the case of height, the peak measured value of the mercury concentration of chimney is also suppressed to 70 μ g/Nm3-dry。
The > of < embodiments 2
Using the exhaust gas treatment device shown in Fig. 2 in embodiment 2, the processing of the exhaust containing mercury has been carried out.Determine pocket type dust
Mercury concentration in the exhaust of device entrance, utilizes the bag collector entrance mercury concentration and the correspondence of activated carbon quantity delivered shown in Fig. 6
Relation obtains activated carbon quantity delivered, has supplied activated carbon.As shown in fig. 6, in the μ g/ of bag collector entrance mercury concentration ratio 100
Nm3When-dry is low, it is the constant 50mg/Nm as minimum value to make activated carbon quantity delivered3, in bag collector entrance mercury concentration
Than 100 μ g/Nm3- dry height and 700 μ g/Nm of ratio3When-dry is low, activated carbon quantity delivered is gradually increased with the increase of mercury concentration,
The μ g/Nm of bag collector entrance mercury concentration ratio 7003When-dry is high, make activated carbon quantity delivered to be constant as maximum
500mg/Nm3。
Depending on the variation of the rubbish property supplied, the mercury concentration of bag collector entrance changes, but most
In the case of height, the peak measured value of the mercury concentration of chimney can also be suppressed to 25 μ g/Nm3-dry。
The > of < embodiments 3
Using the exhaust gas treatment device shown in Fig. 3 in embodiment 3, the processing of the exhaust containing mercury has been carried out.Determine pocket type dust
Mercury concentration in the exhaust of device entrance determines the mercury concentration in the exhaust of chimney, utilized to control the base unit weight of activated carbon quantity delivered
The corresponding relation of bag collector entrance mercury concentration and activated carbon quantity delivered shown in Fig. 6 controls the base unit weight of activated carbon quantity delivered,
Using the corresponding relation supplement increase and decrease activated carbon quantity delivered of the chimney mercury concentration shown in Fig. 5 and activated carbon quantity delivered, carried out with this
Control.
Depending on the variation of the rubbish property supplied, the mercury concentration of bag collector entrance changes, but most
In the case of height, the peak measured value of the mercury concentration of chimney can also be suppressed to 15 μ g/Nm3-dry。
[table 2]
Unit:μg/Nm3-dry O212% scaled value
。
Description of reference numerals
1 stove (incinerator)
2 boilers
3 activated carbon feedways
4 dust collect plants (bag collector)
5 mercury densimeters
5A the first mercury densimeters
5B the second mercury densimeters
6 chimneys
7 control devices.
Claims (24)
1. exhaust gas treatment device, including:To by fire grate go out containing mercury exhaust carry out dust removal process dust collect plant, and to will
It is vented the activated carbon feedway that the exhaust flow path for being oriented to dust collect plant from stove is blown into activated carbon, it is characterised in that
Including:The downstream mercury densimeter of the mercury concentration in exhaust is determined in the downstream of dust collect plant, and control activated carbon is supplied
To the control device of the activated carbon quantity delivered of device,
Control device controls activated carbon quantity delivered so that more than minimum value same as defined in activated carbon quantity delivered is maintained
When, according to the mercury concentration measurement of downstream mercury densimeter, make above-mentioned dust collect plant downstream exhaust in mercury concentration be
Below setting value.
2. exhaust gas treatment device, including:To from fire grate go out containing mercury exhaust carry out dust removal process dust collect plant and to will
It is vented the activated carbon feedway that the exhaust flow path for being oriented to dust collect plant from stove is blown into activated carbon, it is characterised in that
Including:The upstream side mercury densimeter of mercury concentration in the downstream of stove and the measure exhaust of the upstream side of dust collect plant and control
The control device of the activated carbon quantity delivered of preparing active carbon feedway,
Control device controls activated carbon quantity delivered so that more than minimum value same as defined in activated carbon quantity delivered is maintained
When, according to the mercury concentration measurement of upstream side mercury densimeter, make above-mentioned dust collect plant downstream exhaust in mercury concentration be
Below setting value.
3. exhaust gas treatment device, including:To from fire grate go out containing mercury exhaust carry out dust removal process dust collect plant and to will
It is vented the activated carbon feedway that the exhaust flow path for being oriented to dust collect plant from stove is blown into activated carbon, it is characterised in that
Including:Determined in the downstream of stove and the upstream side of dust collect plant the mercury concentration in exhaust upstream side mercury densimeter,
The downstream of dust collect plant determines the downstream mercury densimeter of the mercury concentration in exhaust and the activity of control activated carbon feedway
The control device of charcoal quantity delivered,
Control device controls activated carbon quantity delivered so that more than minimum value same as defined in activated carbon quantity delivered is maintained
When, according to the mercury concentration measurement of upstream side mercury densimeter and the mercury concentration measurement of downstream mercury densimeter, make above-mentioned dust
Mercury concentration in the exhaust in the downstream of device is below setting value.
4. the exhaust gas treatment device any one of claim 1 ~ 3, wherein, control device upstream side mercury densimeter or under
When swimming the mercury concentration measurement of side mercury densimeter to be more than regulation mercury concentration, activated carbon quantity delivered is remained into defined maximum
The mode of value is controlled.
5. the exhaust gas treatment device described in claim 1, wherein, control device is in the dust collect plant based on downstream mercury densimeter
The mercury concentration measurement in downstream relative to the ratio of the mercury concentration set point in the exhaust in the downstream of dust collect plant be pre-
When more than the ratio first determined, the mode that activated carbon quantity delivered is remained into defined maximum is controlled, above-mentioned advance
The ratio of determination is defined in the range of 0.4 ~ 0.8.
6. the exhaust gas treatment device described in claim 2, wherein, control device is in the dust collect plant based on upstream side mercury densimeter
Upstream side exhaust in mercury concentration measurement relative to the mercury concentration set point in the exhaust in the downstream of dust collect plant
When ratio is more than predetermined ratio, the mode that activated carbon quantity delivered is remained into defined maximum is controlled,
Above-mentioned predetermined ratio is defined in the range of 20 ~ 200.
7. the exhaust gas treatment device described in claim 3, wherein, control device is in the dust collect plant based on downstream mercury densimeter
Downstream exhaust in mercury concentration measurement relative to the mercury concentration set point in the exhaust in the downstream of dust collect plant
Downstream mercury concentration rate be predetermined ratio more than when, or the dust collect plant based on upstream side mercury densimeter upstream side
Exhaust in upstream side mercury of the mercury concentration measurement relative to the mercury concentration set point in the exhaust in the downstream of dust collect plant
When concentration rate is more than predetermined ratio, the mode that activated carbon quantity delivered is remained into defined maximum is controlled
System, above-mentioned predetermined downstream mercury concentration rate is defined in the range of 0.4 ~ 0.8, above-mentioned predetermined upstream side
Mercury concentration rate is defined in the range of 20 ~ 200.
8. the exhaust gas treatment device any one of claim 1 ~ 7, wherein, control device will be used as relative to processing exhaust
The defined minimum value that the activated carbon of flow is blown into the activated carbon quantity delivered that weight is determined is set as 10 ~ 200mg/Nm3Carry out
Control.
9. the exhaust gas treatment device any one of claim 4 ~ 7, wherein, control device will be used as relative to processing exhaust
The defined maximum that the activated carbon of flow is blown into the activated carbon quantity delivered that weight is determined is set as 300 ~ 1000mg/Nm3Enter
Row control.
10. the exhaust gas treatment device described in claim 9, wherein, control device will be used as the work relative to processing extraction flow
The defined minimum value that property charcoal is blown into the activated carbon quantity delivered that weight is determined is set as 10 ~ 200mg/Nm3It is controlled.
11. the exhaust gas treatment device any one of claim 1 ~ 3, wherein, mercury concentration of the control device in exhaust is surveyed
Definite value from zero or less than can determination limit minimum value value to first regulation mercury concentration scope, in the activity of defined minimum value
Activated carbon is supplied on the basis of charcoal quantity delivered, after mercury concentration measurement reaches above-mentioned first regulation mercury concentration, as mercury is dense
The increase of measured value is spent, activated carbon quantity delivered is linearly increased from defined minimum value, reaching second in mercury concentration measurement advises
When determining mercury concentration, make the quantity delivered that activated carbon quantity delivered is defined maximum, above-mentioned second rule are reached in mercury concentration measurement
Determine after mercury concentration, relative to the increase of mercury concentration measurement, activated carbon quantity delivered is remained by perseverance with its defined maximum
It is fixed.
12. the exhaust gas treatment device any one of claim 1 ~ 3, wherein, mercury concentration of the control device in exhaust is surveyed
Definite value from zero or less than can determination limit minimum value value to first regulation mercury concentration scope, using defined minimum value as
Activated carbon is supplied on the basis of the activated carbon quantity delivered of first quantity delivered, it is dense to reach above-mentioned first regulation mercury in mercury concentration measurement
When spending, activated carbon quantity delivered is increased into defined second quantity delivered step by step, reaching second in mercury concentration measurement provides mercury
Scope untill concentration, activated carbon quantity delivered is remained with the second quantity delivered it is constant, in addition, reaching the in mercury concentration measurement
During two regulation mercury concentration, in the way of the 3rd quantity delivered as defined in activated carbon quantity delivered is increased to, with mercury concentration measurement
Increase, repeats increase activated carbon quantity delivered step by step, after activated carbon quantity delivered increases to defined maximum, relative to mercury
The increase of concentration measurement, is remained activated carbon quantity delivered with its defined maximum constant.
, will 13. exhaust gas treatment method, methods described carries out dust removal process with dust collect plant to the exhaust containing mercury gone out by fire grate
Activated carbon is blown into from activated carbon feedway to be vented the exhaust flow path that dust collect plant is oriented to from stove, it is characterised in that
Including:The determination step of the mercury concentration in exhaust is determined with downstream mercury densimeter in the downstream of dust collect plant, and is used
The rate-determining steps of the activated carbon quantity delivered of control device control activated carbon feedway,
Activated carbon quantity delivered is controlled in rate-determining steps so that more than minimum value same as defined in activated carbon quantity delivered is maintained
When, according to the mercury concentration measurement of downstream mercury densimeter, make above-mentioned dust collect plant downstream exhaust in mercury concentration be
Below setting value.
, will 14. exhaust gas treatment method, methods described carries out dust removal process with dust collect plant to the exhaust containing mercury gone out by fire grate
Activated carbon is blown into from activated carbon feedway to be vented the exhaust flow path that dust collect plant is oriented to from stove, it is characterised in that
Including:The survey of the mercury concentration in the measure exhaust of upstream side mercury densimeter in the downstream of stove and the upstream side of dust collect plant
Determine step, and control with control device the rate-determining steps of the activated carbon quantity delivered of activated carbon feedway,
Activated carbon quantity delivered is controlled in rate-determining steps so that more than minimum value same as defined in activated carbon quantity delivered is maintained
When, according to the mercury concentration measurement of upstream side mercury densimeter, make above-mentioned dust collect plant downstream exhaust in mercury concentration be
Below setting value.
, will 15. exhaust gas treatment method, methods described carries out dust removal process with dust collect plant to the exhaust containing mercury gone out by fire grate
Activated carbon is blown into from activated carbon feedway from activated carbon feedway to be vented the exhaust flow path that dust collect plant is oriented to from stove, its
It is characterised by,
Including:The same of the mercury concentration in exhaust is determined with upstream side mercury densimeter in the downstream of stove and the upstream side of dust collect plant
When the determination step of the mercury concentration in exhaust is determined with downstream mercury densimeter in the downstream of dust collect plant, and use control device
The rate-determining steps of the activated carbon quantity delivered of activated carbon feedway are controlled,
Activated carbon quantity delivered is controlled in rate-determining steps so that more than minimum value same as defined in activated carbon quantity delivered is maintained
When, according to the mercury concentration measurement of upstream side mercury densimeter and the mercury concentration measurement of downstream mercury densimeter, make above-mentioned dust
Mercury concentration in the exhaust in the downstream of device is below setting value.
16. the exhaust gas treatment method any one of claim 13 ~ 15, wherein, rate-determining steps are in upstream side mercury densimeter
Or the mercury concentration measurement of downstream mercury densimeter is when providing more than mercury concentration, activated carbon quantity delivered to be remained defined
The mode of maximum is controlled.
17. the exhaust gas treatment method described in claim 13, wherein, rate-determining steps are filled in the dust based on downstream mercury densimeter
Mercury concentration measurement in the exhaust in the downstream put is relative to the mercury concentration set point in the exhaust in the downstream of dust collect plant
Ratio to be more than predetermined ratio when, by activated carbon quantity delivered remain as defined in the mode of maximum controlled
System, above-mentioned predetermined ratio is defined in the range of 0.4 ~ 0.8.
18. the exhaust gas treatment method described in claim 14, wherein, rate-determining steps are filled in the dust based on upstream side mercury densimeter
Mercury concentration measurement in the exhaust for the upstream side put is relative to the mercury concentration set point in the exhaust in the downstream of dust collect plant
Ratio to be more than predetermined ratio when, by activated carbon quantity delivered remain as defined in the mode of maximum controlled
System, above-mentioned predetermined ratio is defined in the range of 20 ~ 200.
19. the exhaust gas treatment method described in claim 15, wherein, rate-determining steps are filled in the dust based on downstream mercury densimeter
Mercury concentration measurement in the exhaust in the downstream put is relative to the mercury concentration set point in the exhaust in the downstream of dust collect plant
Downstream mercury concentration rate to be more than predetermined ratio when, or the dust collect plant based on upstream side mercury densimeter upstream
Upstream side of the mercury concentration measurement relative to the mercury concentration set point in the exhaust in the downstream of dust collect plant in the exhaust of side
When mercury concentration rate is more than predetermined ratio, the mode that activated carbon quantity delivered is remained into defined maximum is carried out
Control, above-mentioned predetermined downstream mercury concentration rate is defined in the range of 0.4 ~ 0.8, above-mentioned predetermined upstream
Side mercury concentration rate is defined in the range of 20 ~ 200.
20. the exhaust gas treatment method any one of claim 13 ~ 19, wherein, rate-determining steps will be used as relative to processing
The defined minimum value that the activated carbon of extraction flow is blown into the activated carbon quantity delivered that weight is determined is set as 10 ~ 200mg/Nm3
It is controlled.
21. the exhaust gas treatment method any one of claim 16 ~ 20, wherein, rate-determining steps will be used as relative to processing
The defined maximum that the activated carbon of extraction flow is blown into the activated carbon quantity delivered that weight is determined is set as 300 ~ 1000mg/
Nm3It is controlled.
22. the exhaust gas treatment method described in claim 21, wherein, rate-determining steps will be used as the work relative to processing extraction flow
The defined minimum value that property charcoal is blown into the activated carbon quantity delivered that weight is determined is set as 10 ~ 200mg/Nm3It is controlled.
23. the exhaust gas treatment method any one of claim 13 ~ 15, wherein, mercury concentration of the rate-determining steps in exhaust
Measured value from zero or less than can determination limit minimum value value to first regulation mercury concentration scope, in the work of defined minimum value
Property charcoal quantity delivered on the basis of supply activated carbon, mercury concentration measurement reach it is above-mentioned first regulation mercury concentration after, with mercury
The increase of concentration measurement, activated carbon quantity delivered is linearly increased from defined minimum value, and second is reached in mercury concentration measurement
When providing mercury concentration, the quantity delivered for making activated carbon quantity delivered be defined maximum reaches above-mentioned second in mercury concentration measurement
Provide after mercury concentration, relative to the increase of mercury concentration measurement, remained activated carbon quantity delivered with its defined maximum
It is constant.
24. the exhaust gas treatment method any one of claim 13 ~ 15, wherein, mercury concentration of the rate-determining steps in exhaust
Measured value from zero or less than can determination limit minimum value value to first regulation mercury concentration scope, with defined minimum value make
To supply activated carbon on the basis of the activated carbon quantity delivered of the first quantity delivered, above-mentioned first regulation mercury is reached in mercury concentration measurement
During concentration, activated carbon quantity delivered is increased into defined second quantity delivered step by step, reaching second in mercury concentration measurement provides
Scope untill mercury concentration, activated carbon quantity delivered is remained with the second quantity delivered it is constant, in addition, mercury concentration measurement reach
During the second regulation mercury concentration, in the way of the 3rd quantity delivered as defined in activated carbon quantity delivered is increased to, with mercury concentration measurement
Increase, increase activated carbon quantity delivered is repeated step by step, increased in activated carbon quantity delivered as defined in after maximum, relative to
The increase of mercury concentration measurement, is remained activated carbon quantity delivered with its defined maximum constant.
Applications Claiming Priority (5)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2015029417 | 2015-02-18 | ||
JP2015-029417 | 2015-02-18 | ||
JP2015225556 | 2015-11-18 | ||
JP2015-225556 | 2015-11-18 | ||
PCT/JP2016/053100 WO2016132894A1 (en) | 2015-02-18 | 2016-02-02 | Exhaust gas treatment device and exhaust gas treatment method |
Publications (1)
Publication Number | Publication Date |
---|---|
CN107249716A true CN107249716A (en) | 2017-10-13 |
Family
ID=56692211
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201680011095.4A Pending CN107249716A (en) | 2015-02-18 | 2016-02-02 | Exhaust gas treatment device and exhaust gas treatment method |
Country Status (5)
Country | Link |
---|---|
JP (3) | JP6016205B1 (en) |
CN (1) | CN107249716A (en) |
MY (1) | MY180066A (en) |
SG (3) | SG10201709322PA (en) |
WO (1) | WO2016132894A1 (en) |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN111185054A (en) * | 2018-11-14 | 2020-05-22 | 中国石油化工股份有限公司 | Recovery pretreatment device and method for polyolefin-containing organic gas |
CN111919116A (en) * | 2018-04-12 | 2020-11-10 | 日立造船株式会社 | Mercury concentration measuring device, exhaust gas treatment device, and exhaust gas treatment method |
CN112165981A (en) * | 2018-06-06 | 2021-01-01 | 日立造船株式会社 | Exhaust gas treatment device |
CN113727772A (en) * | 2019-04-11 | 2021-11-30 | 日立造船株式会社 | Exhaust gas treatment device and exhaust gas treatment method |
Families Citing this family (16)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP6703748B2 (en) * | 2016-09-12 | 2020-06-03 | Jfeエンジニアリング株式会社 | Exhaust gas treatment device and exhaust gas treatment method |
JP2018135248A (en) * | 2017-02-23 | 2018-08-30 | 太平洋セメント株式会社 | Method and system for removing mercury from exhaust gas of cement kiln |
JP6872169B2 (en) * | 2017-03-31 | 2021-05-19 | Jfeエンジニアリング株式会社 | Exhaust gas treatment equipment and exhaust gas treatment method |
JP6958158B2 (en) * | 2017-09-15 | 2021-11-02 | 宇部興産株式会社 | Exhaust gas treatment equipment and exhaust gas treatment method |
JP2019063765A (en) * | 2017-10-04 | 2019-04-25 | Jfeエンジニアリング株式会社 | Exhaust gas treatment apparatus and exhaust gas treatment method |
CN108554115B (en) * | 2018-01-29 | 2019-07-12 | 中冶长天国际工程有限责任公司 | A kind of flue gas purification system being related to multi-process and its control method |
JP7047487B2 (en) * | 2018-03-12 | 2022-04-05 | Jfeエンジニアリング株式会社 | Exhaust gas treatment equipment and exhaust gas treatment method |
JP7047488B2 (en) * | 2018-03-12 | 2022-04-05 | Jfeエンジニアリング株式会社 | Exhaust gas treatment equipment and exhaust gas treatment method |
JP6439207B1 (en) | 2018-06-29 | 2018-12-19 | 三菱重工環境・化学エンジニアリング株式会社 | Exhaust gas mercury removal system |
KR102131116B1 (en) * | 2018-11-30 | 2020-07-07 | (주)에프테크 | Exhaust gas measuring system and apparatus based on monitoring of operating state about processing of exhaust gas |
JP7299721B2 (en) * | 2019-03-14 | 2023-06-28 | 荏原環境プラント株式会社 | Exhaust gas treatment system and exhaust gas treatment method |
JP7175835B2 (en) | 2019-04-16 | 2022-11-21 | 荏原環境プラント株式会社 | Incineration system with stoker type incinerator |
JP6846778B2 (en) * | 2019-07-23 | 2021-03-24 | 株式会社プランテック | Mercury removal device and method in exhaust gas |
JP7214594B2 (en) * | 2019-08-22 | 2023-01-30 | 日立造船株式会社 | Exhaust gas treatment device and exhaust gas treatment method |
JP7203711B2 (en) * | 2019-10-04 | 2023-01-13 | 日立造船株式会社 | Exhaust gas treatment device and exhaust gas treatment method |
FR3117044B1 (en) * | 2020-12-04 | 2022-12-16 | Lab | Smoke demercurization process |
Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102015070A (en) * | 2008-04-25 | 2011-04-13 | 三菱重工业株式会社 | System for treating discharge gas and method of removing mercury from discharge gas |
CN103068469A (en) * | 2010-10-15 | 2013-04-24 | 三菱重工业株式会社 | System for processing mercury in exhaust gas |
JP2013136059A (en) * | 2013-03-28 | 2013-07-11 | Mitsubishi Materials Corp | Method and apparatus for treatment of kiln exhaust gas |
JP2014213308A (en) * | 2013-04-30 | 2014-11-17 | 株式会社タクマ | Mercury adsorbent charging device and mercury removal system using the same |
Family Cites Families (8)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH09308817A (en) * | 1996-05-22 | 1997-12-02 | Babcock Hitachi Kk | Method for treating exhaust gas and apparatus therefor |
JP5198786B2 (en) * | 2007-04-13 | 2013-05-15 | バブコック日立株式会社 | Exhaust gas purification method and apparatus |
JP2009291734A (en) * | 2008-06-06 | 2009-12-17 | Hitachi Plant Technologies Ltd | Apparatus and method for exhaust gas treatment |
JP5340125B2 (en) * | 2008-12-08 | 2013-11-13 | 太平洋セメント株式会社 | Cement kiln exhaust gas treatment apparatus and treatment method |
JP5239813B2 (en) * | 2008-12-11 | 2013-07-17 | 三菱マテリアル株式会社 | Kiln exhaust gas treatment method and treatment equipment |
JP6020085B2 (en) * | 2012-11-20 | 2016-11-02 | 栗田工業株式会社 | Acid gas stabilization method and combustion exhaust gas treatment facility |
JP6194840B2 (en) * | 2014-03-31 | 2017-09-13 | Jfeエンジニアリング株式会社 | Exhaust gas treatment apparatus and method |
CN107249717A (en) * | 2015-02-24 | 2017-10-13 | 日立造船株式会社 | The processing unit of burning and gas-exhausting |
-
2016
- 2016-02-02 SG SG10201709322PA patent/SG10201709322PA/en unknown
- 2016-02-02 WO PCT/JP2016/053100 patent/WO2016132894A1/en active Application Filing
- 2016-02-02 SG SG11201706561SA patent/SG11201706561SA/en unknown
- 2016-02-02 MY MYPI2017703033A patent/MY180066A/en unknown
- 2016-02-02 SG SG10201709324XA patent/SG10201709324XA/en unknown
- 2016-02-02 JP JP2016519397A patent/JP6016205B1/en active Active
- 2016-02-02 CN CN201680011095.4A patent/CN107249716A/en active Pending
- 2016-08-01 JP JP2016151440A patent/JP6070971B1/en active Active
- 2016-08-01 JP JP2016151491A patent/JP6124097B1/en active Active
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102015070A (en) * | 2008-04-25 | 2011-04-13 | 三菱重工业株式会社 | System for treating discharge gas and method of removing mercury from discharge gas |
CN103068469A (en) * | 2010-10-15 | 2013-04-24 | 三菱重工业株式会社 | System for processing mercury in exhaust gas |
JP2013136059A (en) * | 2013-03-28 | 2013-07-11 | Mitsubishi Materials Corp | Method and apparatus for treatment of kiln exhaust gas |
JP2014213308A (en) * | 2013-04-30 | 2014-11-17 | 株式会社タクマ | Mercury adsorbent charging device and mercury removal system using the same |
Cited By (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN111919116A (en) * | 2018-04-12 | 2020-11-10 | 日立造船株式会社 | Mercury concentration measuring device, exhaust gas treatment device, and exhaust gas treatment method |
CN111919116B (en) * | 2018-04-12 | 2022-11-08 | 日立造船株式会社 | Mercury concentration measuring device, exhaust gas treatment device, and exhaust gas treatment method |
CN112165981A (en) * | 2018-06-06 | 2021-01-01 | 日立造船株式会社 | Exhaust gas treatment device |
CN112165981B (en) * | 2018-06-06 | 2022-07-01 | 日立造船株式会社 | Exhaust gas treatment device |
CN111185054A (en) * | 2018-11-14 | 2020-05-22 | 中国石油化工股份有限公司 | Recovery pretreatment device and method for polyolefin-containing organic gas |
CN113727772A (en) * | 2019-04-11 | 2021-11-30 | 日立造船株式会社 | Exhaust gas treatment device and exhaust gas treatment method |
CN113727772B (en) * | 2019-04-11 | 2022-11-22 | 日立造船株式会社 | Exhaust gas treatment device and exhaust gas treatment method |
Also Published As
Publication number | Publication date |
---|---|
SG11201706561SA (en) | 2017-09-28 |
JPWO2016132894A1 (en) | 2017-04-27 |
JP6016205B1 (en) | 2016-10-26 |
JP6124097B1 (en) | 2017-05-10 |
SG10201709322PA (en) | 2018-01-30 |
SG10201709324XA (en) | 2018-01-30 |
JP2017094318A (en) | 2017-06-01 |
MY180066A (en) | 2020-11-20 |
WO2016132894A1 (en) | 2016-08-25 |
JP2017094319A (en) | 2017-06-01 |
JP6070971B1 (en) | 2017-02-01 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN107249716A (en) | Exhaust gas treatment device and exhaust gas treatment method | |
US9945557B2 (en) | Sorbents for coal combustion | |
TWI528997B (en) | System and method for protection of scr catalyst and control of multiple emissions | |
JP6194840B2 (en) | Exhaust gas treatment apparatus and method | |
TWI505867B (en) | System and method for protection of scr catalyst and control of multiple emissions | |
CN104748566B (en) | A kind of method of agglomeration for iron mine energy-saving and emission-reduction | |
CN104122906B (en) | The control method of the lime white straying quatity in fume treatment reaction tower | |
JP6315275B2 (en) | Exhaust gas treatment apparatus and exhaust gas treatment method | |
CN112105442B (en) | Exhaust gas mercury removal system | |
JP7047488B2 (en) | Exhaust gas treatment equipment and exhaust gas treatment method | |
JP6805788B2 (en) | Mercury recovery device and mercury recovery method | |
JP6539885B1 (en) | Exhaust gas mercury removal system | |
CN102614756A (en) | Limestone shielding situation diagnosis and treatment method of limestone-gypsum gas desulfurization system | |
JP7047487B2 (en) | Exhaust gas treatment equipment and exhaust gas treatment method | |
JP6872169B2 (en) | Exhaust gas treatment equipment and exhaust gas treatment method | |
JP6703748B2 (en) | Exhaust gas treatment device and exhaust gas treatment method | |
JP2006035123A (en) | Elution lowering method of harmful elements in fly ash | |
CN108267023B (en) | Nitrogen oxide emission control method and device | |
Zhijie et al. | Design and application of the Dry-FGD process in sanming steel No. 2 sintering plant | |
CN206191570U (en) | Desulfurization minimum discharge circulating fluidized bed boiler in stove | |
JP5483490B2 (en) | Dilution water amount management apparatus and dilution water amount management method | |
JP2021008674A (en) | Mercury recovery device and mercury recovery method | |
CN112827313A (en) | Coal-fired boiler fly ash modified self-adsorption flue gas demercuration device and method | |
CN106753682A (en) | A kind of fluidized bed furnace desulfurizer and sulfur method | |
JP2004285401A (en) | Method for reducing quantity of dust in main exhaust gas in sintering process |
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 | ||
RJ01 | Rejection of invention patent application after publication |
Application publication date: 20171013 |
|
RJ01 | Rejection of invention patent application after publication |