JP7047488B2 - Exhaust gas treatment equipment and exhaust gas treatment method - Google Patents

Exhaust gas treatment equipment and exhaust gas treatment method Download PDF

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JP7047488B2
JP7047488B2 JP2018044556A JP2018044556A JP7047488B2 JP 7047488 B2 JP7047488 B2 JP 7047488B2 JP 2018044556 A JP2018044556 A JP 2018044556A JP 2018044556 A JP2018044556 A JP 2018044556A JP 7047488 B2 JP7047488 B2 JP 7047488B2
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hydrogen chloride
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厚志 長尾
敦 平山
崇 三浦
祐人 臼井
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JFE Engineering Corp
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Description

本発明は、廃棄物焼却施設、セメント製造工場、火力発電所、非鉄金属製錬工場等の各種工場から排出される水銀を含む排ガスの処理装置及び排ガス処理方法に関する。 The present invention relates to an exhaust gas treatment device and an exhaust gas treatment method containing mercury emitted from various factories such as a waste incinerator, a cement manufacturing factory, a thermal power plant, and a non-ferrous metal smelting factory.

セメントキルン炉、非鉄金属製錬炉から排出される排ガスや、水銀を含んだ廃棄物が廃棄物焼却炉で焼却され排出される排ガス中に水銀が含まれることがあり、そのまま大気に放出されると、大気汚染を引き起こし問題となる。そこで、排ガス中の水銀を除去することが求められている。 Emissions emitted from cement kiln furnaces and non-ferrous metal smelting furnaces and wastes containing mercury may be contained in the exhaust gas emitted by incinerators in waste incinerators, and are released to the atmosphere as they are. It causes air pollution and becomes a problem. Therefore, it is required to remove mercury in the exhaust gas.

さらに、「水銀に関する水俣条約」が2013年に採択され、世界的な水銀管理強化の動きが進行している。この条約発効後、水銀排出規制対象施設に対して水銀の排出を抑制する対策が検討されている。水銀排出規制対象施設としては、石炭火力発電所、石炭焚きボイラ、非鉄金属製錬施設、廃棄物焼却施設、セメント製造施設が挙げられる。かかる状況において、これらの施設から排出される排ガス中の水銀を効率的に除去する処理方法の要望が高まっている。 Furthermore, the "Minamata Convention on Mercury" was adopted in 2013, and movements to strengthen mercury management worldwide are underway. After the entry into force of this treaty, measures to curb mercury emissions have been considered for facilities subject to mercury emission restrictions. Facilities subject to mercury emission control include coal-fired power plants, coal-fired boilers, non-ferrous metal smelting facilities, waste incinerator facilities, and cement manufacturing facilities. Under such circumstances, there is an increasing demand for a treatment method for efficiently removing mercury in the exhaust gas discharged from these facilities.

例えば、廃棄物焼却炉やボイラ火炉から排出される排ガス中の水銀の一般的な除去方法としては、排ガス中のダストを除塵するバグフィルタや電気集塵機へ排ガスを導くダクト内へ、バグフィルタ等に対して上流側位置で粉粒状の活性炭を吹き込み、該活性炭に水銀を吸着させ、この水銀を吸着した活性炭をダストとともにバグフィルタ等で集塵して排ガスから除去する方法が特許文献1で知られている。 For example, as a general method for removing mercury in exhaust gas discharged from a waste incinerator or a boiler furnace, a bag filter for removing dust in the exhaust gas, a bag filter for guiding the exhaust gas to an electrostatic precipitator, etc. On the other hand, Patent Document 1 knows a method in which powdered and granular activated carbon is blown at an upstream position, mercury is adsorbed on the activated carbon, and the activated carbon adsorbing the mercury is collected together with dust by a bag filter or the like and removed from the exhaust gas. ing.

また、排ガス中の酸性ガスを中和して除去するための消石灰に活性炭を予め混合した混合粉を用意し、この混合粉をバグフィルタの上流側でダクト内の排ガスに吹き込んで、酸性ガスと消石灰の反応生成物そして水銀を吸着した活性炭をダストとともにバグフィルタ等で集塵して処理する方法が用いられることもある。かくして、排ガス中の水銀は活性炭により吸着された後、バグフィルタ等で集塵除去される。 In addition, a mixed powder in which activated carbon is mixed in advance with slaked lime to neutralize and remove the acid gas in the exhaust gas is prepared, and this mixed powder is blown into the exhaust gas in the duct on the upstream side of the bag filter to combine with the acid gas. A method of collecting and treating the reaction product of acid gas and activated carbon adsorbed with mercury together with dust with a bag filter or the like may be used. Thus, mercury in the exhaust gas is adsorbed by activated carbon and then collected and removed by a bag filter or the like.

特開2010-221085JP 2010-221085

焼却炉で焼却処理される廃棄物の種類や、セメントキルン炉、非鉄金属製錬炉で製錬される原料の種類によっては、排ガス中の水銀濃度が一時的に高くなるような変動が生じる場合がある。この場合においても煙突から排出する排ガス中の水銀濃度を低く維持するためには、ダクトへ吹き込む活性炭の供給量を常時多量に吹き込む必要か、あるいは、消石灰と活性炭とが予め混合された混合粉をダクト内へ供給する際、混合粉の供給量を常時多量に吹き込む必要がある。 Depending on the type of waste incinerated in the incinerator and the type of raw material smelted in the cement kiln furnace and non-ferrous metal smelting furnace, the mercury concentration in the exhaust gas may fluctuate to temporarily increase. There is. Even in this case, in order to keep the concentration of mercury in the exhaust gas discharged from the chimney low, it is necessary to constantly inject a large amount of activated carbon to be blown into the duct, or a mixed powder in which slaked lime and activated carbon are mixed in advance is used. When supplying into the duct, it is necessary to constantly blow a large amount of the mixed powder.

このように、一時的に高くなる水銀濃度を想定して活性炭又は混合粉を常時多量にダクト内へ供給すると、上記一時的な時間帯を除いた多くの時間帯で活性炭そして混合粉を過度に供給する結果となってしまい、活性炭や混合粉の使用量が多大となり、排ガス処理費用が嵩むという問題や、集塵したダスト等の量が多大となり、除塵処理費用が嵩むという問題が生じる。 In this way, if a large amount of activated carbon or mixed powder is constantly supplied into the duct assuming a temporarily high mercury concentration, the activated carbon and mixed powder will be excessively supplied in many time zones other than the above-mentioned temporary time zone. As a result of the supply, the amount of activated carbon and mixed powder used becomes large, which causes a problem that the exhaust gas treatment cost increases, and the amount of collected dust and the like becomes large, which causes a problem that the dust removal treatment cost increases.

また、廃棄物焼却炉、セメントキルン炉、非鉄金属精錬炉から排出される排ガスに含まれる水銀は、主に塩化水銀と金属水銀の二種類の形態がある。活性炭の水銀に対する吸着性能は、これらの排ガス中の水銀形態や排ガス中の成分によって変化する。活性炭の水銀吸着性能に影響を与える排ガス中の成分としては酸素および塩化水素が挙げられる。 Further, mercury contained in the exhaust gas discharged from the waste incinerator, the cement kiln furnace, and the non-ferrous metal smelting furnace mainly has two types, mercury chloride and metallic mercury. The adsorption performance of activated carbon on mercury varies depending on the form of mercury in the exhaust gas and the components in the exhaust gas. Oxygen and hydrogen chloride are examples of components in the exhaust gas that affect the mercury adsorption performance of activated carbon.

本発明は、このような事情に鑑み、排ガス中の水銀を確実に吸着除去し、排ガス中の水銀濃度が変動してもこれに適切な活性炭量で活性炭を供給することができ、また、排ガス中の酸素濃度及び塩化水素の変動に対応して適切に活性炭による吸着除去処理を行うことができる排ガス処理装置及び排ガス処理方法を提供することを課題とする。 In view of such circumstances, the present invention can reliably adsorb and remove mercury in exhaust gas, and can supply activated carbon with an appropriate amount of activated carbon even if the concentration of mercury in exhaust gas fluctuates, and also exhaust gas. It is an object of the present invention to provide an exhaust gas treatment apparatus and an exhaust gas treatment method capable of appropriately performing adsorption removal treatment with activated carbon in response to fluctuations in oxygen concentration and hydrogen chloride in the medium.

本発明によると、上述の課題は、次の排ガス処理装置さらにはその方法により解決される。 According to the present invention, the above-mentioned problems are solved by the following exhaust gas treatment device and further by the method thereof.

[排ガス処理装置]
本発明における排ガス処理装置は、次の第一発明、第二発明そして第三発明のごとく構成され、いずれによっても上記課題は解決される。ここで、活性炭供給量(mg/Nm)は処理排ガス流量に対する活性炭吹込み重量として定められる。
[Exhaust gas treatment equipment]
The exhaust gas treatment device in the present invention is configured as the following first invention, second invention and third invention, and the above-mentioned problems are solved by any of them. Here, the amount of activated carbon supplied (mg / Nm 3 ) is determined as the weight of activated carbon blown with respect to the flow rate of the treated exhaust gas.

<第一発明>
炉から排出され水銀を含む排ガスを除塵処理する集塵装置と、炉から集塵装置へ排ガスを導く排ガス流路へ活性炭を吹き込む活性炭供給装置とを備える排ガス処理装置において、
炉の下流側でかつ集塵装置の上流側で、排ガス中の酸素濃度を測定する酸素濃度計と、排ガス中の塩化水素濃度を測定する塩化水素濃度計と、活性炭供給装置の活性炭供給量を制御する制御装置を備え、
制御装置は、酸素濃度計による酸素濃度測定値及び塩化水素濃度計による塩化水素濃度測定値に基づき、上記集塵装置の下流側での排ガス中の下流側水銀濃度を設定値以下とするように、酸素濃度測定値及び塩化水素濃度測定値と活性炭供給量との予め定める対応関係に基づき活性炭供給量を制御することを特徴とする排ガス処理装置。
<First invention>
In an exhaust gas treatment device including a dust collector that removes exhaust gas discharged from a furnace and contains mercury, and an activated carbon supply device that blows activated carbon into an exhaust gas flow path that guides the exhaust gas from the furnace to the dust collector.
On the downstream side of the furnace and on the upstream side of the dust collector, an oxygen concentration meter that measures the oxygen concentration in the exhaust gas, a hydrogen chloride concentration meter that measures the hydrogen chloride concentration in the exhaust gas, and the activated charcoal supply amount of the activated charcoal supply device. Equipped with a control device to control
The control device sets the downstream mercury concentration in the exhaust gas on the downstream side of the dust collector to the set value or less based on the oxygen concentration measurement value by the oxygen concentration meter and the hydrogen chloride concentration measurement value by the hydrogen chloride concentration meter. , An exhaust gas treatment device characterized in that the activated charcoal supply amount is controlled based on a predetermined correspondence relationship between the oxygen concentration measured value and the hydrogen chloride concentration measured value and the activated charcoal supply amount.

<第二発明>
炉から排出され水銀を含む排ガスを除塵処理する集塵装置と、炉から集塵装置へ排ガスを導く排ガス流路へ活性炭を吹き込む活性炭供給装置とを備える排ガス処理装置において、
炉の下流側でかつ集塵装置の上流側で、排ガス中の酸素濃度を測定する酸素濃度計と、排ガス中の塩化水素濃度を測定する塩化水素濃度計と、排ガス中の上流側水銀濃度を測定する上流側水銀濃度計と、活性炭供給装置の活性炭供給量を制御する制御装置を備え、
制御装置は、酸素濃度計による酸素濃度測定値と塩化水素濃度計による塩化水素濃度測定値及び上流側水銀濃度計による上流側水銀濃度測定値に基づき、上記集塵装置の下流側での排ガス中の下流側水銀濃度を設定値以下とするように、活性炭供給量を制御することを特徴とする排ガス処理装置。
<Second invention>
In an exhaust gas treatment device including a dust collector that removes exhaust gas discharged from a furnace and contains mercury, and an activated carbon supply device that blows activated carbon into an exhaust gas flow path that guides the exhaust gas from the furnace to the dust collector.
An oxygen concentration meter that measures the oxygen concentration in the exhaust gas, a hydrogen chloride concentration meter that measures the hydrogen chloride concentration in the exhaust gas, and an upstream mercury concentration in the exhaust gas on the downstream side of the furnace and on the upstream side of the dust collector. Equipped with an upstream mercury concentration meter to measure and a control device to control the amount of activated charcoal supplied by the activated charcoal supply device.
The control device is in the exhaust gas on the downstream side of the dust collector based on the oxygen concentration measurement value by the oxygen concentration meter, the hydrogen chloride concentration measurement value by the hydrogen chloride concentration meter, and the upstream mercury concentration measurement value by the upstream mercury concentration meter. An exhaust gas treatment device characterized in that the amount of activated charcoal supplied is controlled so that the mercury concentration on the downstream side of the water is set to a set value or less.

<第三発明>
炉から排出され水銀を含む排ガスを除塵処理する集塵装置と、炉から集塵装置へ排ガスを導く排ガス流路へ活性炭を吹き込む活性炭供給装置とを備える排ガス処理装置において、
炉の下流側でかつ集塵装置の上流側で、排ガス中の酸素濃度を測定する酸素濃度計と、排ガス中の塩化水素濃度を測定する塩化水素濃度計と、排ガス中の上流側水銀濃度を測定する上流側水銀濃度計と、集塵装置の下流側で排ガス中の水銀濃度を測定する下流側水銀濃度計と、活性炭供給装置の活性炭供給量を制御する制御装置を備え、
制御装置は、酸素濃度計による酸素濃度測定値と塩化水素濃度計による塩化水素濃度測定値と、上流側水銀濃度計による上流側水銀濃度測定値及び下流側水銀濃度計による下流側水銀濃度測定値に基づき、上記集塵装置の下流側での排ガス中の下流側水銀濃度を設定値以下とするように、活性炭供給量を制御することを特徴とする排ガス処理装置。
<Third invention>
In an exhaust gas treatment device including a dust collector that removes exhaust gas discharged from a furnace and contains mercury, and an activated carbon supply device that blows activated carbon into an exhaust gas flow path that guides the exhaust gas from the furnace to the dust collector.
An oxygen concentration meter that measures the oxygen concentration in the exhaust gas, a hydrogen chloride concentration meter that measures the hydrogen chloride concentration in the exhaust gas, and an upstream mercury concentration in the exhaust gas on the downstream side of the furnace and on the upstream side of the dust collector. It is equipped with an upstream mercury concentration meter to measure, a downstream mercury concentration meter to measure the mercury concentration in the exhaust gas on the downstream side of the dust collector, and a control device to control the activated charcoal supply amount of the activated charcoal supply device.
The control device is the oxygen concentration measurement value by the oxygen concentration meter, the hydrogen chloride concentration measurement value by the hydrogen chloride concentration meter, the upstream mercury concentration measurement value by the upstream mercury concentration meter, and the downstream mercury concentration measurement value by the downstream mercury concentration meter. Based on the above, an exhaust gas treatment device characterized in that the amount of activated charcoal supplied is controlled so that the concentration of mercury on the downstream side in the exhaust gas on the downstream side of the dust collector is set to a set value or less.

第一ないし第三発明においては、制御装置は、活性炭供給量を所定の最小値以上に維持するように制御することが好ましい。かかる制御により、集塵装置のバグフィルタには、活性炭の吸着層が常に形成されているようになるので、予め形成された上記吸着層による吸着除去作用とその際に吹き込まれる活性炭による吸着除去作用とにより水銀を速やかにかつ確実に吸着除去でき、集塵後の排ガスの水銀濃度を十分に低濃度とすることができる。また、第二又は第三発明においては、排ガス中の水銀濃度が所定値より低い場合には、活性炭供給量を所定の最小値に保つように制御することが好ましい。集塵装置のバグフィルタに活性炭の吸着層が常に形成されているようにして、上記所定値よりも高濃度の水銀を含む排ガスが排出された際にも、予め形成された上記吸着層による吸着除去作用とその際に吹き込まれる活性炭による吸着除去作用とにより水銀を速やかにかつ確実に吸着除去でき、集塵後の排ガスの水銀濃度を十分に低濃度とすることができる。 In the first to third inventions, it is preferable that the control device is controlled so as to maintain the amount of activated carbon supplied to a predetermined minimum value or more. By such control, the adsorption layer of activated carbon is always formed on the bag filter of the dust collector. Therefore, the adsorption removal action by the above-mentioned adsorption layer formed in advance and the adsorption removal action by the activated carbon blown at that time. As a result, mercury can be quickly and surely adsorbed and removed, and the mercury concentration of the exhaust gas after dust collection can be made sufficiently low. Further, in the second or third invention, when the mercury concentration in the exhaust gas is lower than a predetermined value, it is preferable to control the amount of activated carbon supply so as to keep it at a predetermined minimum value. The activated carbon adsorption layer is always formed on the bag filter of the dust collector, and even when the exhaust gas containing mercury having a concentration higher than the predetermined value is discharged, the adsorption layer is adsorbed by the preformed adsorption layer. The removal action and the adsorption removal action by the activated carbon blown at that time can quickly and surely adsorb and remove mercury, and the mercury concentration of the exhaust gas after dust collection can be made sufficiently low.

また、第二又は第三発明においては、制御装置は、上流側水銀濃度計による上流側水銀濃度測定値又は下流側水銀濃度計による下流側水銀濃度測定値が所定水銀濃度以上であるとき、活性炭供給量を所定の最大値に保つように制御することが好ましい。時間平均としてはさほど水銀濃度が高くないにも拘らず一時的に急激に水銀濃度が高くなったときに、この高い水銀濃度に合せて多量の活性炭を供給すると、その後の時間にわたり過剰に活性炭を供給してしまう結果になる。このような過剰な供給となることを、上記活性炭供給量を所定の最大値に保つように制御することにより防止できる。 Further, in the second or third invention, the control device is activated when the measured value of the upstream mercury concentration by the upstream mercury concentration meter or the measured value of the downstream mercury concentration by the downstream mercury concentration meter is equal to or higher than the predetermined mercury concentration. It is preferable to control the supply amount so as to keep it at a predetermined maximum value. When the mercury concentration rises temporarily and suddenly even though the mercury concentration is not so high as an hourly average, if a large amount of activated carbon is supplied in accordance with this high mercury concentration, the activated carbon will be excessively generated over the subsequent time. The result is that it will be supplied. Such an excessive supply can be prevented by controlling the amount of the activated carbon supply to be maintained at a predetermined maximum value.

また、第二又は第三発明において、活性炭供給量の最小値から最大値へ向けた増大に関しては、制御装置は、排ガス中の水銀濃度測定値が零又は測定可能な限界最小値未満の値から、第一の所定水銀濃度に達するまでの範囲には、所定の最小値の活性炭供給量のもとに活性炭を供給し、水銀濃度測定値が上記第一の所定水銀濃度に達した後に、水銀濃度測定値の増加にしたがって、所定の最小値から直線的に活性炭供給量を増大させ、水銀濃度測定値が第二の所定水銀濃度に達したときに、活性炭供給量を所定の最大値の供給量とし、水銀濃度測定値が上記第二の所定水銀濃度に達した後には、水銀濃度測定値の増加に対してその所定の最大値で活性炭供給量を一定に保つようにすることができる。 Further, in the second or third invention, regarding the increase from the minimum value to the maximum value of the activated carbon supply amount, the control device starts from the value where the measured mercury concentration in the exhaust gas is zero or less than the measurable limit minimum value. In the range until the first predetermined mercury concentration is reached, the activated charcoal is supplied under the predetermined minimum value of the activated charcoal supply amount, and after the measured mercury concentration reaches the first predetermined mercury concentration, the mercury As the concentration measurement value increases, the activated charcoal supply amount is linearly increased from the predetermined minimum value, and when the mercury concentration measurement value reaches the second predetermined mercury concentration, the activated charcoal supply amount is supplied to the predetermined maximum value. After the measured mercury concentration reaches the second predetermined mercury concentration, the amount of activated charcoal can be kept constant at the predetermined maximum value with respect to the increase in the measured mercury concentration.

さらに、第二又は第三発明において、活性炭供給量の最小値から最大値に向けた増大に関しては、制御装置は、排ガス中の水銀濃度測定値が零又は測定可能な限界最小値未満の値から、第一の所定水銀濃度に達するまでの範囲には、所定の最小値で第一の供給量とする活性炭供給量のもとに活性炭を供給し、水銀濃度測定値が上記第一の所定水銀濃度に達したときに、階段状に活性炭供給量を所定の第二の供給量にまで増大させ、水銀濃度測定値が第二の所定水銀濃度に達するまでの範囲には、活性炭供給量を第二の供給量で一定に保ち、さらに、水銀濃度測定値が第二の所定水銀濃度に達したときに、活性炭供給量を所定の第三の供給量にまで増大させるように、水銀濃度測定値の増加にしたがって、階段状に活性炭供給量を増大させることを繰り返し、活性炭供給量を所定の最大値にまで増大させた後は、水銀濃度測定値の増加に対してその所定の最大値で活性炭供給量を一定に保つようにすることもできる。 Further, in the second or third invention, regarding the increase from the minimum value to the maximum value of the activated charcoal supply amount, the control device starts from the value where the measured mercury concentration in the exhaust gas is zero or less than the measurable limit minimum value. In the range until the first predetermined mercury concentration is reached, the activated charcoal is supplied under the activated charcoal supply amount which is the first supply amount at the predetermined minimum value, and the measured mercury concentration is the first predetermined mercury. When the concentration is reached, the activated charcoal supply amount is increased stepwise to the predetermined second supply amount, and the activated charcoal supply amount is increased within the range until the measured mercury concentration reaches the second predetermined mercury concentration. The mercury concentration measurement value is kept constant at the second supply amount, and further, when the mercury concentration measurement value reaches the second predetermined mercury concentration, the activated carbon supply amount is increased to the predetermined third supply amount. The amount of activated charcoal supply is repeatedly increased stepwise as the amount of water is increased, and after the amount of activated charcoal supply is increased to a predetermined maximum value, the activated charcoal is increased at the predetermined maximum value with respect to the increase in the measured mercury concentration value. It is also possible to keep the supply constant.

上記のように、排ガス中の水銀濃度測定値に基づき、活性炭供給量を最小値から最大値へ向けて増大させることにより、活性炭供給装置の供給量調整機構にとって不具合が生じることもなく、活性炭供給量を円滑に制御することができる。 As described above, by increasing the amount of activated carbon supply from the minimum value to the maximum value based on the measured value of mercury concentration in the exhaust gas, the activated carbon supply without any trouble for the supply amount adjustment mechanism of the activated carbon supply device. The amount can be controlled smoothly.

[排ガス処理方法]
本発明における排ガス処理方法は、次の第四発明、第五発明そして第六発明のごとく構成され、いずれによっても上記課題は解決される。
[Exhaust gas treatment method]
The exhaust gas treatment method in the present invention is configured as the following fourth invention, fifth invention and sixth invention, and the above-mentioned problems are solved by any of them.

<第四発明>
炉から排出され水銀を含む排ガスを集塵装置で除塵処理し、炉から集塵装置へ排ガスを導く排ガス流路へ活性炭供給装置から活性炭を吹き込むこととする排ガス処理方法において、
炉の下流側でかつ集塵装置の上流側で排ガス中の酸素濃度を酸素濃度計で測定する酸素濃度計測工程と、炉の下流側でかつ集塵装置の上流側で排ガス中の塩化水素濃度を塩化水素濃度計で測定する塩化水素測定工程と、制御装置で活性炭供給装置の活性炭供給量を制御する制御工程を備え、
制御工程で、酸素濃度計による酸素濃度測定値及び塩化水素濃度計による塩化水素濃度測定値に基づき、上記集塵装置の下流側での排ガス中の下流側水銀濃度を設定値以下とするように、活性炭供給量を制御することを特徴とする排ガス処理方法。
<Fourth invention>
In the exhaust gas treatment method in which the exhaust gas discharged from the furnace and containing mercury is dust-removed by the dust collector, and the activated carbon is blown from the activated carbon supply device into the exhaust gas flow path that guides the exhaust gas from the furnace to the dust collector.
An oxygen concentration measurement process that measures the oxygen concentration in the exhaust gas on the downstream side of the furnace and upstream of the dust collector with an oxygen concentration meter, and the hydrogen chloride concentration in the exhaust gas on the downstream side of the furnace and upstream of the dust collector. It is equipped with a hydrogen chloride measurement step that measures the amount of hydrogen chloride with a hydrogen chloride concentration meter and a control step that controls the amount of activated charcoal supply of the activated charcoal supply device with a control device.
In the control process, the downstream mercury concentration in the exhaust gas on the downstream side of the dust collector should be set to the set value or less based on the oxygen concentration measured value by the oxygen concentration meter and the hydrogen chloride concentration measured value by the hydrogen chloride concentration meter. , An exhaust gas treatment method characterized by controlling the amount of activated carbon supply.

<第五発明>
炉から排出され水銀を含む排ガスを集塵装置で除塵処理し、炉から集塵装置へ排ガスを導く排ガス流路へ活性炭供給装置から活性炭を吹き込むこととする排ガス処理方法において、
炉の下流側でかつ集塵装置の上流側で排ガス中の酸素濃度を酸素濃度計で測定する酸素濃度計測工程と、炉の下流側でかつ集塵装置の上流側で排ガス中の塩化水素濃度を塩化水素濃度計で測定する塩化水素濃度測定工程と、炉の下流側でかつ集塵装置の上流側で排ガス中の上流側水銀濃度を上流側水銀濃度計で測定する上流側水銀濃度測定工程と、制御装置で活性炭供給装置の活性炭供給量を制御する制御工程を備え、
制御工程で、酸素濃度計による酸素濃度測定値と塩化水素濃度計による塩化水素濃度測定値及び上流側水銀濃度計による上流側水銀濃度測定値に基づき、上記集塵装置の下流側での排ガス中の下流側水銀濃度を設定値以下とするように、活性炭供給量を制御することを特徴とする排ガス処理方法。
<Fifth invention>
In the exhaust gas treatment method in which the exhaust gas discharged from the furnace and containing mercury is dust-removed by the dust collector, and the activated carbon is blown from the activated carbon supply device into the exhaust gas flow path that guides the exhaust gas from the furnace to the dust collector.
An oxygen concentration measurement process that measures the oxygen concentration in the exhaust gas on the downstream side of the furnace and upstream of the dust collector with an oxygen concentration meter, and the hydrogen chloride concentration in the exhaust gas on the downstream side of the furnace and upstream of the dust collector. Hydrogen chloride concentration measurement step that measures the upstream mercury concentration in the exhaust gas on the downstream side of the furnace and upstream side of the dust collector, and the upstream mercury concentration measurement step that measures the upstream mercury concentration in the exhaust gas with the upstream mercury concentration meter. And, it is equipped with a control process that controls the amount of activated charcoal supplied by the activated charcoal supply device with a control device.
In the exhaust gas on the downstream side of the dust collector, based on the oxygen concentration measurement value by the oxygen concentration meter, the hydrogen chloride concentration measurement value by the hydrogen chloride concentration meter, and the upstream mercury concentration measurement value by the upstream mercury concentration meter in the control step. An exhaust gas treatment method characterized in that the amount of activated carbon supplied is controlled so that the mercury concentration on the downstream side of the water is set to a set value or less.

<第六発明>
炉から排出され水銀を含む排ガスを集塵装置で除塵処理し、炉から集塵装置へ排ガスを導く排ガス流路へ活性炭供給装置から活性炭を吹き込むこととする排ガス処理方法において、
炉の下流側でかつ集塵装置の上流側で排ガス中の酸素濃度を酸素濃度計で測定する酸素濃度計測工程と、炉の下流側でかつ集塵装置の上流側で排ガス中の塩化水素濃度を塩化水素濃度計で測定する塩化水素濃度測定工程と、炉の下流側でかつ集塵装置の上流側で排ガス中の水銀濃度を上流側水銀濃度計で測定する上流側水銀濃度測定工程と、集塵装置の下流側で排ガス中の下流側水銀濃度を下流側水銀濃度計で測定する下流側水銀濃度測定工程と、制御装置で活性炭供給装置の活性炭供給量を制御する制御工程を備え、
制御工程で、酸素濃度計による酸素濃度測定値と塩化水素濃度計による塩化水素濃度測定値と上流側水銀濃度計による上流側水銀濃度測定値及び下流側水銀濃度計による下流側水銀濃度測定値に基づき、上記集塵装置の下流側での排ガス中の下流側水銀濃度を設定値以下とするように、活性炭供給量を制御することを特徴とする排ガス処理方法。
<Sixth invention>
In the exhaust gas treatment method in which the exhaust gas discharged from the furnace and containing mercury is dust-removed by the dust collector, and the activated carbon is blown from the activated carbon supply device into the exhaust gas flow path that guides the exhaust gas from the furnace to the dust collector.
An oxygen concentration measurement process that measures the oxygen concentration in the exhaust gas on the downstream side of the furnace and upstream of the dust collector with an oxygen concentration meter, and the hydrogen chloride concentration in the exhaust gas on the downstream side of the furnace and upstream of the dust collector. The hydrogen chloride concentration measurement step that measures the mercury concentration in the exhaust gas on the downstream side of the furnace and the upstream side of the dust collector, and the upstream mercury concentration measurement step that measures the mercury concentration in the exhaust gas with the upstream mercury concentration meter. It is equipped with a downstream mercury concentration measuring step that measures the downstream mercury concentration in the exhaust gas on the downstream side of the dust collector with a downstream mercury concentration meter, and a control step that controls the activated charcoal supply amount of the activated charcoal supply device with the control device.
In the control process, the oxygen concentration measurement value by the oxygen concentration meter, the hydrogen chloride concentration measurement value by the hydrogen chloride concentration meter, the upstream mercury concentration measurement value by the upstream mercury concentration meter, and the downstream mercury concentration measurement value by the downstream mercury concentration meter Based on this, an exhaust gas treatment method characterized in that the amount of activated charcoal supplied is controlled so that the concentration of mercury on the downstream side in the exhaust gas on the downstream side of the dust collector is set to a set value or less.

第四ないし第六発明においては、制御工程では、活性炭供給量を所定の最小値以上に維持するように制御することが好ましい。かかる制御により、集塵装置のバグフィルタには、活性炭の吸着層が常に形成されているようになるので、予め形成された上記吸着層による吸着除去作用とその際に吹き込まれる活性炭による吸着除去作用とにより水銀を速やかにかつ確実に吸着除去でき、集塵後の排ガスの水銀濃度を十分に低濃度とすることができる。また、第五又は第六発明においては、排ガス中の水銀濃度が所定値より低い場合には、活性炭供給量を所定の最小値に保つように制御することが好ましい。集塵装置のバグフィルタに活性炭の吸着層が常に形成されているようにして、上記所定値よりも高濃度の水銀を含む排ガスが排出された際にも、予め形成された上記吸着層による吸着除去作用とその際に吹き込まれる活性炭による吸着除去作用とにより水銀を速やかにかつ確実に吸着除去でき、集塵後の排ガスの水銀濃度を十分に低濃度とすることができる。 In the fourth to sixth inventions, in the control step, it is preferable to control the amount of activated carbon supply so as to be maintained at a predetermined minimum value or more. By such control, the adsorption layer of activated carbon is always formed on the bag filter of the dust collector. Therefore, the adsorption removal action by the above-mentioned adsorption layer formed in advance and the adsorption removal action by the activated carbon blown at that time. As a result, mercury can be quickly and surely adsorbed and removed, and the mercury concentration of the exhaust gas after dust collection can be made sufficiently low. Further, in the fifth or sixth invention, when the mercury concentration in the exhaust gas is lower than the predetermined value, it is preferable to control the amount of activated carbon supply to be maintained at the predetermined minimum value. The activated carbon adsorption layer is always formed on the bag filter of the dust collector, and even when the exhaust gas containing mercury having a concentration higher than the predetermined value is discharged, the adsorption layer is adsorbed by the preformed adsorption layer. The removal action and the adsorption removal action by the activated carbon blown at that time can quickly and surely adsorb and remove mercury, and the mercury concentration of the exhaust gas after dust collection can be made sufficiently low.

また、第五又は第六発明においては、制御工程では、上流側水銀濃度計又は下流側水銀濃度計による水銀濃度測定値が所定水銀濃度以上であるとき、活性炭供給量を所定の最大値に保つように制御することが好ましい。時間平均としてはさほど水銀濃度が高くないにも拘らず一時的に急激に水銀濃度が高くなったときに、この高い水銀濃度に合せて多量の活性炭を供給すると、その後の時間にわたり過剰に活性炭を供給してしまう結果になる。このような過剰な供給となることを、上記活性炭供給量を所定の最大値に保つように制御することにより防止できる。 Further, in the fifth or sixth invention, in the control step, when the mercury concentration measured by the upstream mercury concentration meter or the downstream mercury concentration meter is equal to or higher than the predetermined mercury concentration, the activated charcoal supply amount is maintained at the predetermined maximum value. It is preferable to control such a method. When the mercury concentration rises temporarily and suddenly even though the mercury concentration is not so high as an hourly average, if a large amount of activated carbon is supplied in accordance with this high mercury concentration, the activated carbon will be excessively generated over the subsequent time. The result is that it will be supplied. Such an excessive supply can be prevented by controlling the amount of the activated carbon supply to be maintained at a predetermined maximum value.

また、第五又は第六発明において、活性炭供給量の最小値から最大値へ向けた増大に関しては、制御工程は、排ガス中の水銀濃度測定値が零又は測定可能な限界最小値未満の値から、第一の所定水銀濃度に達するまでの範囲には、所定の最小値の活性炭供給量のもとに活性炭を供給し、水銀濃度測定値が上記第一の所定水銀濃度に達した後に、水銀濃度測定値の増加にしたがって、所定の最小値から直線的に活性炭供給量を増大させ、水銀濃度測定値が第二の所定水銀濃度に達したときに、活性炭供給量を所定の最大値の供給量とし、水銀濃度測定値が上記第二の所定水銀濃度に達した後には、水銀濃度測定値の増加に対してその所定の最大値で活性炭供給量を一定に保つようにすることができる。 Further, in the fifth or sixth invention, regarding the increase from the minimum value to the maximum value of the activated carbon supply amount, the control step starts from the value where the measured mercury concentration in the exhaust gas is zero or less than the measurable limit minimum value. In the range until the first predetermined mercury concentration is reached, the activated charcoal is supplied under the predetermined minimum value of the activated charcoal supply amount, and after the measured mercury concentration reaches the first predetermined mercury concentration, the mercury As the concentration measurement value increases, the activated charcoal supply amount is linearly increased from the predetermined minimum value, and when the mercury concentration measurement value reaches the second predetermined mercury concentration, the activated charcoal supply amount is supplied to the predetermined maximum value. After the measured mercury concentration reaches the second predetermined mercury concentration, the amount of activated charcoal can be kept constant at the predetermined maximum value with respect to the increase in the measured mercury concentration.

さらに、第五又は第六発明において、活性炭供給量の最小値から最大値に向けた増大に関しては、制御工程は、排ガスの水銀濃度測定値が零又は測定可能な限界最小値未満の値から、第一の所定水銀濃度に達するまでの範囲には、所定の最小値で第一の供給量とする活性炭供給量のもとに活性炭を供給し、水銀濃度測定値が上記第一の所定水銀濃度に達したときに、階段状に活性炭供給量を所定の第二の供給量にまで増大させ、水銀濃度測定値が第二の所定水銀濃度に達するまでの範囲には、活性炭供給量を第二の供給量で一定に保ち、さらに、水銀濃度測定値が第二の所定水銀濃度に達したときに、活性炭供給量を所定の第三の供給量にまで増大させるように、水銀濃度測定値の増加にしたがって、階段状に活性炭供給量を増大させることを繰り返し、活性炭供給量を所定の最大値にまで増大させた後は、水銀濃度測定値の増加に対してその所定の最大値で活性炭供給量を一定に保つようにすることもできる。 Further, in the fifth or sixth invention, regarding the increase from the minimum value to the maximum value of the activated carbon supply amount, the control step starts from the value where the measured mercury concentration of the exhaust gas is zero or less than the measurable limit minimum value. In the range until the first predetermined mercury concentration is reached, the activated charcoal is supplied under the activated charcoal supply amount which is the first supply amount at the predetermined minimum value, and the measured mercury concentration is the first predetermined mercury concentration. When it reaches, the amount of activated charcoal supply is increased stepwise to the predetermined second supply amount, and the amount of activated charcoal supply is increased to the range until the measured mercury concentration reaches the second predetermined mercury concentration. In addition, when the measured mercury concentration reaches the second predetermined mercury concentration, the activated carbon supply is increased to the predetermined third supply. The amount of activated charcoal supplied is repeatedly increased in a stepwise manner as the amount increases, and after the amount of activated charcoal supply is increased to a predetermined maximum value, the activated charcoal is supplied at the predetermined maximum value with respect to the increase in the measured mercury concentration value. You can also try to keep the amount constant.

上記のように、排ガスの水銀濃度測定値に基づき、活性炭供給量の最小値から最大値へ向けて増大させることにより、活性炭供給装置の供給量調整機構にとって不具合が生じることもなく、活性炭供給量を円滑に制御することができる。 As described above, by increasing the activated carbon supply amount from the minimum value to the maximum value based on the measured value of the mercury concentration of the exhaust gas, the activated carbon supply amount does not cause a problem for the supply amount adjustment mechanism of the activated carbon supply device. Can be controlled smoothly.

このような本発明によれば、第一発明そして第四発明では、炉の下流側でかつ集塵装置の上流側で排ガス中の酸素濃度を酸素濃度計で測定しそして塩化水素濃度を塩化水素濃度計で測定して、酸素濃度測定値及び塩化水素濃度測定値に基づき、活性炭供給量を調整することとして、排ガス中の酸素濃度そして塩化水素濃度の状況に対応して、活性炭による排ガス中の水銀の除去性能を把握し、活性炭供給量を過不足なく調整することで、集塵装置の下流側での排ガス中の水銀濃度を許容される設定値以下とすることができる。 According to the present invention as described above, in the first invention and the fourth invention, the oxygen concentration in the exhaust gas is measured by an oxygen concentration meter on the downstream side of the furnace and on the upstream side of the dust collector, and the hydrogen chloride concentration is measured by hydrogen chloride. By measuring with a densitometer and adjusting the amount of activated charcoal supply based on the measured oxygen concentration and hydrogen chloride concentration, the oxygen concentration in the exhaust gas and the hydrogen chloride concentration in the exhaust gas are adjusted according to the situation. By grasping the removal performance of mercury and adjusting the amount of activated carbon supply in just proportion, the concentration of mercury in the exhaust gas on the downstream side of the dust collector can be kept below the allowable set value.

第二発明そして第五発明では、炉よりも下流側で集塵装置よりも上流側で、排ガス中の酸素濃度を酸素濃度計で測定しそして塩化水素濃度を塩化水素濃度計で測定し、上流側水銀濃度を上流側水銀濃度計で測定し、その測定値に基づき活性炭供給量を調整して集塵装置の下流側での排ガス中の下流側水銀濃度を許容される設定値以下とする。炉からの排ガス中の酸素濃度そして塩化水素濃度が変動した場合に酸素濃度測定値そして塩化水素濃度測定値に基づき活性炭による排ガス中の水銀の除去性能を把握し、さらに、排ガス中の水銀濃度が変動した場合に、排ガスの集塵装置への流入前に上流側水銀濃度を測定しその測定値に基づき、速やかに活性炭供給量を適正量に調整することができ、水銀濃度の変動に対して遅れが生じることなく確実に煙突から排出される排ガス中の水銀濃度を許容される設定値以下とすることができる。 In the second and fifth inventions, the oxygen concentration in the exhaust gas is measured with an oxygen concentration meter and the hydrogen chloride concentration is measured with a hydrogen chloride concentration meter on the downstream side of the furnace and upstream of the dust collector, and the upstream side. The side mercury concentration is measured with an upstream mercury concentration meter, and the amount of activated charcoal supplied is adjusted based on the measured value so that the downstream mercury concentration in the exhaust gas on the downstream side of the dust collector is below the allowable set value. When the oxygen concentration and hydrogen chloride concentration in the exhaust gas from the furnace fluctuate, the performance of removing mercury in the exhaust gas by activated charcoal is grasped based on the oxygen concentration measurement value and the hydrogen chloride concentration measurement value, and the mercury concentration in the exhaust gas is further increased. If it fluctuates, the upstream mercury concentration can be measured before the exhaust gas flows into the dust collector, and the amount of activated carbon supply can be quickly adjusted to an appropriate amount based on the measured value. The mercury concentration in the exhaust gas discharged from the chimney can be surely set to the allowable set value or less without causing a delay.

さらに第三発明そして第六発明では、炉よりも下流側で集塵装置より上流側で、排ガス中の酸素濃度を酸素濃度計で測定しそして塩化水素濃度を塩化水素濃度計で測定し、上流側水銀濃度を上流側水銀濃度計で測定するとともに、集塵装置の下流側でも下流側水銀濃度を下流側水銀濃度計で測定し、これらの四つの測定値に基づき活性炭供給量を調整して集塵装置の下流側での下流側水銀濃度を許容される設定値以下とする。炉からの排ガス中の酸素濃度そして塩化水素濃度が変動した場合に酸素濃度測定値そして塩化水素濃度測定値に基づき活性炭による排ガス中の水銀の除去性能を把握し、さらに、炉よりも下流側で集塵装置よりも上流側での上流側水銀濃度測定値及び集塵装置の下流側での下流側水銀濃度測定値に基づき、活性炭供給量を制御する。このようにすることにより、酸素濃度そして塩化水素濃度の変動と水銀濃度の変動に対して遅れが生じることなくより確実に煙突から排出される排ガス中の水銀濃度を許容される設定値以下にできる。 Further, in the third invention and the sixth invention, the oxygen concentration in the exhaust gas is measured by an oxygen concentration meter and the hydrogen chloride concentration is measured by a hydrogen chloride concentration meter on the downstream side of the furnace and upstream of the dust collector. In addition to measuring the side mercury concentration with the upstream mercury densitometer, the downstream mercury concentration is also measured with the downstream mercury densitometer on the downstream side of the dust collector, and the amount of activated charcoal supplied is adjusted based on these four measured values. The downstream mercury concentration on the downstream side of the dust collector shall be less than or equal to the allowable set value. When the oxygen concentration and hydrogen chloride concentration in the exhaust gas from the furnace fluctuate, the performance of removing mercury in the exhaust gas by activated charcoal is grasped based on the oxygen concentration measurement value and the hydrogen chloride concentration measurement value, and further downstream from the furnace. The amount of activated charcoal supplied is controlled based on the measured value of the mercury concentration on the upstream side on the upstream side of the dust collector and the measured value of the mercury concentration on the downstream side on the downstream side of the dust collector. By doing so, it is possible to more reliably reduce the mercury concentration in the exhaust gas discharged from the chimney to the allowable set value or less without delaying the fluctuation of the oxygen concentration and the hydrogen chloride concentration and the fluctuation of the mercury concentration. ..

第一発明そして第四発明では、酸素濃度測定値そして塩化水素濃度測定値に基づき活性炭による排ガス中の水銀の除去性能を把握し活性炭供給量を制御するが、炉からの排ガス中の水銀濃度が変動したときには、その変動に対して活性炭供給量の調整に遅れが生じることがある。一方、第二発明そして第五発明では、集塵装置よりも上流側で上流側水銀濃度を測定するので、上記変動に対しても速やかに対応できる。さらに、第三発明および第六発明では、集塵装置よりも上流側で上流側水銀濃度を測定し、さらに集塵装置の下流側で下流側水銀濃度を測定し、これらの二つの測定値に基づき活性炭供給量を調整することで、排ガス中の水銀濃度の変動に対して遅れが生じることなく、より確実に煙突から排出される排ガス中の水銀濃度を許容される設定値以下にできる。 In the first invention and the fourth invention, the mercury concentration in the exhaust gas from the furnace is controlled by grasping the removal performance of mercury in the exhaust gas by the activated carbon based on the measured oxygen concentration and the measured hydrogen chloride concentration. When it fluctuates, there may be a delay in adjusting the amount of activated carbon supply due to the fluctuation. On the other hand, in the second invention and the fifth invention, since the mercury concentration on the upstream side is measured on the upstream side of the dust collector, the above fluctuation can be quickly dealt with. Further, in the third invention and the sixth invention, the mercury concentration on the upstream side is measured on the upstream side of the dust collector, and the mercury concentration on the downstream side is measured on the downstream side of the dust collector. By adjusting the amount of activated charcoal supplied based on this, the mercury concentration in the exhaust gas discharged from the chimney can be more reliably reduced to the allowable set value or less without delaying the fluctuation of the mercury concentration in the exhaust gas.

このように本発明によれば、排ガス中の酸素濃度そして塩化水素濃度を集塵装置の上流側の位置で測定し、あるいは集塵装置の上流側で酸素濃度そして塩化水素濃度を測定するとともに上流側水銀濃度も測定し、あるいは集塵装置の上流側で酸素濃度そして塩化水素濃度を測定するとともに集塵装置の上流側で上流側水銀濃度そして下流側で下流側水銀濃度を測定して、酸素温度測定値そして塩化水素濃度測定値に基づき活性炭による排ガス中の水銀の除去性能を把握し、吹き込む活性炭の供給量を調整するので、煙突から排出される排ガス中の水銀濃度は確実に許容される設定値以下となり、しかも活性炭は過不足なく供給されることとなり、活性炭の使用量を抑制できるとともに、排ガス処理費用の低減化を図れる。 Thus, according to the present invention, the oxygen concentration and the hydrogen chloride concentration in the exhaust gas are measured at the position on the upstream side of the dust collector, or the oxygen concentration and the hydrogen chloride concentration are measured on the upstream side of the dust collector and upstream. Oxygen is also measured by measuring the side mercury concentration, or measuring the oxygen concentration and hydrogen chloride concentration on the upstream side of the dust collector, and measuring the upstream mercury concentration on the upstream side of the dust collector and the downstream mercury concentration on the downstream side. Based on the temperature measurement value and the hydrogen chloride concentration measurement value, the performance of removing mercury in the exhaust gas by the activated charcoal is grasped, and the supply amount of the activated charcoal to be blown in is adjusted, so that the mercury concentration in the exhaust gas discharged from the chimney is surely tolerated. The value will be less than the set value, and the activated charcoal will be supplied in just proportion, so that the amount of activated charcoal used can be suppressed and the exhaust gas treatment cost can be reduced.

また、本発明によれば、排ガス中の酸素濃度そして塩化水素濃度もしくは排ガス中の酸素濃度として塩化水素濃度および上流側水銀濃度を集塵装置の上流側で測定し、その測定値に基づき吹き込む活性炭の供給量を調整するので、排ガス中の酸素濃度そして塩化水素濃度が低くなり、活性炭による水銀吸着効率が低下してしまった場合でも、活性炭吹込み量を制御することで、煙突から排出される排ガス中の水銀濃度を所定値以下にできる。また、水銀濃度測定値が所定水銀濃度以上であるとき、活性炭供給量を所定の最大値に保つように制御することにより、活性炭は過不足なく供給されるので、活性炭の使用量を適正にできるとともに、排ガス処理費用の低減化を図れる。 Further, according to the present invention, the hydrogen chloride concentration and the upstream mercury concentration as the oxygen concentration and the hydrogen chloride concentration in the exhaust gas or the oxygen concentration in the exhaust gas are measured on the upstream side of the dust collector, and the activated carbon is blown based on the measured values. Even if the oxygen concentration and hydrogen chloride concentration in the exhaust gas are low and the mercury adsorption efficiency by the activated charcoal is lowered, the amount of activated charcoal blown in is controlled to be discharged from the chimney. The mercury concentration in the exhaust gas can be reduced to a predetermined value or less. Further, when the measured mercury concentration is equal to or higher than the predetermined mercury concentration, the activated carbon is supplied without excess or deficiency by controlling the amount of activated carbon supply to be maintained at the predetermined maximum value, so that the amount of activated carbon used can be adjusted appropriately. At the same time, it is possible to reduce the exhaust gas treatment cost.

本発明の第一実施形態装置を示し、(A)はその概要構成図、(B)は活性炭供給装置の概要構成図である。The first embodiment apparatus of this invention is shown, (A) is the schematic block diagram, (B) is the schematic block diagram of the activated carbon supply apparatus. 本発明の第二実施形態装置の概要構成図である。It is a schematic block diagram of the 2nd Embodiment apparatus of this invention. 本発明の第三実施形態装置の概要構成図である。It is a schematic block diagram of the 3rd Embodiment apparatus of this invention. (A)~(H)は排ガス中の水銀濃度と活性炭供給量との関係として、採用可能な各種パターンを示している。(A) to (H) show various patterns that can be adopted as the relationship between the mercury concentration in the exhaust gas and the amount of activated carbon supplied. 酸素濃度と塩化水素濃度と活性炭供給量との関係を示す図である。It is a figure which shows the relationship between the oxygen concentration, the hydrogen chloride concentration, and the amount of activated carbon supply.

以下、添付図面にもとづき、本発明の実施の形態を説明する。 Hereinafter, embodiments of the present invention will be described with reference to the accompanying drawings.

本実施形態では、水銀を含む排ガスを排出する炉として、廃棄物を焼却する焼却炉について説明しているが、本発明は、これに限らず、セメントキルン炉、非鉄金属製錬炉等の各種炉から排出される水銀を含む排ガスの処理装置及び処理方法として用いることができる。 In the present embodiment, an incinerator that incinerates waste is described as a furnace that discharges exhaust gas containing mercury, but the present invention is not limited to this, and various types such as a cement kiln furnace and a non-ferrous metal smelting furnace are described. It can be used as a treatment device and a treatment method for exhaust gas containing mercury discharged from a furnace.

廃棄物を焼却する焼却炉からの排ガスに対して、集塵のために設置したバグフィルタの上流位置で排ガス流路へ活性炭を吹き込むことで、該排ガス流路に浮遊する水銀を活性炭で吸着するとともに、バグフィルタの濾過材表面に活性炭層を作成して水銀を該活性炭層で吸着して、排ガス中の水銀を吸着除去して、バグフィルタの下流側での水銀濃度を低濃度レベルに抑制することが可能であるが、従来は廃棄物の種類や量の変動により、焼却炉からの排ガス中の水銀の形態や水銀濃度が変動しバグフィルタの下流側において一時的に水銀濃度が上昇する場合に備え、活性炭を常時、多量に吹き込む必要があり、排ガス処理費用が嵩むことになっている。 By blowing activated carbon into the exhaust gas flow path at the upstream position of the bag filter installed for dust collection for the exhaust gas from the incinerator that incinerates the waste, the activated carbon adsorbs the mercury floating in the exhaust gas flow path. At the same time, an activated carbon layer is created on the surface of the filter material of the bag filter, and mercury is adsorbed by the activated carbon layer to adsorb and remove the mercury in the exhaust gas to suppress the mercury concentration on the downstream side of the bag filter to a low concentration level. However, in the past, due to fluctuations in the type and amount of waste, the morphology and mercury concentration in the exhaust gas from the incinerator fluctuated, and the mercury concentration temporarily increased on the downstream side of the bag filter. In preparation for the case, it is necessary to inject a large amount of activated carbon at all times, which increases the cost of treating exhaust gas.

そこで、本実施形態では、バグフィルタの上流側の排ガス流路で活性炭を吹き込む位置より上流側に酸素濃度計そして塩化水素濃度計もしくは酸素濃度計そして塩化水素濃度計および水銀濃度計を設置し、酸素濃度そして塩化水素濃度もしくは酸素濃度そして塩化水素濃度および水銀濃度を測定し、測定された酸素濃度そして塩化水素濃度もしくは酸素濃度そして塩化水素濃度および水銀濃度にもとづき、吹込む活性炭量を制御し、排ガス流路に吹き込んでいる。酸素濃度計そして塩化水素濃度計および水銀濃度計は、連続的に測定する形式が好ましい。 Therefore, in the present embodiment, an oxygen concentration meter, a hydrogen chloride concentration meter or an oxygen concentration meter, a hydrogen chloride concentration meter, and a mercury concentration meter are installed on the upstream side from the position where the activated charcoal is blown in the exhaust gas flow path on the upstream side of the bag filter. Oxygen concentration and hydrogen chloride concentration or oxygen concentration and hydrogen chloride concentration and mercury concentration are measured, and the amount of activated carbon to be blown is controlled based on the measured oxygen concentration and hydrogen chloride concentration or oxygen concentration and hydrogen chloride concentration and mercury concentration. It is blowing into the exhaust gas flow path. Oxygen densitometers and hydrogen chloride densitometers and mercury densitometers are preferably in the form of continuous measurement.

<第一実施形態>
本実施形態装置の概要構成を示す図1(A)において、焼却炉1からの排ガスを煙突4まで導く排ガス流路Aに、上流側からボイラ2、さらに集塵装置としてバグフィルタ3が配設されており、バグフィルタ3の上流位置で排ガス流路Aへ、排ガス中の水銀を吸着除去するための活性炭を吹き込む活性炭供給装置5とこれを制御する制御装置6が設けられており、バグフィルタ3の上流側であって、活性炭供給装置5による活性炭吹込み位置よりも上流側の位置で排ガス中の酸素濃度を測定する酸素濃度計7とその直下流側で塩化水素濃度を測定する塩化水素濃度計8が設けられ、該酸素濃度計7と塩化水素濃度計8の測定値を出力信号として上記制御装置6へ送るように、上記酸素濃度計7と塩化水素濃度計8が該制御装置6に接続されている。
<First Embodiment>
In FIG. 1A showing an outline configuration of the apparatus of the present embodiment, a boiler 2 is arranged from the upstream side and a bag filter 3 as a dust collecting device in the exhaust gas flow path A that guides the exhaust gas from the incinerator 1 to the chimney 4. An activated carbon supply device 5 for blowing activated carbon for adsorbing and removing mercury in the exhaust gas and a control device 6 for controlling the activated carbon are provided in the exhaust gas flow path A at the upstream position of the bag filter 3. An oxygen concentration meter 7 that measures the oxygen concentration in the exhaust gas at a position upstream of the activated carbon blowing position by the activated carbon supply device 5 on the upstream side of 3 and hydrogen chloride that measures the hydrogen chloride concentration immediately downstream thereof. The oxygen concentration meter 7 and the hydrogen chloride concentration meter 8 are provided with the densitometer 8 so that the measured values of the oxygen concentration meter 7 and the hydrogen chloride concentration meter 8 are sent to the control device 6 as an output signal. It is connected to the.

酸素濃度計7の測定値と塩化水素濃度計8の測定値は制御装置6に送られ、この測定値に基づき活性炭供給装置5が制御される。 The measured value of the oxygen concentration meter 7 and the measured value of the hydrogen chloride concentration meter 8 are sent to the control device 6, and the activated carbon supply device 5 is controlled based on the measured value.

制御装置6は、酸素濃度計7による酸素濃度測定値そして塩化水素濃度計8による塩化水素濃度測定値と活性炭供給量との予め定めた対応関係を記憶しており、この対応関係に基づき、活性炭供給量を制御するようにしてもよい。 The control device 6 stores a predetermined correspondence relationship between the oxygen concentration measured value by the oxygen concentration meter 7 and the hydrogen chloride concentration measured value by the hydrogen chloride concentration meter 8 and the amount of activated charcoal supplied, and based on this correspondence relationship, the activated charcoal is used. The supply amount may be controlled.

上記活性炭供給装置5は、具体的には、図1(B)に示されるように、活性炭を収容するホッパ5Aと、該ホッパ5Aの下部出口に設けられたロータリ形式の切出し部材5Bと、さらにその下方に設けられたバルブまたはダンパ5Cとを有している。かかる活性炭供給装置5では、制御装置6からの指令信号を受けて、切出し部材5Bのロータリの回転数、バルブの開度及びダンパ5Cの開度のうち少なくとも一つが調整され活性炭が供給量を調整されて上記排ガス流路Aへ供給される。 Specifically, as shown in FIG. 1B, the activated carbon supply device 5 includes a hopper 5A for accommodating activated carbon, a rotary type cutting member 5B provided at a lower outlet of the hopper 5A, and further. It has a valve or damper 5C provided below it. In the activated carbon supply device 5, at least one of the rotation speed of the rotary of the cutting member 5B, the opening degree of the valve, and the opening degree of the damper 5C is adjusted in response to the command signal from the control device 6, and the amount of activated carbon supplied is adjusted. It is supplied to the exhaust gas flow path A.

<酸素濃度測定値そして塩化水素濃度測定値と活性炭供給量との対応関係の説明>
酸素濃度測定値そして塩化水素濃度測定値と活性炭供給量との対応関係を定める手順を以下に示す。
<Explanation of the correspondence between the measured oxygen concentration and the measured hydrogen chloride concentration and the amount of activated carbon supplied>
The procedure for determining the correspondence between the measured oxygen concentration and the measured hydrogen chloride concentration and the amount of activated carbon supplied is shown below.

図1に示す排ガス処理装置を用いて排ガス中の水銀を活性炭により吸着除去する実験を行った。バグフィルタ3よりも上流側での排ガス流路Aにおける排ガス中の上流側水銀濃度は200μg/Nm程度でほぼ一定であり、酸素濃度が4vol%以下、4~8vol%、8vol%以上の三種の酸素濃度についてこの排ガス中の塩化水素濃度を50~400ppmの範囲で変化させ、上記三種の酸素濃度について、種々の塩化水素濃度の場合にバグフィルタ3の下流側である煙突4内の排ガス中の下流側水銀濃度を一時間の平均値で50μg/Nm以下とするために必要な活性炭供給量を求め、排ガス中の酸素濃度と塩化水素濃度と活性炭供給量との好ましい対応関係を図5に示すように定めた。 An experiment was conducted in which mercury in the exhaust gas was adsorbed and removed with activated carbon using the exhaust gas treatment device shown in FIG. The upstream mercury concentration in the exhaust gas in the exhaust gas flow path A on the upstream side of the bag filter 3 is almost constant at about 200 μg / Nm 3 , and the oxygen concentration is 4 vol% or less, 4 to 8 vol%, and 8 vol% or more. The hydrogen chloride concentration in the exhaust gas is changed in the range of 50 to 400 ppm, and the above three types of oxygen concentration are in the exhaust gas in the chimney 4 on the downstream side of the bag filter 3 in the case of various hydrogen chloride concentrations. The amount of activated charcoal supply required to keep the concentration of mercury on the downstream side of the slag below 50 μg / Nm 3 or less on average for one hour was obtained, and the preferable correspondence between the oxygen concentration in the exhaust gas, the hydrogen chloride concentration, and the activated charcoal supply amount is shown in FIG. It was decided as shown in.

図5に示されるように、酸素濃度が8vol%以上の高い濃度の場合には、活性炭の水銀除去性能が高く水銀は十分に吸着除去されるので、活性炭供給量は酸素濃度が4~8vol%の場合や4vol%以下の場合に比べて少ない供給量で十分に水銀を除去でき、排ガス中の水銀濃度を十分に許容される設定値以下とすることができる。一方、酸素濃度が低い場合には、活性炭による排ガス中水銀の吸着除去性能が低いため、多くの活性炭供給量が必要であり、活性炭供給量を増加して排ガス中の水銀濃度を許容される設定値以下とするようにする。すなわち、酸素濃度が低いほど必要な活性炭供給量は多くなる。 As shown in FIG. 5, when the oxygen concentration is as high as 8 vol% or more, the mercury removal performance of the activated carbon is high and mercury is sufficiently adsorbed and removed. Therefore, the amount of activated carbon supplied is 4 to 8 vol%. Compared with the case of 4 vol% or less, mercury can be sufficiently removed with a smaller supply amount, and the mercury concentration in the exhaust gas can be sufficiently set to be less than the allowable set value. On the other hand, when the oxygen concentration is low, the ability of activated carbon to adsorb and remove mercury in the exhaust gas is low, so a large amount of activated carbon supply is required, and the amount of activated carbon supply is increased to allow the mercury concentration in the exhaust gas. Try to be less than or equal to the value. That is, the lower the oxygen concentration, the larger the required amount of activated carbon supplied.

さらに、図5に示されるように、上記三種の酸素濃度のいずれの場合も、塩化水素濃度が高い濃度の場合には、活性炭による排ガス中水銀の吸着除去性能が高く、活性炭により十分に吸着除去される。例えば、酸素濃度が8vol%以上で、塩化水素濃度が300ppm以上であると、活性炭による排ガス中水銀の吸着除去性能が高く、活性炭により十分に吸着除去されるので、活性炭供給量は排ガス流量あたり50mg/Nm程度で十分に水銀を除去でき、排ガス中の水銀濃度を十分に許容される設定値以下とすることができる。一方、塩化水素濃度が300ppmより低い場合には、活性炭による排ガス中水銀の吸着除去性能が低いため、多くの活性炭供給量が必要であり、活性炭供給量を増加して排ガス中の水銀濃度を許容される設定値以下とするようにする。すなわち、塩化水素濃度が低いほど必要な活性炭供給量は多くなる。 Further, as shown in FIG. 5, in any of the above three oxygen concentrations, when the hydrogen chloride concentration is high, the performance of adsorbing and removing mercury in the exhaust gas by activated carbon is high, and the activated carbon sufficiently adsorbs and removes mercury. Will be done. For example, when the oxygen concentration is 8 vol% or more and the hydrogen chloride concentration is 300 ppm or more, the performance of adsorbing and removing mercury in the exhaust gas by the activated carbon is high, and the activated carbon sufficiently adsorbs and removes the mercury. Mercury can be sufficiently removed at about / Nm3 , and the mercury concentration in the exhaust gas can be set to a sufficiently acceptable set value or less. On the other hand, when the hydrogen chloride concentration is lower than 300 ppm, the performance of adsorbing and removing mercury in the exhaust gas by activated carbon is low, so a large amount of activated carbon supply is required, and the amount of activated carbon supply is increased to allow the mercury concentration in the exhaust gas. It should be less than or equal to the set value to be set. That is, the lower the hydrogen chloride concentration, the larger the required amount of activated carbon supply.

排ガス中の水銀濃度が異なる場合にも、同様に排ガス中の酸素濃度測定値そして塩化水素濃度測定値と活性炭供給量との好ましい対応関係を定めておき、測定した酸素濃度測定値そして塩化水素濃度測定値に基づき、活性炭供給装置の活性炭供給量を制御する。 Even when the mercury concentration in the exhaust gas is different, the measured oxygen concentration and the hydrogen chloride concentration in the exhaust gas have a favorable correspondence between the measured oxygen concentration and the hydrogen chloride concentration, and the measured oxygen concentration and the hydrogen chloride concentration are measured. The amount of activated charcoal supplied by the activated charcoal supply device is controlled based on the measured values.

<第二実施形態>
図2に示される第二実施形態は、既述の第一実施形態に比し、酸素濃度計7そして塩化水素濃度計8に加え、活性炭供給装置5による活性炭吹込み位置よりも上流側の位置に上流側水銀濃度計9を設置したことのみが異なり他は図1の場合と同じである。したがって、図2では、図1の第一実施形態における部位と共通な部位について同一符号を付すことで、その説明は省略する。
<Second embodiment>
The second embodiment shown in FIG. 2 has a position upstream of the activated carbon blowing position by the activated carbon supply device 5 in addition to the oxygen densitometer 7 and the hydrogen chloride densitometer 8 as compared with the first embodiment described above. It is the same as the case of FIG. 1 except that the upstream mercury densitometer 9 is installed in. Therefore, in FIG. 2, the same reference numerals are given to the parts common to the parts in the first embodiment of FIG. 1, and the description thereof will be omitted.

本実施形態では、図2に見られるように、上流側水銀濃度計9は焼却炉1の下流側かつバグフィルタ3よりも上流側であって、活性炭供給装置5による活性炭吹込み位置よりも上流側の位置で排ガス中の上流側水銀濃度を測定するように配設されている。本実施形態では、この測定位置での酸素濃度そして塩化水素濃度、上流側水銀濃度および活性炭供給量と、バグフィルタ3よりも下流位置での下流側水銀濃度との関係が蓄積されたデータにもとづき把握されている。したがって、活性炭吹込み位置よりも上流側での酸素濃度そして塩化水素濃度および上流側水銀濃度を測定しその酸素測定値そして塩化水素濃度測定値および上流側水銀濃度測定値とその時点で供給している活性炭供給量とから、バグフィルタ3の下流での下流側水銀濃度を推定できる。すなわち、制御装置6によって上記活性炭吹込み位置よりも上流側での酸素濃度そして塩化水素濃度および上流側水銀濃度測定値に基づき、バグフィルタ3の下流側での下流側水銀濃度を推定し、その推定下流側水銀濃度を設定値以下とするために必要な活性炭供給量を求めることができ、活性炭供給装置5の活性炭供給量を制御する。その結果としてバグフィルタ3の下流側での下流側水銀濃度を設定値以下としている。制御装置6は、酸素濃度計7による酸素濃度測定値そして塩化水素濃度計8による塩化水素濃度測定値と上流側水銀濃度計9による上流側水銀濃度測定値と制御を行う時点で供給されている活性炭供給量との予め定めた対応関係に基づき、活性炭供給量を制御するようにしてもよい。 In the present embodiment, as seen in FIG. 2, the upstream mercury concentration meter 9 is on the downstream side of the incinerator 1 and on the upstream side of the bag filter 3, and is upstream of the activated carbon blowing position by the activated carbon supply device 5. It is arranged so as to measure the mercury concentration on the upstream side in the exhaust gas at the position on the side. In the present embodiment, the relationship between the oxygen concentration and the hydrogen chloride concentration at the measurement position, the upstream mercury concentration and the activated charcoal supply amount, and the downstream mercury concentration at the downstream position from the bag filter 3 is accumulated based on the accumulated data. It is grasped. Therefore, the oxygen concentration, the hydrogen chloride concentration, and the upstream mercury concentration measured on the upstream side of the activated charcoal blowing position are measured, and the oxygen measured value, the hydrogen chloride concentration measured value, the upstream mercury concentration measured value, and the upstream mercury concentration measured value are supplied at that time. The downstream mercury concentration downstream of the bag filter 3 can be estimated from the amount of activated charcoal supplied. That is, the control device 6 estimates the downstream mercury concentration on the downstream side of the bag filter 3 based on the oxygen concentration, the hydrogen chloride concentration, and the upstream mercury concentration measured value on the upstream side of the activated carbon blowing position. The amount of activated carbon supplied to keep the estimated downstream mercury concentration below the set value can be obtained, and the amount of activated carbon supplied by the activated carbon supply device 5 is controlled. As a result, the downstream mercury concentration on the downstream side of the bug filter 3 is set to be equal to or less than the set value. The control device 6 is supplied at the time of controlling the oxygen concentration measured value by the oxygen concentration meter 7, the hydrogen chloride concentration measured value by the hydrogen chloride concentration meter 8, and the upstream mercury concentration measured value by the upstream mercury concentration meter 9. The amount of activated carbon supply may be controlled based on a predetermined correspondence with the amount of activated carbon supply.

かかる本実施形態では、焼却炉1からの排ガス中の酸素濃度そして塩化水素濃度や水銀濃度に変動があった場合、この酸素濃度そして塩化水素濃度や水銀濃度の変動を焼却炉1の下流側かつ活性炭供給装置5による活性炭吹込み位置よりも上流側の位置で酸素濃度計7そして塩化水素濃度計8および上流側水銀濃度計9が測定して検知し、速やかに活性炭供給量を調整する対応ができるので、タイムラグがなく、バグフィルタ3の下流側の排ガス中の水銀濃度を確実に設定値以下に維持することができる。図2に図示された例では、酸素濃度計7そして塩化水素濃度計8による酸素濃度そして塩化水素濃度の測定位置および上流側水銀濃度計9による上流側水銀濃度の測定位置は、活性炭吹込み位置よりも上流側であるが、これに限定されずに、バグフィルタ3の上流側であって、該活性炭吹込み位置よりも下流側であってもよい。 In the present embodiment, when there is a change in the oxygen concentration, the hydrogen chloride concentration, or the mercury concentration in the exhaust gas from the incinerator 1, the change in the oxygen concentration, the hydrogen chloride concentration, or the mercury concentration is transferred to the downstream side of the incinerator 1. The oxygen concentration meter 7, the hydrogen chloride concentration meter 8 and the upstream mercury concentration meter 9 measure and detect at a position upstream of the activated charcoal injection position by the activated charcoal supply device 5, and promptly adjust the activated charcoal supply amount. Therefore, there is no time lag, and the mercury concentration in the exhaust gas on the downstream side of the bag filter 3 can be reliably maintained below the set value. In the example shown in FIG. 2, the measurement position of the oxygen concentration and the hydrogen chloride concentration by the oxygen concentration meter 7 and the hydrogen chloride concentration meter 8 and the measurement position of the upstream mercury concentration by the upstream mercury concentration meter 9 are the activated carbon blowing positions. It is on the upstream side, but is not limited to this, and may be on the upstream side of the bag filter 3 and on the downstream side of the activated carbon blowing position.

水銀濃度測定値の変化に対して活性炭供給量を対応させる対応関係としては、種々の形態を適用することができる。 Various forms can be applied as a correspondence relationship in which the amount of activated carbon supplied corresponds to a change in the measured value of mercury concentration.

測定した排ガス中の水銀濃度が零又は測定可能な限界最小値未満又は予め定めた所定値より低い場合には、活性炭の供給を行わず、排ガス中の水銀濃度が零又は測定可能な限界最小値又は予め定めた所定値より高い場合には、活性炭供給量を排ガス中の水銀濃度の増加にしたがって、次第に増加させるような対応関係の形態(形態1)にしてもよい。また、上記の形態1に付加して、水銀濃度の測定値が所定の水銀濃度に達するまでの間、水銀濃度の増加にしたがって、活性炭供給量を増大させ、水銀濃度の測定値が所定の水銀濃度以上の場合に、活性炭供給量を所定の最大値の供給量とし一定とする対応関係の形態
(形態2)としてもよい。また、形態1または形態2において、水銀濃度の増加にしたがって、活性炭供給量を増大させる際に、直線的に増大させてもよいし、ステップ状に増大させてもよい。
If the measured mercury concentration in the exhaust gas is zero or less than the measurable limit minimum value or lower than the predetermined value, the activated charcoal is not supplied and the mercury concentration in the exhaust gas is zero or the measurable limit minimum value. Alternatively, if the value is higher than a predetermined value, the amount of activated charcoal may be gradually increased as the mercury concentration in the exhaust gas increases (form 1). Further, in addition to the above-mentioned form 1, the amount of activated charcoal supplied is increased as the mercury concentration increases until the measured value of the mercury concentration reaches a predetermined mercury concentration, and the measured value of the mercury concentration is the predetermined mercury. When the concentration is equal to or higher than the concentration, the activated carbon supply amount may be a predetermined maximum value supply amount and may be a form of correspondence (form 2) in which the supply amount is constant. Further, in the first form or the second form, when the amount of activated carbon supplied is increased as the mercury concentration increases, it may be increased linearly or stepwise.

また、水銀濃度測定値の変化に対して活性炭供給量を対応させる対応関係としては、水銀濃度測定値が所定の水銀濃度以下の場合は活性炭供給量を所定の最小値とし、水銀濃度測定値が所定の水銀濃度より高い場合には水銀濃度測定値の増加にしたがって、活性炭供給量を所定の最小値から次第に増加して、さらに、水銀濃度測定値が所定の水銀濃度より高い場合には活性炭供給量を所定の最大値に維持する対応関係の形態(形態3)にしてもよい。活性炭供給量の最小値としては、焼却炉1から排ガスが排出されている運転中は排ガス中の水銀濃度が極めて低い場合にも、最低限としてこの最小値の供給量で常時活性炭を吹き込むことにより、煙突内の排ガス中の水銀濃度を設定値以下に確実に維持できるようにする活性炭供給量の値を定める。水銀濃度測定値の増加にしたがって、活性炭供給量を所定の最小値から次第に増加させることにより、排ガス中の水銀濃度に対して適正な量の活性炭を供給することができる。活性炭供給量を所定の最小値から次第に増大させる場合には、直線的に増大させてもよいし、複数段階に分けてステップ状に増大させるようにしてもよく、種々の対応関係の形態を採用できる。 In addition, as a correspondence relationship in which the amount of activated charcoal supplied corresponds to the change in the measured value of mercury concentration, when the measured value of mercury concentration is equal to or less than the predetermined mercury concentration, the amount of activated charcoal supplied is set to the predetermined minimum value, and the measured value of mercury concentration is set. When the mercury concentration is higher than the predetermined mercury concentration, the amount of activated charcoal supplied is gradually increased from the predetermined minimum value as the measured mercury concentration increases, and when the measured mercury concentration is higher than the predetermined mercury concentration, the activated charcoal is supplied. It may be in the form of a correspondence relationship (form 3) in which the amount is maintained at a predetermined maximum value. As the minimum value of the amount of activated carbon supplied, even if the concentration of mercury in the exhaust gas is extremely low during operation when the exhaust gas is discharged from the incinerator 1, by constantly injecting activated carbon with this minimum amount of supply. , Determine the value of the amount of activated carbon supplied to ensure that the concentration of mercury in the exhaust gas in the chimney is maintained below the set value. By gradually increasing the amount of activated carbon supplied from a predetermined minimum value as the measured value of mercury concentration increases, it is possible to supply an appropriate amount of activated carbon with respect to the concentration of mercury in the exhaust gas. When the amount of activated carbon supply is gradually increased from a predetermined minimum value, it may be increased linearly, or it may be divided into a plurality of steps and increased in steps, and various forms of correspondence are adopted. can.

活性炭の供給量を調整する手段として、活性炭供給装置のロータリ形式切出し部材のロータリの回転数、バルブの開度及びダンパの開度などを単独で又は組み合わせて調整することを行うが、これらの調整機構の調整範囲や調整の特性(例えば供給量の増減を連続的に可能、又は段階的に可能等)に適した対応関係の形態を採用することが好ましい。 As a means for adjusting the supply amount of activated carbon, the rotation speed of the rotary of the rotary type cutting member of the activated carbon supply device, the opening degree of the valve, the opening degree of the damper, etc. are adjusted individually or in combination. It is preferable to adopt a form of correspondence suitable for the adjustment range of the mechanism and the characteristics of adjustment (for example, the supply amount can be continuously increased or decreased, or can be gradually increased or decreased).

水銀濃度測定値と活性炭供給量との対応関係の形態のうち形態3についての各種の応用形態の例を図4に示す。 FIG. 4 shows examples of various application forms for Form 3 among the forms of the correspondence between the measured mercury concentration value and the amount of activated carbon supplied.

図4(A)に示す応用形態は、排ガス中の水銀濃度の測定値が零又は測定可能な限界最小値未満の値から、予め定める所定水銀濃度までの範囲には、所定の最小値の活性炭供給量のもとに活性炭を供給し、水銀濃度の測定値が上記所定水銀濃度に達したときに、ステップ状に活性炭供給量を所定の最大値にまで増大させ、さらに、排ガス中の水銀濃度の増加に対して、活性炭供給量をその所定の最大値で一定に保つ形態である。水銀濃度の測定値が所定水銀濃度より低い場合には活性炭供給量を所定の最小値とし、所定水銀濃度より高い場合には活性炭供給量を所定の最大値とする対応関係の形態であり、簡単な制御機構で活性炭供給量を制御することができる。 In the application mode shown in FIG. 4A, the measured value of the mercury concentration in the exhaust gas is zero or a value less than the measurable limit minimum value, and the predetermined minimum value of the activated carbon is in the range from the predetermined mercury concentration to the predetermined value. Activated charcoal is supplied based on the supply amount, and when the measured value of mercury concentration reaches the predetermined mercury concentration, the amount of activated charcoal supply is increased stepwise to the predetermined maximum value, and the mercury concentration in the exhaust gas is further increased. It is a form in which the amount of activated carbon supplied is kept constant at a predetermined maximum value with respect to the increase in the amount of mercury. When the measured value of the mercury concentration is lower than the predetermined mercury concentration, the activated carbon supply amount is set to the predetermined minimum value, and when the measured value is higher than the predetermined mercury concentration, the activated carbon supply amount is set to the predetermined maximum value. The amount of activated carbon supplied can be controlled by a flexible control mechanism.

図4(B)に示す応用形態は、排ガス中の水銀濃度の測定値が零又は測定可能な限界最小値未満の値から、第一の所定水銀濃度に達するまでの範囲には、所定の最小値の活性炭供給量(第一の供給量)のもとに活性炭を供給し、水銀濃度の測定値が上記第一の所定水銀濃度に達したときに、ステップ状に活性炭供給量を所定の第二の供給量にまで増大させ、排ガス中の水銀濃度の増加に対して活性炭供給量を第二の供給量で一定に保ち、さらに、水銀濃度の測定値が第二の所定水銀濃度に達したときに、活性炭供給量を所定の第三の供給量にまで増大させるように、排ガス中の水銀濃度の増加にしたがって、細かい階段状で活性炭供給量を増大させることを繰り返し、活性炭供給量を所定の最大値にまで増大させた後は、排ガス中の水銀濃度の増加に対してその所定の最大値で活性炭供給量を一定に保つ形態である。排ガス中の水銀濃度の増加にしたがって、活性炭供給量を所定の最小値から所定の最大値にまで階段状で増大させることにより、排ガス中の水銀濃度に対して活性炭の供給をより適正な量で供給するように制御することができる。 In the application mode shown in FIG. 4B, the measured value of the mercury concentration in the exhaust gas is zero or less than the measurable limit minimum value, and the range from reaching the first predetermined mercury concentration is a predetermined minimum. Activated charcoal is supplied based on the value of the activated charcoal supply amount (first supply amount), and when the measured value of the mercury concentration reaches the above-mentioned first predetermined mercury concentration, the activated charcoal supply amount is determined in a stepwise manner. It was increased to the second supply amount, the activated charcoal supply amount was kept constant at the second supply amount against the increase of the mercury concentration in the exhaust gas, and the measured value of the mercury concentration reached the second predetermined mercury concentration. Occasionally, in order to increase the amount of activated charcoal supply to a predetermined third supply amount, the amount of activated charcoal supply is repeatedly increased in fine steps as the mercury concentration in the exhaust gas increases, and the amount of activated charcoal supply is predetermined. After increasing to the maximum value of, the activated carbon supply amount is kept constant at the predetermined maximum value against the increase of the mercury concentration in the exhaust gas. By increasing the amount of activated carbon supply from a predetermined minimum value to a predetermined maximum value in a stepwise manner as the mercury concentration in the exhaust gas increases, the amount of activated carbon supplied is more appropriate for the mercury concentration in the exhaust gas. It can be controlled to supply.

図4(C)に示す応用形態は、排ガス中の水銀濃度の増加にしたがって、所定の最小値から直線的に活性炭供給量を増大させる形態である。また、図4(D)に示す応用形態は、排ガス中の水銀濃度の測定値が所定水銀濃度に達するまでの範囲には、排ガス中の水銀濃度の増加にしたがって、所定の最小値から直線的に活性炭供給量を増大させ、水銀濃度の測定値が上記所定の排ガス中の水銀濃度に達したときに、活性炭供給量を所定の最大値の供給量とし、活性炭供給量を所定の最大値にまで増大させた後は、排ガス中の水銀濃度の増加に対してその所定の最大値で活性炭供給量を一定に保つ形態である。図4(C)、(D)に示す応用形態では、排ガス中の水銀濃度の増加にしたがって、所定の最小値から連続的に活性炭供給量を増大させることにより、排ガス中の水銀濃度に対してきめ細かく適正量で活性炭を供給するように制御することができる。 The application form shown in FIG. 4C is a form in which the amount of activated carbon supplied is linearly increased from a predetermined minimum value as the mercury concentration in the exhaust gas increases. Further, in the application mode shown in FIG. 4 (D), in the range until the measured value of the mercury concentration in the exhaust gas reaches the predetermined mercury concentration, as the mercury concentration in the exhaust gas increases, the value is linear from the predetermined minimum value. When the measured value of mercury concentration reaches the mercury concentration in the above-mentioned predetermined exhaust gas, the activated charcoal supply amount is set to the predetermined maximum value and the activated charcoal supply amount is set to the predetermined maximum value. After increasing to, the amount of activated charcoal supplied is kept constant at a predetermined maximum value against an increase in the concentration of mercury in the exhaust gas. In the application embodiments shown in FIGS. 4C and 4D, the amount of activated carbon supplied is continuously increased from a predetermined minimum value as the mercury concentration in the exhaust gas increases, so that the mercury concentration in the exhaust gas is increased. It is possible to finely control the supply of activated carbon in an appropriate amount.

図4(E)に示す応用形態は、排ガス中の水銀濃度の測定値が零又は測定可能な限界最小値未満の値から、第一の所定水銀濃度に達するまでの範囲には、所定の最小値の活性炭供給量のもとに活性炭を供給し、水銀濃度の測定値が上記第一の所定水銀濃度に達した後に、排ガス中の水銀濃度の増加にしたがって、所定の最小値から直線的に活性炭供給量を増大させ、水銀濃度の測定値が第二の所定水銀濃度に達したときに、活性炭供給量を所定の最大値の供給量とし、活性炭供給量を所定の最大値にまで増大させた後は、排ガス中の水銀濃度の増加に対してその所定の最大値で活性炭供給量を一定に保つ形態である。図4(E)に示す応用形態は、図4(A)と(C)に示す応用形態を組み合わせた形態であり、それぞれの形態の特徴、効果を併せもつ。 In the application mode shown in FIG. 4 (E), the measured value of the mercury concentration in the exhaust gas is zero or less than the measurable limit minimum value, and the range from reaching the first predetermined mercury concentration is a predetermined minimum. After the activated charcoal is supplied based on the value of the activated charcoal supply amount and the measured value of the mercury concentration reaches the above-mentioned first predetermined mercury concentration, as the mercury concentration in the exhaust gas increases, the activated charcoal is linearly applied from the predetermined minimum value. When the measured value of the mercury concentration reaches the second predetermined mercury concentration by increasing the activated charcoal supply amount, the activated charcoal supply amount is set to the predetermined maximum value supply amount and the activated charcoal supply amount is increased to the predetermined maximum value. After that, the amount of activated charcoal supplied is kept constant at a predetermined maximum value against an increase in the concentration of mercury in the exhaust gas. The application form shown in FIG. 4 (E) is a combination of the application forms shown in FIGS. 4 (A) and 4 (C), and has the characteristics and effects of each form.

図4(F)に示す応用形態は、排ガス中の水銀濃度の測定値が零又は測定可能な限界最小値未満の値から、第一の所定水銀濃度に達するまでの範囲には、所定の最小値の活性炭供給量(第一の供給量)のもとに活性炭を供給し、水銀濃度の測定値が上記第一の所定水銀濃度に達した後に、排ガス中の水銀濃度の増加にしたがって、第一の供給量から直線的に活性炭供給量を増大させ、第二の所定水銀濃度に対応する第二の供給量にまで増大させ、その後排ガス中の水銀濃度の増加に対して活性炭供給量を第二の供給量で一定に保ち、さらに、第三の所定水銀濃度に達したときに、第二の供給量から直線的に活性炭供給量を増大させ、第四の所定水銀濃度に対応する第三の供給量にまで増大させ、その後排ガス中の水銀濃度の増加に対して活性炭供給量を第三の供給量で一定に保ち、このような排ガス中の水銀濃度の増加に対して活性炭供給量を一定に保つことと増大させることを繰り返し、活性炭供給量を所定の最大値にまで増大させた後は、排ガス中の水銀濃度の増加に対してその所定の最大値で活性炭供給量を一定に保つ形態である。図4(F)に示す応用形態は、図4(B)と(D)に示す応用形態を組み合わせた形態であり、それぞれの形態の特徴、効果を併せもつ。 In the application mode shown in FIG. 4 (F), the measured value of the mercury concentration in the exhaust gas is zero or less than the measurable limit minimum value, and the range from reaching the first predetermined mercury concentration is a predetermined minimum. Activated charcoal is supplied based on the value of the activated charcoal supply amount (first supply amount), and after the measured value of the mercury concentration reaches the above-mentioned first predetermined mercury concentration, as the mercury concentration in the exhaust gas increases, the first The amount of activated carbon supply is increased linearly from one supply amount to a second supply amount corresponding to the second predetermined mercury concentration, and then the activated charcoal supply amount is increased in response to the increase in the mercury concentration in the exhaust gas. The third supply amount is kept constant, and when the third predetermined mercury concentration is reached, the activated carbon supply amount is linearly increased from the second supply amount to correspond to the fourth predetermined mercury concentration. After that, the amount of activated charcoal supply is kept constant at the third supply amount in response to the increase in the mercury concentration in the exhaust gas, and the amount of activated charcoal supply is increased in response to such an increase in the mercury concentration in the exhaust gas. After increasing the amount of activated charcoal supply to a predetermined maximum value by repeating keeping it constant and increasing it, the amount of activated charcoal supply is kept constant at the predetermined maximum value against an increase in the mercury concentration in the exhaust gas. It is a form. The application form shown in FIG. 4F is a combination of the application forms shown in FIGS. 4B and 4D, and has the characteristics and effects of each form.

図4(G)に示す応用形態は、排ガス中の水銀濃度の測定値が所定水銀濃度に達するまでの間、排ガス中の水銀濃度の増加にしたがって、所定の最小値から直線的に活性炭供給量を増大させ、水銀濃度の測定値が上記所定水銀濃度に達したときに、ステップ状に活性炭供給量を所定の最大値にまで増大させ、活性炭供給量を所定の最大値にまで増大させた後は、排ガス中の水銀濃度の増加に対してその所定の最大値で活性炭供給量を一定に保つ形態である。排ガス中の水銀濃度の測定値が比較的中程度の所定の値より低い場合には、排ガス中水銀濃度の増加にしたがって、所定の最小値から連続的に活性炭供給量を増大させることにより、排ガス中の水銀濃度に対してきめ細かく適正量で活性炭を供給するように制御することができ、排ガス中の水銀濃度の測定値が比較的中程度の所定水銀濃度より高い場合には、活性炭供給量を所定の最大値とすることとする対応関係であり、活性炭の供給量を調整する複数の手段を有効に利用して活性炭供給量を適切量で制御することができる。 In the application mode shown in FIG. 4 (G), the amount of activated charcoal supplied linearly from a predetermined minimum value as the mercury concentration in the exhaust gas increases until the measured value of the mercury concentration in the exhaust gas reaches the predetermined mercury concentration. When the measured value of the mercury concentration reaches the above-mentioned predetermined mercury concentration, the activated charcoal supply amount is increased to the predetermined maximum value in a stepwise manner, and the activated charcoal supply amount is increased to the predetermined maximum value. Is a form in which the amount of activated charcoal supplied is kept constant at a predetermined maximum value with respect to an increase in the concentration of mercury in the exhaust gas. When the measured value of the mercury concentration in the exhaust gas is lower than the predetermined value, which is relatively medium, the amount of activated charcoal supplied is continuously increased from the predetermined minimum value as the mercury concentration in the exhaust gas increases. It is possible to finely control the supply of activated charcoal in an appropriate amount with respect to the medium mercury concentration, and if the measured value of the mercury concentration in the exhaust gas is higher than the relatively medium predetermined mercury concentration, the activated charcoal supply amount is adjusted. It is a correspondence relationship in which a predetermined maximum value is set, and the activated charcoal supply amount can be controlled by an appropriate amount by effectively utilizing a plurality of means for adjusting the activated charcoal supply amount.

図4(H)に示す応用形態は、排ガス中の水銀濃度の測定値が第一の所定水銀濃度に達するまでの間、排ガス中の水銀濃度の増加にしたがって、所定の最小値から直線的に活性炭供給量を増大させ、水銀濃度の測定値が上記第一の所定水銀濃度に達したときに、活性炭供給量を所定の第一の供給量とし、水銀濃度の測定値が第二の所定水銀濃度に達するまでの間、活性炭供給量を所定の第一の供給量で一定に保ち、水銀濃度の測定値が上記第二の所定水銀濃度に達したときに、ステップ状に活性炭供給量を所定の最大値にまで増大させ、活性炭供給量を所定の最大値にまで増大させた後は、排ガス中の水銀濃度の増加に対してその所定の最大値で活性炭供給量を一定に保つ形態である。図4(H)に示す応用形態は、図4(G)に示す応用形態に、排ガス中の水銀濃度の測定値が比較的中程度の所定の範囲(第一の所定水銀濃度から第二の所定銀濃度までの範囲)では、活性炭供給量を第一の所定供給量で一定に保つことを組み合わせた形態であり、活性炭の供給をより適正な量で供給するように制御することができる。 In the application mode shown in FIG. 4 (H), until the measured value of the mercury concentration in the exhaust gas reaches the first predetermined mercury concentration, as the mercury concentration in the exhaust gas increases, the measured value linearly from the predetermined minimum value. When the activated charcoal supply amount is increased and the measured value of the mercury concentration reaches the first predetermined mercury concentration, the activated charcoal supply amount is set as the predetermined first supply amount, and the measured value of the mercury concentration is the second predetermined mercury. Until the concentration is reached, the activated charcoal supply amount is kept constant at the predetermined first supply amount, and when the measured value of the mercury concentration reaches the second predetermined mercury concentration, the activated charcoal supply amount is predetermined in a stepwise manner. After increasing to the maximum value of and increasing the amount of activated charcoal supply to a predetermined maximum value, the activated charcoal supply amount is kept constant at the predetermined maximum value against an increase in the mercury concentration in the exhaust gas. .. The application form shown in FIG. 4 (H) has a predetermined range (from the first predetermined mercury concentration to the second) in which the measured value of the mercury concentration in the exhaust gas is relatively medium in the application form shown in FIG. 4 (G). In the range up to the predetermined silver concentration), the activated carbon supply amount is kept constant at the first predetermined supply amount, and the supply of the activated carbon can be controlled to be supplied in a more appropriate amount.

<第三実施形態>
図3に示される第三実施形態は、前出の第二実施形態に比し、活性炭供給装置5による活性炭吹込み位置よりも上流側に配された酸素濃度計7と塩化水素濃度計8そして第一水銀濃度計(上流側水銀濃度計)9Aに加え、バグフィルタ3の下流側であるバグフィルタ3の出口又は煙突4に排ガス中の水銀濃度を測定する第二水銀濃度計(下流側水銀濃度計)9Bも設けられている点で特徴がある。この点以外は第二実施形態と同じである。上記第二水銀濃度計9Bの測定値は、上記酸素濃度計7と塩化水素濃度計8そして第一水銀濃度計9Aの測定値とともに出力信号として制御装置6へ送られるようになっている。図3では、図2の第二実施形態における部位と共通な部位について同一符号を付すことで、その説明は省略する。
<Third embodiment>
Compared to the second embodiment described above, the third embodiment shown in FIG. 3 has an oxygen densitometer 7, a mercury densitometer 8, and a hydrogen densitometer 8 arranged on the upstream side of the activated charcoal blowing position by the activated charcoal supply device 5. In addition to the first mercury densitometer (upstream mercury densitometer) 9A, the second mercury densitometer (downstream mercury) that measures the mercury concentration in the exhaust gas at the outlet or chimney 4 of the bag filter 3 on the downstream side of the bag filter 3. Densitometer) 9B is also provided, which is a feature. Other than this point, it is the same as the second embodiment. The measured value of the second mercury densitometer 9B is sent to the control device 6 as an output signal together with the measured values of the oxygen densitometer 7, the hydrogen chloride densitometer 8, and the first mercury densitometer 9A. In FIG. 3, the same reference numerals are given to the parts common to the parts in the second embodiment of FIG. 2, and the description thereof will be omitted.

本実施形態では、図3に見られるように、上述のように、水銀濃度計として、前出の第二実施形態の活性炭供給装置5による活性炭吹込み位置よりも上流側に配された第一水銀濃度計9A(上流側水銀濃度計)に加え、バグフィルタ3の出口又は煙突4に第二水銀濃度計9B(下流側水銀濃度計)が設けられている。第二実施形態と同様に活性炭供給装置5による活性炭吹込み位置よりも上流側における酸素濃度計7による酸素濃度と塩化水素濃度計8による塩化水素濃度そして第一水銀濃度計9Aによる上流側水銀濃度測定値に基づいて活性炭供給量を制御し、さらにバグフィルタ3の出口における第二水銀濃度計9Bによる下流側水銀濃度測定値に基づき、酸素濃度計7による酸素濃度そして塩化水素濃度計8による塩化水素濃度と第一水銀濃度計9Aによる上流側水銀濃度測定値に基づく制御を補完するようにして、活性炭供給量を増減するように制御する。 In this embodiment, as seen in FIG. 3, as described above, as a mercury densitometer, the first is arranged on the upstream side of the activated charcoal blowing position by the activated charcoal supply device 5 of the second embodiment described above. In addition to the mercury densitometer 9A (upstream mercury densitometer), a second mercury densitometer 9B (downstream mercury densitometer) is provided at the outlet of the bag filter 3 or the chimney 4. Similar to the second embodiment, the oxygen concentration by the oxygen concentration meter 7 and the hydrogen chloride concentration by the hydrogen chloride concentration meter 8 and the upstream mercury concentration by the first mercury concentration meter 9A on the upstream side of the activated charcoal blowing position by the activated charcoal supply device 5. The amount of activated charcoal supplied is controlled based on the measured value, and the oxygen concentration by the oxygen concentration meter 7 and the chloride by the hydrogen chloride concentration meter 8 are based on the downstream mercury concentration measurement value by the secondary mercury concentration meter 9B at the outlet of the bag filter 3. The amount of activated charcoal supplied is controlled to be increased or decreased by complementing the control based on the hydrogen concentration and the measured value of the upstream mercury concentration by the first mercury concentration meter 9A.

バグフィルタ3の出口又は煙突4における排ガス中の水銀濃度の設定値を予め定めておき、第二水銀濃度計9Bによる下流側水銀濃度測定値が該設定値を上回った場合に、活性炭供給量をさらに増加させるように制御するようにしてもよい。 The set value of the mercury concentration in the exhaust gas at the outlet of the bag filter 3 or the chimney 4 is set in advance, and when the measured value of the mercury concentration on the downstream side by the secondary mercury concentration meter 9B exceeds the set value, the amount of activated carbon supplied is determined. It may be controlled so as to further increase.

この制御を組み込むことで、第二実施形態よりもさらに確実にバグフィルタ3の出口又は煙突4における水銀濃度を設定値以下に制御することができる。 By incorporating this control, the mercury concentration at the outlet of the bug filter 3 or the chimney 4 can be controlled to a set value or less more reliably than in the second embodiment.

1 炉(焼却炉)
2 ボイラ
3 集塵装置(バグフィルタ)
4 煙突
5 活性炭供給装置
6 制御装置
7 酸素濃度計
8 塩化水素濃度計
9 水銀濃度計
9A 第一水銀濃度計(上流側水銀濃度計)
9B 第二水銀濃度計(下流側水銀濃度計)
1 furnace (incinerator)
2 Boiler 3 Dust collector (bug filter)
4 Chimney 5 Activated carbon supply device 6 Control device 7 Oxygen densitometer 8 Hydrogen chloride densitometer 9 Mercury densitometer 9A First mercury densitometer (upstream mercury densitometer)
9B Second Mercury Densitometer (Downstream Mercury Densitometer)

Claims (10)

炉から排出され水銀を含む排ガスを除塵処理する集塵装置と、炉から集塵装置へ排ガスを導く排ガス流路へ活性炭を吹き込む活性炭供給装置とを備える排ガス処理装置において、
炉の下流側でかつ集塵装置の上流側で排ガス中の酸素濃度を測定する酸素濃度計と、
炉の下流側でかつ集塵装置の上流側で排ガス中の塩化水素濃度を測定する塩化水素濃度計と、活性炭供給装置の活性炭供給量を制御する制御装置を備え、
制御装置は、酸素濃度計による酸素濃度測定値及び塩化水素濃度計による塩化水素濃度測定値に基づき、上記集塵装置の下流側での排ガス中の下流側水銀濃度を設定値以下とするように、酸素濃度測定値及び塩化水素濃度測定値と活性炭供給量との予め定める対応関係に基づき活性炭供給量を制御することを特徴とする排ガス処理装置。
In an exhaust gas treatment device including a dust collector that removes exhaust gas discharged from a furnace and contains mercury, and an activated carbon supply device that blows activated carbon into an exhaust gas flow path that guides the exhaust gas from the furnace to the dust collector.
An oxygen concentration meter that measures the oxygen concentration in the exhaust gas on the downstream side of the furnace and on the upstream side of the dust collector,
Equipped with a hydrogen chloride concentration meter that measures the hydrogen chloride concentration in the exhaust gas on the downstream side of the furnace and upstream of the dust collector, and a control device that controls the amount of activated carbon supplied by the activated carbon supply device.
The control device sets the downstream mercury concentration in the exhaust gas on the downstream side of the dust collector to the set value or less based on the oxygen concentration measurement value by the oxygen concentration meter and the hydrogen chloride concentration measurement value by the hydrogen chloride concentration meter. , An exhaust gas treatment device characterized in that the activated charcoal supply amount is controlled based on a predetermined correspondence relationship between the oxygen concentration measured value and the hydrogen chloride concentration measured value and the activated charcoal supply amount.
炉から排出され水銀を含む排ガスを除塵処理する集塵装置と、炉から集塵装置へ排ガスを導く排ガス流路へ活性炭を吹き込む活性炭供給装置とを備える排ガス処理装置において、
炉の下流側でかつ集塵装置の上流側で排ガス中の酸素濃度を測定する酸素濃度計と、炉の下流側でかつ集塵装置の上流側で排ガス中の塩化水素濃度を測定する塩化水素濃度計と、排ガス中の上流側水銀濃度を測定する上流側水銀濃度計と、活性炭供給装置の活性炭供給量を制御する制御装置を備え、
制御装置は、酸素濃度計による酸素濃度測定値及び塩化水素濃度計による塩化水素濃度測定値と上流側水銀濃度計による上流側水銀濃度測定値に基づき、上記集塵装置の下流側での排ガス中の下流側水銀濃度を設定値以下とするように、活性炭供給量を制御することを特徴とする排ガス処理装置。
In an exhaust gas treatment device including a dust collector that removes exhaust gas discharged from a furnace and contains mercury, and an activated carbon supply device that blows activated carbon into an exhaust gas flow path that guides the exhaust gas from the furnace to the dust collector.
An oxygen concentration meter that measures the oxygen concentration in the exhaust gas on the downstream side of the furnace and on the upstream side of the dust collector, and hydrogen chloride that measures the hydrogen chloride concentration in the exhaust gas on the downstream side of the furnace and on the upstream side of the dust collector. It is equipped with a densitometer, an upstream mercury densitometer that measures the upstream mercury concentration in the exhaust gas, and a control device that controls the activated charcoal supply amount of the activated charcoal supply device.
The control device is in the exhaust gas on the downstream side of the dust collector based on the oxygen concentration measurement value by the oxygen concentration meter, the hydrogen chloride concentration measurement value by the hydrogen chloride concentration meter, and the upstream mercury concentration measurement value by the upstream mercury concentration meter. An exhaust gas treatment device characterized in that the amount of activated charcoal supplied is controlled so that the mercury concentration on the downstream side of the water is set to a set value or less.
炉から排出され水銀を含む排ガスを除塵処理する集塵装置と、炉から集塵装置へ排ガスを導く排ガス流路へ活性炭を吹き込む活性炭供給装置とを備える排ガス処理装置において、
炉の下流側でかつ集塵装置の上流側で排ガス中の酸素濃度を測定する酸素濃度計と、炉の下流側でかつ集塵装置の上流側で排ガス中の塩化水素濃度を測定する塩化水素濃度計と、排ガス中の上流側水銀濃度を測定する上流側水銀濃度計と、集塵装置の下流側で排ガス中の水銀濃度を測定する下流側水銀濃度計と、活性炭供給装置の活性炭供給量を制御する制御装置を備え、
制御装置は、酸素濃度計による酸素濃度測定値及び塩化水素濃度計による塩化水素濃度測定値と、上流側水銀濃度計による上流側水銀濃度測定値と、下流側水銀濃度計による下流側水銀濃度測定値とに基づき、上記集塵装置の下流側での排ガス中の下流側水銀濃度を設定値以下とするように、活性炭供給量を制御することを特徴とする排ガス処理装置。
In an exhaust gas treatment device including a dust collector that removes exhaust gas discharged from a furnace and contains mercury, and an activated carbon supply device that blows activated carbon into an exhaust gas flow path that guides the exhaust gas from the furnace to the dust collector.
An oxygen concentration meter that measures the oxygen concentration in the exhaust gas on the downstream side of the furnace and upstream of the dust collector, and hydrogen chloride that measures the hydrogen chloride concentration in the exhaust gas on the downstream side of the furnace and upstream of the dust collector. A densitometer, an upstream mercury concentration meter that measures the upstream mercury concentration in the exhaust gas, a downstream mercury concentration meter that measures the mercury concentration in the exhaust gas on the downstream side of the dust collector, and the activated charcoal supply amount of the activated charcoal supply device. Equipped with a control device to control
The control device is the oxygen concentration measurement value by the oxygen concentration meter, the hydrogen chloride concentration measurement value by the hydrogen chloride concentration meter, the upstream mercury concentration measurement value by the upstream mercury concentration meter, and the downstream mercury concentration measurement by the downstream mercury concentration meter. An exhaust gas treatment device characterized in that the amount of activated charcoal supplied is controlled so that the concentration of mercury on the downstream side in the exhaust gas on the downstream side of the dust collector is set to a set value or less based on the value.
制御装置は、活性炭供給量を所定の最小値以上に維持するように制御することとする請求項1ないし請求項3のうちの一つに記載の排ガス処理装置。 The exhaust gas treatment device according to claim 1, wherein the control device is controlled so as to maintain the amount of activated carbon supplied to a predetermined minimum value or more. 制御装置は、上流側水銀濃度計による上流側水銀濃度測定値又は下流側水銀濃度計による下流側水銀濃度測定値が所定水銀濃度以上であるとき、活性炭供給量を所定の最大値に保つように制御することとする請求項2又は請求項3に記載の排ガス処理装置。 The control device keeps the amount of activated charcoal supplied at the specified maximum value when the measured value of the upstream mercury concentration by the upstream mercury concentration meter or the measured value of the downstream mercury concentration by the downstream mercury concentration meter is equal to or higher than the specified mercury concentration. The exhaust gas treatment apparatus according to claim 2 or claim 3, which is to be controlled. 炉から排出され水銀を含む排ガスを集塵装置で除塵処理し、炉から集塵装置へ排ガスを導く排ガス流路へ活性炭供給装置から活性炭を吹き込むこととする排ガス処理方法において、
炉の下流側でかつ集塵装置の上流側で排ガス中の酸素濃度を酸素濃度計で測定する酸素濃度計測工程と、炉の下流側でかつ集塵装置の上流側で排ガス中の塩化水素濃度を塩化水素濃度計で測定する塩化水素測定工程と、制御装置で活性炭供給装置の活性炭供給量を制御する制御工程を備え、
制御工程で、酸素濃度計による酸素濃度測定値及び塩化水素濃度計による塩化水素濃度測定値に基づき、上記集塵装置の下流側での排ガス中の下流側水銀濃度を設定値以下とするように、活性炭供給量を制御することを特徴とする排ガス処理方法。
In the exhaust gas treatment method in which the exhaust gas discharged from the furnace and containing mercury is dust-removed by the dust collector, and the activated carbon is blown from the activated carbon supply device into the exhaust gas flow path that guides the exhaust gas from the furnace to the dust collector.
An oxygen concentration measurement process that measures the oxygen concentration in the exhaust gas on the downstream side of the furnace and upstream of the dust collector with an oxygen concentration meter, and the hydrogen chloride concentration in the exhaust gas on the downstream side of the furnace and upstream of the dust collector. It is equipped with a hydrogen chloride measurement step that measures the amount of hydrogen chloride with a hydrogen chloride concentration meter and a control step that controls the amount of activated charcoal supply of the activated charcoal supply device with a control device.
In the control process, the downstream mercury concentration in the exhaust gas on the downstream side of the dust collector should be set to the set value or less based on the oxygen concentration measured value by the oxygen concentration meter and the hydrogen chloride concentration measured value by the hydrogen chloride concentration meter. , An exhaust gas treatment method characterized by controlling the amount of activated carbon supply.
炉から排出され水銀を含む排ガスを集塵装置で除塵処理し、炉から集塵装置へ排ガスを導く排ガス流路へ活性炭供給装置から活性炭を吹き込むこととする排ガス処理方法において、
炉の下流側でかつ集塵装置の上流側で排ガス中の酸素濃度を酸素濃度計で測定する酸素濃度計測工程と、炉の下流側でかつ集塵装置の上流側で排ガス中の塩化水素濃度を塩化水素濃度計で測定する塩化水素濃度測定工程と、排ガス中の上流側水銀濃度を上流側水銀濃度計で測定する上流側水銀濃度測定工程と、制御装置で活性炭供給装置の活性炭供給量を制御する制御工程を備え、
制御工程で、酸素濃度計による酸素濃度測定値及び塩化水素濃度計による塩化水素濃度測定値と上流側水銀濃度計による上流側水銀濃度測定値とに基づき、上記集塵装置の下流側での排ガス中の下流側水銀濃度を設定値以下とするように、活性炭供給量を制御することを特徴とする排ガス処理方法。
In the exhaust gas treatment method in which the exhaust gas discharged from the furnace and containing mercury is dust-removed by the dust collector, and the activated carbon is blown from the activated carbon supply device into the exhaust gas flow path that guides the exhaust gas from the furnace to the dust collector.
An oxygen concentration measurement process that measures the oxygen concentration in the exhaust gas on the downstream side of the furnace and upstream of the dust collector with an oxygen concentration meter, and the hydrogen chloride concentration in the exhaust gas on the downstream side of the furnace and upstream of the dust collector. The hydrogen chloride concentration measuring step that measures the hydrogen chloride concentration meter, the upstream mercury concentration measuring step that measures the upstream mercury concentration in the exhaust gas with the upstream mercury concentration meter, and the activated charcoal supply amount of the activated charcoal supply device with the control device. Equipped with a control process to control
In the control process, the exhaust gas on the downstream side of the dust collector is based on the oxygen concentration measurement value by the oxygen concentration meter, the hydrogen chloride concentration measurement value by the hydrogen chloride concentration meter, and the upstream mercury concentration measurement value by the upstream mercury concentration meter. An exhaust gas treatment method characterized in that the amount of activated carbon supplied is controlled so that the concentration of mercury on the downstream side of the inside is set to a set value or less.
炉から排出され水銀を含む排ガスを集塵装置で除塵処理し、炉から集塵装置へ排ガスを導く排ガス流路へ活性炭供給装置から活性炭を吹き込むこととする排ガス処理方法において、
炉の下流側でかつ集塵装置の上流側で排ガス中の酸素濃度を酸素濃度計で測定する酸素濃度計測工程と、炉の下流側でかつ集塵装置の上流側で排ガス中の塩化水素濃度を塩化水素濃度計で測定する塩化水素濃度測定工程と、排ガス中の水銀濃度を上流側水銀濃度計で測定する上流側水銀濃度測定工程と、集塵装置の下流側で排ガス中の下流側水銀濃度を下流側水銀濃度計で測定する下流側水銀濃度測定工程と、制御装置で活性炭供給装置の活性炭供給量を制御する制御工程を備え、
制御工程で、酸素濃度計による酸素濃度測定値及び塩化水素濃度計による塩化水素濃度測定値と上流側水銀濃度計による上流側水銀濃度測定値と下流側水銀濃度計による下流側水銀濃度測定値とに基づき、上記集塵装置の下流側での排ガス中の下流側水銀濃度を設定値以下とするように、活性炭供給量を制御することを特徴とする排ガス処理方法。
In the exhaust gas treatment method in which the exhaust gas discharged from the furnace and containing mercury is dust-removed by the dust collector, and the activated carbon is blown from the activated carbon supply device into the exhaust gas flow path that guides the exhaust gas from the furnace to the dust collector.
An oxygen concentration measurement process that measures the oxygen concentration in the exhaust gas on the downstream side of the furnace and upstream of the dust collector with an oxygen concentration meter, and the hydrogen chloride concentration in the exhaust gas on the downstream side of the furnace and upstream of the dust collector. The hydrogen chloride concentration measuring step that measures the mercury concentration in the exhaust gas with the hydrogen chloride concentration meter, the upstream mercury concentration measuring step that measures the mercury concentration in the exhaust gas with the upstream mercury concentration meter, and the downstream mercury in the exhaust gas on the downstream side of the dust collector. It is equipped with a downstream mercury concentration measuring step that measures the concentration with a downstream mercury concentration meter and a control step that controls the activated charcoal supply amount of the activated charcoal supply device with a control device.
In the control process, the oxygen concentration measurement value by the oxygen concentration meter, the hydrogen chloride concentration measurement value by the hydrogen chloride concentration meter, the upstream mercury concentration measurement value by the upstream mercury concentration meter, and the downstream mercury concentration measurement value by the downstream mercury concentration meter. Based on the above, an exhaust gas treatment method characterized in that the amount of activated charcoal supplied is controlled so that the concentration of mercury on the downstream side in the exhaust gas on the downstream side of the dust collector is set to a set value or less.
制御工程は、活性炭供給量を所定の最小値以上に維持するように制御することとする請求項6ないし請求項8のうちの一つに記載の排ガス処理方法。 The exhaust gas treatment method according to claim 6, wherein the control step is controlled so as to maintain the amount of activated carbon supplied to a predetermined minimum value or more. 制御工程は、上流側水銀濃度計による上流側水銀濃度測定値又は下流側水銀濃度計による下流側水銀濃度測定値が所定水銀濃度以上であるとき、活性炭供給量を所定の最大値に保つように制御することとする請求項7又は請求項8に記載の排ガス処理方法。 In the control step, when the upstream mercury concentration measurement value by the upstream mercury concentration meter or the downstream mercury concentration measurement value by the downstream mercury concentration meter is equal to or higher than the predetermined mercury concentration, the activated carbon supply amount is maintained at the predetermined maximum value. The exhaust gas treatment method according to claim 7 or claim 8, which is to be controlled.
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