TWI565514B - Method for treating acidic gas - Google Patents

Method for treating acidic gas Download PDF

Info

Publication number
TWI565514B
TWI565514B TW101124563A TW101124563A TWI565514B TW I565514 B TWI565514 B TW I565514B TW 101124563 A TW101124563 A TW 101124563A TW 101124563 A TW101124563 A TW 101124563A TW I565514 B TWI565514 B TW I565514B
Authority
TW
Taiwan
Prior art keywords
acid gas
concentration
addition amount
amount
hcl
Prior art date
Application number
TW101124563A
Other languages
Chinese (zh)
Other versions
TW201306918A (en
Inventor
益子光博
Original Assignee
栗田工業股份有限公司
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by 栗田工業股份有限公司 filed Critical 栗田工業股份有限公司
Publication of TW201306918A publication Critical patent/TW201306918A/en
Application granted granted Critical
Publication of TWI565514B publication Critical patent/TWI565514B/en

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/346Controlling the process
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/46Removing components of defined structure
    • B01D53/48Sulfur compounds
    • B01D53/50Sulfur oxides
    • B01D53/508Sulfur oxides by treating the gases with solids
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/46Removing components of defined structure
    • B01D53/68Halogens or halogen compounds
    • B01D53/685Halogens or halogen compounds by treating the gases with solids

Landscapes

  • Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (AREA)
  • Health & Medical Sciences (AREA)
  • Biomedical Technology (AREA)
  • Environmental & Geological Engineering (AREA)
  • Analytical Chemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Treating Waste Gases (AREA)
  • Control Of Non-Electrical Variables (AREA)

Description

酸性氣體的處理方法 Acid gas treatment method

本發明是有關於都市垃圾廢棄物焚燒爐、工業廢棄物焚燒爐、發電鍋爐、碳化爐、民間工廠等的燃燒設備中產生的有害氯化氫或硫氧化物等的酸性氣體的處理方法。詳細而言,是有關於有效控制處理酸性氣體的鹼劑的添加量的方法。 The present invention relates to a method for treating acid gases such as harmful hydrogen chloride or sulfur oxides generated in combustion equipment such as municipal waste waste incinerators, industrial waste incinerators, power generation boilers, carbonization furnaces, and private factories. Specifically, it is a method for effectively controlling the amount of addition of an alkali agent for treating an acid gas.

含有有害的氯化氫或硫氧化物的廢氣藉由氫氧化鈣或碳酸氫鈉等鹼劑處理後,藉由過濾袋(BF,bag filter)等集塵機除塵後,自煙囪排出。另一方面,藉由集塵機集塵的飛灰含有有害的Pb、Cd等重金屬類,將這些有害重金屬穩定化處理後,進行掩埋處理。 The exhaust gas containing harmful hydrogen chloride or sulfur oxide is treated with an alkali agent such as calcium hydroxide or sodium hydrogencarbonate, and then dedusted by a dust collector such as a filter bag (BF, bag filter), and then discharged from the chimney. On the other hand, the fly ash collected by the dust collector contains harmful heavy metals such as Pb and Cd, and these harmful heavy metals are stabilized and then subjected to burying treatment.

作為對酸性氣體進行處理的鹼劑,即,經微粉加工成5μm~30μm的碳酸氫鈉,與氫氧化鈣相比反應性更高,可穩定地處理酸性氣體,並且未反應成分少,可削減掩埋處理量,是對降低環境負荷較為有效的方法。另外,重金屬處理方法通常是藉由二乙基二硫代胺基甲酸鹽等螯合物進行不溶化處理的方法,短期而言,重金屬固定效果較高,但殘留以下問題:由於最終處理場中因酸雨引起的pH值降低及螯合物的氧化自我分解,而鉛等重金屬再溶出。另一方面,藉由磷酸等磷酸化合物的重金屬固定,由於變化至作為無機礦物的羥基磷灰石(hydroxyapatite)形態,因而最終處理場中的長期穩定性優異,就環境保護的觀點而 言,是價值非常高的處理方法。而且,藉由磷酸等重金屬固定劑對利用上述微粉碳酸氫鈉處理的飛灰進行處理的方法,是具有使大部分的環境負荷降低的效果的有效方法。 As an alkali agent for treating an acid gas, that is, sodium bicarbonate processed to 5 μm to 30 μm by fine powder, it has higher reactivity than calcium hydroxide, and can stably treat acid gas, and has less unreacted components, and can be reduced. The amount of buried treatment is a more effective method for reducing environmental load. In addition, the heavy metal treatment method is usually a method of insolubilizing treatment by a chelate compound such as diethyldithiocarbamate, and in the short term, the heavy metal fixing effect is high, but the following problems remain: due to the final treatment field The pH value due to acid rain decreases and the oxidative self-decomposition of the chelate compound, and heavy metals such as lead dissolve again. On the other hand, the fixation with a heavy metal of a phosphoric acid compound such as phosphoric acid changes to a form of hydroxyapatite which is an inorganic mineral, so that the long-term stability in the final treatment field is excellent, and from the viewpoint of environmental protection. Words are very high value processing methods. Further, the method of treating the fly ash treated with the above-mentioned fine powder of sodium hydrogencarbonate by a heavy metal fixing agent such as phosphoric acid is an effective method for reducing the environmental load.

然而,控制對氯化氫或硫氧化物等酸性氣體進行處理的氫氧化鈣或碳酸氫鈉等鹼劑的添加量,不僅可削減酸性氣體處理費用,而且可期待降低鹼劑的未反應成分、削減飛灰的掩埋處理量的效果。 However, the addition of an alkali agent such as calcium hydroxide or sodium hydrogencarbonate to treat an acid gas such as hydrogen chloride or sulfur oxide can not only reduce the cost of acid gas treatment, but also reduce the unreacted component of the alkali agent and reduce the fly. The effect of the burial throughput of ash.

對氯化氫或硫氧化物等酸性氣體進行處理的鹼劑的添加量,通常亦根據藉由設置於過濾袋的後段的離子電極式氯化氫測定裝置而測定的HCl濃度,藉由比例積分微分(ProportionIntegralDifferential,PID)控制裝置進行反饋控制。然而,在焚燒設備等燃燒設備中,通常不設置測定入口的酸性氣體濃度的裝置,在未知入口的變動狀況的狀態下設定PID控制的參數並調整控制輸出。然而,PID控制裝置具有P、I、D、添加量(輸出)下限、添加量(輸出)上限這5個設定項,並且各項的設定值複合而決定控制輸出值,因此研究適當的添加控制需要大量的時間。因此,通常在PID控制裝置的設定超過控制目標值(SV)時,大多數設備實施大幅度增加添加量的控制。 The amount of the alkali agent to be treated for an acid gas such as hydrogen chloride or sulfur oxide is usually also based on the HCl concentration measured by the ion electrode type hydrogen chloride measuring device provided in the subsequent stage of the filter bag, by proportional integral differentiation (ProportionIntegralDifferential, The PID) control device performs feedback control. However, in a combustion apparatus such as an incineration facility, a device for measuring the acid gas concentration at the inlet is generally not provided, and the PID control parameter is set and the control output is adjusted in a state where the inlet is not changed. However, the PID control device has five setting items of P, I, D, the addition amount (output) lower limit, and the addition amount (output) upper limit, and the set values of the respective items are combined to determine the control output value, so the appropriate addition control is studied. It takes a lot of time. Therefore, generally, when the setting of the PID control device exceeds the control target value (SV), most devices implement control that greatly increases the amount of addition.

然而,通常的PID控制裝置的控制輸出僅設定單一的上限,例如將HCl濃度的控制目標值(SV)設定為40ppm的情況下,在40ppm以上的濃度下將控制輸出的單一的上限作為限度而添加鹼劑,導致過量添加鹼劑。另外,上述反饋控制受到酸性氣體測定裝置的計測延遲的影響。過 濾袋出口的HCl濃度通常藉由離子電極法(例如京都電子工業製造的HL-36)進行測定,硫氧化物濃度藉由紅外線吸收法(例如島津製作所製造的NSA-3080)進行測定,但若包括試樣廢氣的取樣時間、及計測器的響應時間,則具有5分鐘~10分鐘的較大的計測延遲。此計測延遲成為引起鹼劑的添加延遲、導致酸性氣體的處理不良、並引起鹼劑的過量添加的原因。 However, the control output of the normal PID control device sets only a single upper limit. For example, when the control target value (SV) of the HCl concentration is set to 40 ppm, the single upper limit of the control output is limited to a concentration of 40 ppm or more. The addition of an alkaline agent results in an excessive addition of an alkaline agent. Further, the above feedback control is affected by the measurement delay of the acid gas measuring device. Over The HCl concentration at the outlet of the filter bag is usually measured by an ion electrode method (for example, HL-36 manufactured by Kyoto Electronics Industry Co., Ltd.), and the sulfur oxide concentration is measured by an infrared absorption method (for example, NSA-3080 manufactured by Shimadzu Corporation). The sampling time including the sample exhaust gas and the response time of the measuring device have a large measurement delay of 5 minutes to 10 minutes. This measurement delay causes a delay in the addition of the alkali agent, causes poor treatment of the acid gas, and causes excessive addition of the alkali agent.

為了解決本課題而研究各種控制方法。專利文獻1中,提出在通常的PID控制式中進一步添加P的「P+PID控制」。本提案考慮了藉由通常的PID控制難以應對酸性氣體的突然產生。另外,專利文獻2及專利文獻3中提出,將根據入口的酸性氣體濃度決定鹼劑的添加量的前饋控制、與根據經鹼劑處理後的酸性氣體濃度補充鹼劑的添加量的反饋控制加以組合的控制方式。一般認為,此控制方式希望抑制反饋控制的過量添加的效果,並獲得酸性氣體的穩定處理與削減鹼劑的過量添加的效果。 In order to solve this problem, various control methods are studied. Patent Document 1 proposes to further add "P+PID Control" of P to a normal PID control formula. This proposal considers that it is difficult to cope with the sudden generation of acid gas by the usual PID control. Further, in Patent Document 2 and Patent Document 3, it is proposed to control the feedforward control of the amount of the alkali agent added according to the acid gas concentration of the inlet and the feedback control of the amount of the alkali agent added according to the acid gas concentration after the alkali treatment. The combination of control methods. It is considered that this control method is intended to suppress the effect of excessive addition of feedback control, and to obtain an effect of stabilizing the acid gas and reducing the excessive addition of the alkali agent.

[先前技術文獻] [Previous Technical Literature] [專利文獻] [Patent Literature]

[專利文獻1]日本專利特開2002-113327號公報 [Patent Document 1] Japanese Patent Laid-Open Publication No. 2002-113327

[專利文獻2]日本專利特開平10-165752號公報 [Patent Document 2] Japanese Patent Laid-Open No. Hei 10-165752

[專利文獻3]日本專利特開2006-75758號公報 [Patent Document 3] Japanese Patent Laid-Open Publication No. 2006-75758

然而,專利文獻1中,能夠一定程度地應對在入口處突然產生的酸性氣體,但控制輸出的上限值及下限值為單一設定,因此在入口酸性氣體濃度的變動激烈的設備中, 會因藥劑而引起亂調(hunting),因此難以實現出口酸性氣體濃度的峰值較少而穩定的處理。另外,不考慮上述測定裝置的計測延遲,而無法應對因計測延遲引起的鹼劑的添加延遲所導致的酸性氣體的處理不良。而且,專利文獻2及專利文獻3中提出,在焚燒設備等燃燒設備中,僅計測出口的酸性氣體濃度的設備佔多數,為了實施此控制方式,而需要導入計測入口的酸性氣體濃度的新的高價的酸性氣體測定裝置。 However, in Patent Document 1, the acid gas suddenly generated at the inlet can be dealt with to some extent, but the upper limit value and the lower limit value of the control output are individually set. Therefore, in a device in which the fluctuation of the inlet acid gas concentration is intense, It causes hunting due to the drug, so it is difficult to achieve a stable and stable treatment of the peak value of the outlet acid gas concentration. Further, irrespective of the measurement delay of the above-described measuring device, it is not possible to cope with the processing failure of the acid gas due to the delay in the addition of the alkaline agent due to the measurement delay. Further, Patent Document 2 and Patent Document 3 propose that in a combustion apparatus such as an incineration facility, only a device that measures the acid gas concentration of the outlet is dominant, and in order to implement this control method, it is necessary to introduce a new acid gas concentration of the measurement inlet. High-priced acid gas measuring device.

考慮到上述先前情況,本發明的目的是提供酸性氣體處理方法,其在無須導入新的高價的酸性氣體測定裝置的反饋形式中,進行出口的酸性氣體濃度的峰值產生較少而穩定的酸性氣體處理,並且利用用以削減鹼劑的過量添加的新的控制方式。 In view of the foregoing prior circumstances, it is an object of the present invention to provide an acid gas treatment method which produces a less stable acid gas at the peak of the acid gas concentration at the outlet without feedback of a new high-priced acid gas measuring device. The treatment is followed by a new control method to reduce the excessive addition of the alkaline agent.

(1)一種酸性氣體的處理方法,其在含有酸性氣體的燃燒廢氣中添加鹼劑,根據測定將粉塵集塵後的酸性氣體濃度的酸性氣體濃度測定設備的測定信號,對鹼劑的添加量進行反饋控制,且包括:算出至少與平均時間(例如後述的5分鐘、15分鐘、30分鐘、1小時、3小時、6小時等)相對應的平均添加量乘以1倍以下的係數(例如後述的95%、90%、80%、70%、50%等)而得的基礎添加量的步驟;根據上述算出的基礎添加量藉由反饋運算而算出鹼劑的添加量輸出值的步驟。 (1) An acid gas treatment method in which an alkali agent is added to a combustion exhaust gas containing an acid gas, and a measurement signal of an acid gas concentration measuring device that measures an acid gas concentration after dust collection is added to an alkali agent. Performing feedback control includes: calculating a coefficient that is at least equal to an average addition amount (for example, 5 minutes, 15 minutes, 30 minutes, 1 hour, 3 hours, 6 hours, and the like described later) multiplied by 1 time or less (for example, a step of adding a base amount obtained by 95%, 90%, 80%, 70%, 50%, etc., which will be described later, and a step of calculating an output value of the addition amount of the alkali agent by a feedback calculation based on the calculated basic addition amount.

現狀主要使用的PID控制中,添加輸出僅可設定單一 的上限與下限。因此,例如將出口HCl濃度的控制目標值(SV)設定為40ppm的情況下,在實際的出口HCl濃度為40ppm以下時,為了減少鹼劑的添加,而以控制輸出的下限添加,在控制目標值(SV)40ppm以上時,為了增加鹼劑的添加,而以控制輸出的上限添加,如此反覆的鹼劑的不恰當添加(過量添加、不足添加),而使出口的HCl濃度發生較大變動,並且成為鹼劑的過量添加的原因。 In the current PID control, the added output can only be set to a single Upper and lower limits. Therefore, for example, when the control target value (SV) of the outlet HCl concentration is set to 40 ppm, when the actual outlet HCl concentration is 40 ppm or less, in order to reduce the addition of the alkaline agent, the lower limit of the control output is added, and the control target is added. When the value (SV) is 40 ppm or more, in order to increase the addition of the alkali agent, the upper limit of the control output is added, and the alkaline agent thus added is improperly added (excessive addition or insufficient addition), and the HCl concentration at the outlet is largely changed. And become the cause of excessive addition of the alkaline agent.

相對於此,如(1)的發明般,算出至少與平均時間相對應的平均添加量乘以1倍以下的係數而得的基礎添加量,根據算出的基礎添加量藉由反饋運算而算出鹼劑的添加量輸出值時,可防止鹼劑的不恰當添加,並可實現應處理的出口HCl濃度的變動少而穩定的處理,並且根據(1)的發明的適當添加的結果,亦可削減鹼劑的添加量。 On the other hand, as in the invention of (1), the basic addition amount obtained by multiplying the average addition amount corresponding to the average time by a factor of 1 or less is calculated, and the base is calculated by the feedback calculation based on the calculated basic addition amount. When the addition amount of the agent is added, it is possible to prevent the improper addition of the alkali agent, and it is possible to achieve a stable treatment with a small fluctuation in the concentration of the outlet HCl to be treated, and it is also possible to reduce the result of the appropriate addition of the invention according to (1). The amount of the alkali agent added.

(1)的發明具有如下特徵:作為與先前在反饋控制中無法考慮的入口的HCl濃度相關的因素,而著眼於過去平均添加量,應用過去平均添加量乘以1倍以下的係數而得的基礎添加量作為控制因素。藉此,無須如先前般使下限與上限反覆大幅變動而進行鹼劑的添加,而是將作為添加量的基礎具有妥當性的過去平均添加量乘以1倍以下的係數而得的基礎添加量作為基礎,藉由例如PID等反饋控制算出鹼劑的添加量。因此,鹼劑的添加變動變少,抑制鹼劑自身的添加不良(過量添加、不足添加)引起的亂調,藉由進行恰當的添加而可實現添加量削減,並可實現變動較少的酸性氣體的穩定處理。 The invention of (1) is characterized in that, as a factor relating to the HCl concentration of the inlet which was previously unconsidered in the feedback control, focusing on the past average addition amount, a coefficient obtained by multiplying the average addition amount by a factor of 1 or less is used. The amount of base added is used as a controlling factor. In this way, it is not necessary to increase the lower limit and the upper limit in a large amount, and the base additive is added, and the base addition amount obtained by multiplying the past average addition amount which is a basis for the addition amount by a factor of 1 or less is used. On the basis of this, the amount of addition of the alkaline agent is calculated by feedback control such as PID. Therefore, the fluctuation of the addition of the alkali agent is reduced, and the disorder of the addition of the alkali agent itself (excessive addition or insufficient addition) is suppressed, and the addition amount can be reduced by appropriate addition, and the acidity with less variation can be realized. Stable treatment of gas.

(2)如(1)所述之酸性氣體的處理方法,其中在上述藉由反饋運算而算出添加量輸出值的步驟中,將上述算出的基礎添加量作為上述鹼劑的添加量輸出值的下限值(例如後述的LO:添加量下限)。 (2) The method for treating an acid gas according to (1), wherein in the step of calculating the addition amount output value by the feedback calculation, the calculated base addition amount is used as an output value of the addition amount of the alkaline agent. Lower limit value (for example, LO to be described later: lower limit of addition amount).

根據(2)的發明,藉由將基礎添加量作為添加量輸出值的下限值,以該基礎添加量為基礎,藉由先前的反饋運算而調整添加量的過量與不足,因此可使鹼劑的添加適當化,而有效地處理酸性氣體。 According to the invention of (2), by using the base addition amount as the lower limit value of the addition amount output value, based on the base addition amount, the excess amount and the shortage of the addition amount are adjusted by the previous feedback calculation, so that the base can be used. The addition of the agent is appropriate to effectively treat the acid gas.

另外,平均添加量的平均時間並無特別限制,較為有效的是應用添加量的移動平均等的平均值,且較佳為在平均時間為5分鐘以上、15小時~24小時左右下應用。另外,由基礎添加量規定的係數較佳為1倍以下。在使用1倍以上的係數時,雖然可實現酸性氣體的穩定處理,但會妨礙入口酸性氣體濃度的減少所伴隨的添加量的減少,因此會成為過量添加。基礎添加量只要是平均添加量的1倍以下(係數100%以下)即可,特佳為0.5倍~0.95倍(50%~95%)、特別是0.7倍~0.9倍(70%~90%)。 Further, the average time of the average addition amount is not particularly limited, and is preferably an average value of the moving average of the applied amount, and is preferably applied at an average time of 5 minutes or more and 15 hours to 24 hours. Further, the coefficient defined by the amount of base addition is preferably 1 time or less. When the coefficient of one time or more is used, although the stabilization treatment of the acid gas can be achieved, the decrease in the amount of addition accompanying the decrease in the concentration of the inlet acid gas is hindered, and thus the addition is excessive. The base addition amount may be 1 time or less (a coefficient of 100% or less) of the average addition amount, and particularly preferably 0.5 times to 0.95 times (50% to 95%), particularly 0.7 times to 0.9 times (70% to 90%). ).

(3)如(1)或(2)所述之酸性氣體的處理方法,其中上述藉由反饋運算而算出添加量輸出值的步驟進一步包括:設定至少2個酸性氣體濃度的斜率的範圍(例如後述的最接近的HCl濃度的斜率的6秒平均為正的範圍及負的範圍等)的步驟;對上述至少2個斜率的範圍的每個範圍設定酸性氣體濃度的控制目標值(例如後述的實例8中的180ppm、220ppm等)的步驟;至少根據上述測定信號及 上述斜率的範圍的每個範圍的控制目標值,算出鹼劑的添加量輸出值的步驟;在上述設定控制目標值的步驟中,在上述酸性氣體濃度的斜率的範圍較大時(例如後述的最接近的HCl濃度的斜率的6秒平均為正時(酸性氣體濃度上升時))所設定的控制目標值,小於在上述酸性氣體濃度的斜率的範圍較小時(例如後述的最接近的HCl濃度的斜率的6秒平均為負時(酸性氣體濃度下降時))所設定的控制目標值。 (3) The method for treating an acid gas according to (1) or (2), wherein the step of calculating the addition amount output value by the feedback calculation further comprises: setting a range of a slope of at least two acid gas concentrations (for example, a step of equalizing a range of the closest HCl concentration to be described later, which is a positive range and a negative range, and the like; and setting a control target value of the acid gas concentration for each of the ranges of the at least two slopes (for example, described later) Step of 180 ppm, 220 ppm, etc. in Example 8; at least according to the above-mentioned measurement signal and a step of calculating an additive amount of the alkali agent in the range of the control target value of each range of the slope; and a step of setting the control target value, when the range of the slope of the acid gas concentration is large (for example, described later) The control target value set when the average of 6 seconds of the slope of the closest HCl concentration is positive (when the acid gas concentration is raised) is smaller than when the range of the slope of the acid gas concentration is small (for example, the closest HCl described later) The control target value set when the average of 6 seconds of the slope of the concentration is negative (when the acid gas concentration is lowered).

根據(3)的發明,在過濾袋出口的酸性氣體濃度的斜率的範圍較大時(酸性氣體濃度上升時),與斜率的範圍較小時(酸性氣體濃度下降時)相比,酸性氣體濃度的控制目標值減小,因此與酸性氣體濃度下降時相比,可增大在酸性氣體濃度上升時的鹼劑添加量輸出值。因此,與現狀控制相比,可加快在酸性氣體濃度增加時添加鹼劑的時序,可改善因酸性氣體測定裝置的計測延遲引起的酸性氣體的處理不良。 According to the invention of (3), when the range of the slope of the acid gas concentration at the outlet of the filter bag is large (when the acid gas concentration is increased), the acid gas concentration is smaller than when the range of the slope is small (when the acid gas concentration is lowered) Since the control target value is decreased, the output value of the alkali agent addition amount when the acid gas concentration is increased can be increased as compared with when the acid gas concentration is lowered. Therefore, compared with the current state control, the timing of adding the alkaline agent at the time of increasing the acid gas concentration can be accelerated, and the processing failure of the acid gas due to the measurement delay of the acid gas measuring device can be improved.

另外,反之,與酸性氣體濃度上升時相比,可減少在酸性氣體濃度下降時的鹼劑添加量,因此在酸性氣體濃度減少時可快速降低鹼劑添加量,並可降低因酸性氣體測定裝置的計測延遲引起的過量添加。 On the other hand, the amount of the alkali agent added when the acid gas concentration is lowered can be reduced as compared with the case where the acid gas concentration is increased. Therefore, when the acid gas concentration is decreased, the amount of the alkali agent can be rapidly decreased, and the acid gas measuring device can be lowered. The excessive delay caused by the measurement delay.

(4)如(1)至(3)中任一項所述之酸性氣體的處理方法,其中上述藉由反饋運算而算出添加量輸出值的步驟進一步包括如下步驟:在根據上述測定信號而運算的添加量輸出值的下限值(例如後述的表2、表3、表5的LO) 與上限值(例如後述的表2、表3、表5的LH[控制輸出上限])之間,對應上述酸性氣體濃度(例如後述的表2、表3、表5的BF出口HCl濃度)而設定1個以上的上述添加量輸出值的新的上限值(例如後述的表2、表3、表5的LM1[輸出限制1]、LM2[輸出限制2])。通常的反饋運算中的輸出上限僅有1個,若酸性氣體濃度為控制目標值以上,則不論入口的酸性氣體濃度的大小,均可添加鹼劑至上限值,從而引起過量添加。 (4) The method for processing an acid gas according to any one of (1) to (3), wherein the step of calculating the addition amount output value by the feedback calculation further comprises the step of: calculating according to the measurement signal Lower limit value of the added amount output value (for example, LO of Table 2, Table 3, and Table 5 described later) The upper limit value (for example, LH [control output upper limit] of Table 2, Table 3, and Table 5 to be described later) corresponds to the acid gas concentration (for example, BF outlet HCl concentration in Tables 2, 3, and 5 described later). On the other hand, a new upper limit value of one or more of the added amount output values is set (for example, LM1 [output limit 1] and LM2 [output limit 2] of Table 2, Table 3, and Table 5 to be described later). In the normal feedback calculation, the upper limit of the output is only one. If the acid gas concentration is equal to or higher than the control target value, the alkali agent may be added to the upper limit regardless of the acid gas concentration at the inlet, thereby causing excessive addition.

相對於此,根據(4)的發明,藉由在添加量輸出值的下限值與上限值之間施加與當前的酸性氣體濃度相對應的控制輸出的限制,而可根據酸性氣體濃度的大小而實現鹼劑的適當的添加,並可實現添加量的削減。 On the other hand, according to the invention of (4), the restriction of the control output corresponding to the current acid gas concentration is applied between the lower limit value and the upper limit value of the added amount output value, and the acid gas concentration can be used. The appropriate addition of the alkali agent is achieved in size, and the amount of addition can be reduced.

(5)如(1)至(4)中任一項所述之酸性氣體的處理方法,其中在算出上述基礎添加量的步驟中,將移動平均時間為5分鐘以上時的平均添加量的0.5倍~0.95倍設為基礎添加量。 (5) The method for treating an acid gas according to any one of (1) to (4), wherein, in the step of calculating the base addition amount, 0.5 of an average addition amount when the moving average time is 5 minutes or longer The ratio of ~0.95 times is set as the base addition amount.

如上所述,平均添加量的平均時間並無特別限制,較為有效的是應用添加量的移動平均等的平均值,且較佳為在平均時間為5分鐘以上、15小時~24小時左右下應用。另外,由基礎添加量規定的係數較佳為1倍以下。在使用1倍以上的係數時,雖然可實現酸性氣體的穩定處理,但會妨礙入口酸性氣體濃度的減少所伴隨的添加量的減少,因此成為過量添加。基礎添加量只要是平均添加量的1倍以下(係數100%以下)即可,特佳為0.5倍~0.95倍(50% ~95%)、特別是0.7倍~0.9倍(70%~90%)。 As described above, the average time of the average addition amount is not particularly limited, and it is effective to apply an average value of the moving average or the like of the added amount, and it is preferably applied at an average time of 5 minutes or more and 15 hours to 24 hours or so. . Further, the coefficient defined by the amount of base addition is preferably 1 time or less. When the coefficient of one time or more is used, although the stabilization treatment of the acid gas can be achieved, the decrease in the amount of addition accompanying the decrease in the concentration of the inlet acid gas is hindered, and thus the addition is excessive. The amount of the base addition may be 1 time or less (a coefficient of 100% or less) of the average addition amount, and particularly preferably 0.5 to 0.95 times (50%). ~95%), especially 0.7 times to 0.9 times (70% to 90%).

因此,根據(5)的發明,可進行酸性氣體的穩定處理並防止鹼劑的過量添加。 Therefore, according to the invention of (5), the stabilization treatment of the acid gas can be performed and the excessive addition of the alkali agent can be prevented.

(6)如(1)至(5)中任一項所述之酸性氣體的處理方法,其中上述藉由反饋運算而算出添加量輸出值的步驟進一步包括:除了該反饋運算外,使用根據氯化氫濃度運算的控制輸出、與根據硫氧化物濃度運算的控制輸出這兩個輸出來算出鹼劑的添加量輸出值的步驟。 (6) The method for treating an acid gas according to any one of (1) to (5), wherein the step of calculating an additive amount output value by a feedback operation further comprises: using hydrogen chloride according to the feedback operation The step of calculating the addition amount of the alkali agent by the two outputs of the control output of the concentration calculation and the control output calculated based on the sulfur oxide concentration.

在工業廢棄物焚燒爐或民間工廠的燃燒設備中,多數情況下氯化氫與硫氧化物以高濃度產生。此時,氯化氫與硫氧化物這兩者成為處理對象,例如藉由將根據設置於過濾袋後段的氯化氫濃度測定裝置的氯化氫濃度而求出的控制輸出、與根據硫氧化物濃度而求出的控制輸出相加,而可穩定處理氯化氫及硫氧化物這兩種酸性氣體。 In the combustion equipment of industrial waste incinerators or private factories, in most cases, hydrogen chloride and sulfur oxides are produced at a high concentration. In this case, both of hydrogen chloride and sulfur oxide are treated, and for example, a control output obtained based on the hydrogen chloride concentration of the hydrogen chloride concentration measuring device provided in the subsequent stage of the filter bag, and a sulfur oxide concentration are obtained. The control outputs are added, and the two acid gases of hydrogen chloride and sulfur oxide are stably treated.

因此,根據(6)的發明,可穩定處理氯化氫及硫氧化物這兩種酸性氣體。 Therefore, according to the invention of (6), the acid gases of hydrogen chloride and sulfur oxide can be stably treated.

(7)如(1)至(6)中任一項所述之酸性氣體的處理方法,其中上述藉由反饋運算而算出添加量輸出值的步驟除了該反饋運算外進一步包括:根據氯化氫濃度及/或硫氧化物濃度的平均值算出鹼劑的添加量輸出值的步驟。 (7) The method for treating an acid gas according to any one of (1) to (6), wherein the step of calculating an addition amount output value by a feedback operation further includes: according to the hydrogen chloride concentration and / or the average value of the sulfur oxide concentration is a step of calculating the output value of the addition amount of the alkali agent.

然而,酸性氣體的排出濃度管理有藉由各酸性氣體濃度(氯化氫濃度、硫氧化物濃度)的1小時平均值進行管理的設備。通常設置控制目標值(SV)進行控制,但控制目標值只不過是目標,往往有成為超過所控制的結果目標 值的濃度的情況。特別是添加量削減與酸性氣體的穩定處理是相反的概念,因此越要求添加量削減,則1小時平均值超過管理值的風險越大。此時,在酸性氣體濃度到達1小時平均管理值以上、或接近1小時平均管理值的濃度時,藉由添加大量的鹼劑(規定某固定添加量),而可實現添加量削減與酸性氣體的穩定處理可並存的安心度高的控制。 However, the discharge concentration of the acid gas is managed by an average value of one hour of each acid gas concentration (hydrogen chloride concentration, sulfur oxide concentration). The control target value (SV) is usually set for control, but the control target value is only the target, and often becomes the target of the controlled result. The case of the concentration of the value. In particular, the reduction in the amount of addition is contrary to the concept of stabilization of the acid gas. Therefore, the more the amount of addition is required, the greater the risk that the average value of one hour exceeds the management value. In this case, when the acid gas concentration reaches a concentration equal to or higher than the one-hour average management value or close to the one-hour average management value, the addition amount can be reduced and the acid gas can be obtained by adding a large amount of an alkali agent (predetermined by a certain fixed addition amount). The stable handling can coexist with a high degree of peace of mind.

因此,根據(7)的發明,根據氯化氫濃度及/或硫氧化物濃度的平均值,算出鹼劑的添加量輸出值,因此可實現添加量削減與酸性氣體的穩定處理可並存的安心度高的控制。 Therefore, according to the invention of (7), the output value of the addition amount of the alkali agent is calculated from the average value of the hydrogen chloride concentration and/or the sulfur oxide concentration, so that the reduction in the amount of addition and the stabilization of the acid gas can be achieved. control.

(8)如(1)至(7)中任一項所述之酸性氣體的處理方法,其中上述鹼劑是平均粒徑為5μm~30μm的微粉碳酸氫鈉。 (8) The method for treating an acid gas according to any one of (1) to (7) wherein the alkali agent is a fine powder of sodium hydrogencarbonate having an average particle diameter of 5 μm to 30 μm.

本發明所用的鹼劑並無特別限制。特別是與酸性氣體的反應快的平均粒徑被調整為5μm~30μm的微粉碳酸氫鈉,控制響應性佳,可有效地發揮本發明的控制方法的性能。另外,亦可應用氫氧化鈣。此時,即便是JIS特號氫氧化鈣亦可應用,但使用與酸性氣體的反應性高的比表面積為例如30m2/g以上的高比表面積的氫氧化鈣,更可發揮本發明的性能。 The alkali agent used in the present invention is not particularly limited. In particular, the average particle diameter of the reaction with the acid gas is adjusted to a fine powder of sodium bicarbonate of 5 μm to 30 μm, and the control responsiveness is good, and the performance of the control method of the present invention can be effectively exhibited. In addition, calcium hydroxide can also be used. In this case, even if it is JIS-specific calcium hydroxide, it is possible to exhibit the performance of the present invention by using calcium hydroxide having a high specific surface area of, for example, 30 m 2 /g or more having a high reactivity with an acid gas. .

(9)如(8)所述之酸性氣體的處理方法,其中併用與上述微粉碳酸氫鈉不同的其他鹼劑。 (9) The method for treating an acid gas according to (8), wherein another alkali agent different from the above-mentioned fine powder sodium hydrogencarbonate is used in combination.

發揮本發明的效果的鹼劑並無特別限制。微粉碳酸氫 鈉以外的鹼劑可例示:氫氧化鈣、碳酸鈉、碳酸氫鉀、碳酸鉀、倍半碳酸鈉、天然蘇打、氫氧化鈉、氫氧化鉀、氧化鎂、氫氧化鎂等。另外,在鹼劑為粉體時,較佳為與酸性氣體的反應性高的粒徑小於30μm、特別是5μm~20μm的微粉。可應用預先調整了粒徑的劑材,可在現場設置粉碎設備,一邊在現場將粒徑粗的鹼劑粉碎一邊添加。另外,亦可藉由將各鹼劑溶解於水而成的漿料或水溶液進行實施。 The alkaline agent which exerts the effect of the present invention is not particularly limited. Micronized hydrogen carbonate The alkali agent other than sodium may, for example, be calcium hydroxide, sodium carbonate, potassium hydrogencarbonate, potassium carbonate, sodium sesquicarbonate, natural soda, sodium hydroxide, potassium hydroxide, magnesium oxide or magnesium hydroxide. Further, when the alkali agent is a powder, it is preferably a fine powder having a particle diameter of at least 30 μm, particularly 5 μm to 20 μm, which is highly reactive with an acid gas. It is possible to apply a pre-adjusted particle size, and it is possible to provide a pulverizing device on site, and to pulverize the coarse-grained alkaline agent on site. Further, it may be carried out by a slurry or an aqueous solution obtained by dissolving each alkali agent in water.

(10)如(9)所述之酸性氣體的處理方法,其中上述其他鹼劑是選自由氫氧化鈣、氫氧化鈉、氫氧化鎂、氧化鎂、碳酸鈉、倍半碳酸鈉、天然蘇打、及粗碳酸氫鈉所組成群組中的至少1種鹼劑。 (10) The method for treating an acid gas according to (9), wherein the other alkali agent is selected from the group consisting of calcium hydroxide, sodium hydroxide, magnesium hydroxide, magnesium oxide, sodium carbonate, sodium sesquicarbonate, natural soda, And at least one alkali agent in the group consisting of crude sodium hydrogencarbonate.

併用與實施本發明的控制的鹼劑不同的廉價的鹼劑,亦成為於經濟上有效的方法。所併用的鹼劑並無限制,通常使用的廉價的鹼劑可例示:氫氧化鈣、氫氧化鈉、氫氧化鎂、氧化鎂、碳酸鈉、倍半碳酸鈉、天然蘇打、粗碳酸氫鈉。 It is also an economically effective method to use an inexpensive alkaline agent different from the alkaline agent for controlling the present invention. The alkali agent to be used in combination is not limited, and an inexpensive alkali agent which is usually used may, for example, be calcium hydroxide, sodium hydroxide, magnesium hydroxide, magnesium oxide, sodium carbonate, sodium sesquicarbonate, natural soda or crude sodium hydrogencarbonate.

根據本發明,可提供酸性氣體處理方法,其在無須導入新的高價的酸性氣體測定裝置的反饋形式中,進行出口的酸性氣體濃度的峰值產生較少而穩定的酸性氣體處理,並且利用用以削減鹼劑的過量添加的新的控制方式。 According to the present invention, it is possible to provide an acid gas treatment method in which a peak of an acid gas concentration at an outlet is generated in a feedback form in which a new high-priced acid gas measuring device is not required to be introduced, and a less stable acid gas treatment is used, and A new way of controlling the excessive addition of alkaline agents.

以下,列舉實施形態對本發明進行更具體地說明,但 本發明並不限定於此。 Hereinafter, the present invention will be more specifically described by way of embodiments, but The present invention is not limited to this.

圖1是表示焚燒設備中在作為廢氣的HCl中添加微粉碳酸氫鈉的酸性氣體處理系統1的構成的方塊圖。 Fig. 1 is a block diagram showing the configuration of an acid gas treatment system 1 in which a fine powder of sodium hydrogencarbonate is added to HCl as an exhaust gas in an incineration facility.

酸性氣體處理系統1包含控制裝置11、微粉碳酸氫鈉添加裝置12、過濾袋13、HCl濃度測定設備14。控制裝置11根據由HCl濃度測定設備14發送的HCl濃度測定信號、及由過去的平均添加量算出的基礎添加量,藉由反饋控制(PID控制方式或步進方式)算出微粉碳酸氫鈉的添加量輸出值。微粉碳酸氫鈉添加裝置12根據控制裝置11所算出的微粉碳酸氫鈉的添加量輸出值向廢氣中的HCl添加微粉碳酸氫鈉。 The acid gas treatment system 1 includes a control device 11, a fine powder sodium hydrogencarbonate addition device 12, a filter bag 13, and an HCl concentration measuring device 14. The control device 11 calculates the addition of the fine powder sodium bicarbonate by feedback control (PID control method or step method) based on the HCl concentration measurement signal transmitted from the HCl concentration measuring device 14 and the basic addition amount calculated from the past average addition amount. The output value. The fine powder sodium hydrogencarbonate addition device 12 adds the fine powder sodium hydrogencarbonate to the HCl in the exhaust gas based on the output value of the added amount of the fine powder sodium hydrogencarbonate calculated by the control device 11.

另外,基礎添加量是與平均時間(例如移動平均時間)相對應的過去的平均添加量乘以1倍以下的係數而算出。 Further, the base addition amount is calculated by multiplying the average addition amount of the past corresponding to the average time (for example, the moving average time) by a factor of 1 or less.

過濾袋13將廢氣中的HCl與微粉碳酸氫鈉反應後的粉塵除去。HCl濃度測定設備14測定過濾袋13上蓄積的微粉碳酸氫鈉(藉由與廢氣中的HCl反應而殘存的微粉碳酸氫鈉蓄積在過濾袋13上)與廢氣反應後的HCl反應後的HCl濃度(後述的過濾袋出口HCl濃度),而將HCl濃度測定信號發送至控制裝置11。 The filter bag 13 removes the dust after the reaction of HCl in the exhaust gas with the fine powder of sodium hydrogencarbonate. The HCl concentration measuring device 14 measures the HCl concentration of the fine powder sodium hydrogencarbonate accumulated on the filter bag 13 (the fine powder of sodium hydrogencarbonate remaining on the filter bag 13 by the reaction with HCl in the exhaust gas) is reacted with the HCl after the reaction with the exhaust gas. (The filter bag outlet HCl concentration to be described later), and the HCl concentration measurement signal is sent to the control device 11.

酸性氣體處理系統1反覆此種循環而進行反饋控制,而控制裝置11進行使微粉碳酸氫鈉添加量的控制輸出值成為恰當值的控制。 The acid gas treatment system 1 performs feedback control in response to such a cycle, and the control device 11 performs control for setting the control output value of the amount of the fine powder sodium bicarbonate added to an appropriate value.

另外,HCl濃度測定設備14是例如離子電極式HCl濃度測定裝置。 Further, the HCl concentration measuring device 14 is, for example, an ion electrode type HCl concentration measuring device.

另外,如圖1所示,較佳為以測定在過濾袋13上蓄積的微粉碳酸氫鈉與廢氣反應後的HCl反應後的HCl濃度(後述的過濾袋出口HCl濃度)的方式,設置HCl濃度測定設備14。其原因是:藉由與廢氣中的HCl的反應而殘存的微粉碳酸氫鈉蓄積在過濾袋13上,該蓄積的微粉碳酸氫鈉與廢氣反應後的HCl反應,因此可更準確地進行HCl濃度的測定。 In addition, as shown in Fig. 1, it is preferable to set the HCl concentration so as to measure the HCl concentration (the concentration of the HCl of the filter bag outlet to be described later) after the reaction of the fine powder of sodium bicarbonate accumulated on the filter bag 13 with the exhaust gas. Measuring device 14. The reason for this is that the fine powder of sodium hydrogencarbonate remaining by the reaction with HCl in the exhaust gas is accumulated on the filter bag 13, and the accumulated fine powder of sodium hydrogencarbonate reacts with the HCl after the reaction of the exhaust gas, so that the HCl concentration can be more accurately performed. Determination.

另外,控制裝置11是將算出的基礎添加量作為微粉碳酸氫鈉的添加量輸出值的下限值(例如後述的LO:添加量下限)而進行反饋控制。 In addition, the control device 11 performs feedback control using the calculated base addition amount as the lower limit value (for example, LO: the lower limit of the addition amount) which is the output value of the addition amount of the fine powder sodium hydrogencarbonate.

因此,將本基礎添加量作為基礎,而藉由先前的反饋運算調整添加量的過量與不足,因此可使鹼劑的添加適當化,並有效地處理酸性氣體。 Therefore, based on the base addition amount, the excess and the insufficient amount of the addition amount are adjusted by the previous feedback calculation, so that the addition of the alkali agent can be appropriately performed, and the acid gas can be efficiently treated.

另外,平均添加量的平均時間並無特別限制,較為有效的是應用添加量的移動平均等的平均值,且較佳為在平均時間為5分鐘以上、15小時~24小時左右下應用。另外,由基礎添加量規定的係數較佳為1倍以下。在使用1倍以上的係數時,雖然可實現酸性氣體的穩定處理,但會妨礙入口酸性氣體濃度的減少所伴隨的添加量的減少,因此會成為過量添加。基礎添加量只要是平均添加量的1倍以下(係數100%以下)即可,特佳為0.5倍~0.95倍(50%~95%)、特別是0.7倍~0.9倍(70%~90%)。 Further, the average time of the average addition amount is not particularly limited, and is preferably an average value of the moving average of the applied amount, and is preferably applied at an average time of 5 minutes or more and 15 hours to 24 hours. Further, the coefficient defined by the amount of base addition is preferably 1 time or less. When the coefficient of one time or more is used, although the stabilization treatment of the acid gas can be achieved, the decrease in the amount of addition accompanying the decrease in the concentration of the inlet acid gas is hindered, and thus the addition is excessive. The base addition amount may be 1 time or less (a coefficient of 100% or less) of the average addition amount, and particularly preferably 0.5 times to 0.95 times (50% to 95%), particularly 0.7 times to 0.9 times (70% to 90%). ).

接著,控制裝置11設置HCl濃度的斜率(濃度的時間變化率)為正的範圍與負的範圍的2個範圍。並且,對 這些2個範圍的每個範圍設定HCl濃度的控制目標值。 Next, the control device 11 sets the slope of the HCl concentration (time change rate of the concentration) to two ranges of the positive range and the negative range. And, right Each of these two ranges sets a control target value of the HCl concentration.

此處,HCl濃度的控制目標值的設定能夠以如下方式進行設定:相對於HCl濃度的斜率為正的範圍而設定的控制目標值小於相對於負的範圍的控制目標值。藉由此種方式進行設定,與HCl濃度下降時相比可增加HCl濃度上升時的微粉碳酸氫鈉添加量。另外,反之與HCl濃度上升時相比,可減少HCl濃度下降時的微粉碳酸氫鈉添加量。因此,可提前實施藉由反饋運算而得的微粉碳酸氫鈉的添加輸出,並可進一步減輕因計測延遲引起的影響。 Here, the setting of the control target value of the HCl concentration can be set such that the control target value set with respect to the positive slope of the HCl concentration is smaller than the control target value with respect to the negative range. By setting in this manner, the amount of the fine powder sodium bicarbonate added when the HCl concentration is increased can be increased as compared with the case where the HCl concentration is lowered. On the other hand, the amount of the sodium fine sodium hydrogen carbonate added when the HCl concentration is lowered can be reduced as compared with the case where the HCl concentration is increased. Therefore, the addition output of the fine powder sodium hydrogencarbonate obtained by the feedback calculation can be performed in advance, and the influence due to the measurement delay can be further alleviated.

接著,控制裝置11可進行藉由步進方式的反饋控制。此處,步進方式是階段性設定與HCl濃度相對應的控制輸出的控制方式。具體而言,除了在PID控制方式中設定的控制輸出值的上限值外,對應HCl濃度而設定控制輸出值的新的上限值。 Next, the control device 11 can perform feedback control by a stepwise method. Here, the stepping method is a control method of setting the control output corresponding to the HCl concentration in stages. Specifically, in addition to the upper limit value of the control output value set in the PID control method, a new upper limit value of the control output value is set in accordance with the HCl concentration.

此處,通常的PID控制中的輸出上限僅有1個,若酸性氣體成為控制目標值以上,則不論酸性氣體濃度的大小,均可添加鹼劑至上限值,並引起過量添加。因此,藉由採用步進控制(step control)方式,而在添加量輸出值的下限值與上限值之間,添加與當前的HCl濃度相對應的新的控制輸出上限值,藉此可根據HCl濃度的大小而適當添加微粉碳酸氫鈉,可抑制添加量的過量添加。 Here, the upper limit of the output in the normal PID control is only one. When the acid gas is equal to or higher than the control target value, the alkali agent can be added to the upper limit regardless of the acid gas concentration, and excessive addition can be caused. Therefore, by using a step control method, a new control output upper limit value corresponding to the current HCl concentration is added between the lower limit value and the upper limit value of the added amount output value, thereby The fine powder of sodium hydrogencarbonate can be appropriately added depending on the concentration of the HCl, and excessive addition of the added amount can be suppressed.

接著,對應HCl濃度而設定新的控制輸出上限值(例如後述的表2、表3、表5的LM1[輸出限制1]、LM2[輸出限制2]),HCl濃度越高則新的控制輸出上限值亦設定為越 高。但是,為了抑制鹼劑的過量添加,較佳為設定為小於在PID控制方式中設定的控制輸出值的上限值(例如後述的表2、表3、表5的LH[控制輸出上限])的值。 Next, a new control output upper limit value (for example, LM1 [output limit 1] and LM2 [output limit 2] in Table 2, Table 3, and Table 5 to be described later) is set in accordance with the HCl concentration, and the new control is performed as the HCl concentration is higher. The upper limit of the output is also set to high. However, in order to suppress excessive addition of the alkaline agent, it is preferably set to be smaller than the upper limit value of the control output value set in the PID control method (for example, LH [Control Output Upper Limit] of Table 2, Table 3, and Table 5 to be described later). Value.

本實施形態中所用的酸性氣體的測定裝置可與計測方式無關地實施。氯化氫濃度可藉由離子電極法、利用雷射的單一吸收線吸收分光法等而測定,硫氧化物可藉由紅外線吸收法、紫外線螢光法等而測定。另外,本實施形態中,藉由應用在先前的反饋控制中無法考慮的妥當的基礎添加量而可獲得改善效果,因此可與計測延遲速度無關地獲得本發明的效果。 The acid gas measuring device used in the present embodiment can be implemented regardless of the measurement method. The concentration of hydrogen chloride can be measured by an ion electrode method, a single absorption line absorption spectrometry using a laser, or the like, and the sulfur oxide can be measured by an infrared absorption method, an ultraviolet ray method, or the like. Further, in the present embodiment, since the improvement effect can be obtained by applying a proper base addition amount which cannot be considered in the previous feedback control, the effect of the present invention can be obtained regardless of the measurement delay speed.

在工業廢棄物焚燒爐或民間工廠的燃燒設備中,多數情況下氯化氫與硫氧化物以高濃度產生。此時,氯化氫與硫氧化物這兩者成為處理對象,藉由例如將根據設置於過濾袋後段的氯化氫濃度測定裝置的氯化氫濃度而在上述控制方式中求出的控制輸出、與根據硫氧化物濃度而在上述控制方式中求出的控制輸出相加,而可穩定處理氯化氫及硫氧化物這兩種酸性氣體。 In the combustion equipment of industrial waste incinerators or private factories, in most cases, hydrogen chloride and sulfur oxides are produced at a high concentration. In this case, both of the hydrogen chloride and the sulfur oxide are treated, and the control output obtained in the above-described control method based on the hydrogen chloride concentration of the hydrogen chloride concentration measuring device provided in the subsequent stage of the filter bag, and the sulfur oxide-based The concentration and the control outputs obtained in the above control method are added, and the acid gases such as hydrogen chloride and sulfur oxide can be stably treated.

接著,具有以各酸性氣體濃度(氯化氫、硫氧化物濃度)的1小時平均值來管理酸性氣體的排出濃度管理的設備。通常為設置控制目標值(SV)進行控制,但控制目標值只不過是目標,往往有成為超過控制的結果目標值的濃度的情況。特別是添加量削減與酸性氣體的穩定處理是相反的概念,因此越要求添加量削減,則1小時平均值超過管理值的風險越大。此時,在到達1小時平均管理值以上、 或接近1小時平均管理值的濃度時,藉由添加大量的鹼劑(規定某固定添加量),而可實現添加量削減與酸性氣體的穩定處理可並存的安心度高的控制。 Next, there is an apparatus for managing the discharge concentration management of the acid gas with a one hour average value of each acid gas concentration (hydrogen chloride, sulfur oxide concentration). Usually, the control target value (SV) is set to be controlled, but the control target value is only a target, and there is often a case where the concentration exceeds the target value of the control result. In particular, the reduction in the amount of addition is contrary to the concept of stabilization of the acid gas. Therefore, the more the amount of addition is required, the greater the risk that the average value of one hour exceeds the management value. At this time, when it reaches the average management value of 1 hour, When the concentration of the average management value is close to one hour, a large amount of an alkali agent (predetermined amount of a fixed amount) is added, so that the control of the increase in the amount of addition and the stabilization of the acid gas can be achieved.

本實施形態中所用的鹼劑並無特別限制。特別是與酸性氣體的反應快的平均粒徑被調整為5μm~30μm的微粉碳酸氫鈉,控制響應性佳,並可有效地發揮本控制方法的性能。另外,氫氧化鈣即便是JIS特號氫氧化鈣亦可,但使用與酸性氣體的反應性高的比表面積為例如30m2/g以上的高比表面積的氫氧化鈣,則可發揮本發明的性能。上述以外的鹼劑可例示:碳酸鈉、碳酸氫鉀、碳酸鉀、倍半碳酸鈉、天然蘇打、氫氧化鈉、氫氧化鉀、氧化鎂、氫氧化鎂等。 The alkali agent used in the embodiment is not particularly limited. In particular, the average particle diameter of the reaction with the acid gas is adjusted to a fine powder of sodium bicarbonate of 5 μm to 30 μm, and the control responsiveness is good, and the performance of the present control method can be effectively exerted. In addition, although calcium hydroxide may be JIS-specific calcium hydroxide, it is possible to exhibit the high specific surface area of calcium hydroxide having a specific surface area with high reactivity with an acid gas of, for example, 30 m 2 /g or more. performance. The alkali agent other than the above may, for example, be sodium carbonate, potassium hydrogencarbonate, potassium carbonate, sodium sesquicarbonate, natural soda, sodium hydroxide, potassium hydroxide, magnesium oxide or magnesium hydroxide.

另外,在鹼劑為粉體時,較佳為與酸性氣體的反應性高的粒徑小於30μm、特別是5μm~20μm的微粉。可應用預先調整了粒徑的劑材,亦可在現場設置粉碎設備,一邊在現場粉碎粒徑粗的鹼劑一邊添加。另外,亦可藉由將各鹼劑溶解於水而成的漿料或水溶液進行實施。 Further, when the alkali agent is a powder, it is preferably a fine powder having a particle diameter of at least 30 μm, particularly 5 μm to 20 μm, which is highly reactive with an acid gas. It is possible to apply a pre-adjusted particle size, or to provide a pulverizing device on site, and to pulverize an alkali agent having a coarse particle size on site. Further, it may be carried out by a slurry or an aqueous solution obtained by dissolving each alkali agent in water.

接著,併用與實施本實施形態的控制的鹼劑不同的、廉價的鹼劑,亦為於經濟上有效的方法。所併用的鹼劑並無限制,通常使用的廉價的鹼劑可例示:氫氧化鈣、氫氧化鈉、氫氧化鎂、氧化鎂、碳酸鈉、倍半碳酸鈉、天然蘇打、粗碳酸氫鈉。 Next, it is also an economically effective method to use an inexpensive alkali agent different from the alkaline agent to be controlled by the present embodiment. The alkali agent to be used in combination is not limited, and an inexpensive alkali agent which is usually used may, for example, be calcium hydroxide, sodium hydroxide, magnesium hydroxide, magnesium oxide, sodium carbonate, sodium sesquicarbonate, natural soda or crude sodium hydrogencarbonate.

[實例] [Example]

對模擬反應系統進行說明。 The simulated reaction system will be described.

[模擬反應系統]:廢氣與過濾袋上的複合反應 [Simulated Reaction System]: Composite reaction on exhaust gas and filter bag

模擬反應系統包括:微粉碳酸氫鈉與氯化氫(HCL)的反應在廢氣中瞬間引起的反應、及在過濾袋上蓄積的未反應微粉碳酸氫鈉與HCL的反應這二個反應(參照圖2)。另外,過濾袋中的捕獲物的滯留時間通常為2小時左右。因此,本模擬中,設為過濾袋上的微粉碳酸氫鈉在規定時間(設定在約2小時)消失的形態。 The simulated reaction system includes the reaction of the reaction of the powdered sodium bicarbonate with hydrogen chloride (HCL) in the exhaust gas, and the reaction of the unreacted fine powder of sodium bicarbonate and HCL accumulated on the filter bag (refer to FIG. 2). . In addition, the residence time of the capture material in the filter bag is usually about 2 hours. Therefore, in the present simulation, it is assumed that the fine powder of sodium hydrogencarbonate on the filter bag disappears for a predetermined period of time (set at about 2 hours).

參照圖2,說明模擬反應系統的基本構成。 The basic configuration of the simulated reaction system will be described with reference to Fig. 2 .

首先,在焚燒設備中的藥劑注入控制中,根據設置於過濾袋出口的離子電極式HCl濃度測定設備的HCl濃度(處理後)信號,藉由PID等控制式的運算決定藥劑添加量(微粉碳酸氫鈉添加量(Ag))(下述式(1)),將已決定的添加量的微粉碳酸氫鈉(酸性氣體處理劑)添加至廢氣(入口HCl濃度(Hi))中。添加至煙道中的微粉碳酸氫鈉與廢氣中的HCl等酸性氣體反應,而將廢氣中的HCl除去。 First, in the drug injection control in the incineration apparatus, the amount of the chemical addition is determined by a control calculation such as PID based on the HCl concentration (after treatment) signal of the ion electrode type HCl concentration measuring device provided at the outlet of the filter bag. The amount of sodium hydrogen added (Ag) (the following formula (1)) is added to the exhaust gas (inlet HCl concentration (Hi)) by the determined addition amount of the fine powder sodium hydrogencarbonate (acid gas treatment agent). The fine powder of sodium hydrogencarbonate added to the flue reacts with an acid gas such as HCl in the exhaust gas, and the HCl in the exhaust gas is removed.

Ag=Ag1+LO (1) Ag=Ag1+LO (1)

Ag:微粉碳酸氫鈉添加量[kg/h] Ag: Micronized sodium bicarbonate added [kg/h]

Ag1:由HCl濃度測定設備的輸出規定的添加量[kg/h](步進方式的情況下,參照表2、表3、表5) Ag1: The amount of addition specified by the output of the HCl concentration measuring device [kg/h] (refer to Table 2, Table 3, and Table 5 in the case of the step method)

LO:添加量下限[kg/h] LO: lower limit of addition [kg/h]

通常時(不應用本發明的基礎添加量時),使用預先設 定的LO。 Normally (when the base addition amount of the present invention is not applied), the pre-set is used. The fixed LO.

在應用本發明的基礎添加量時,將LO作為使指定時間的移動平均添加量乘以特定係數而得的基礎添加量,並運算輸出。 When the base addition amount of the present invention is applied, the LO is used as a base addition amount obtained by multiplying the moving average addition amount of the specified time by a specific coefficient, and the output is calculated.

另外,藉由微粉碳酸氫鈉的入口HCl濃度的HCl除去率,是根據本公司微粉碳酸氫鈉的應用知識,根據廢氣反應微粉碳酸氫鈉添加當量(Jg)與廢氣反應HCl除去率(αg)的關係(圖3)、及根據過濾袋上反應微粉碳酸氫鈉添加當量(Js)與過濾袋上反應HCl除去率(αs)的關係(圖4)進行估算。另外,HCl與微粉碳酸氫鈉的反應是瞬間完成。首先,廢氣中的反應後的HCl濃度(Hg)是由廢氣反應的微粉碳酸氫鈉添加當量(Jg)與廢氣反應HCl除去率(αg)導出(下述式(2))。另外,廢氣反應的微粉碳酸氫鈉添加當量(Jg)是根據下述式(3)算出。 In addition, the HCl removal rate by the inlet HCl concentration of the sodium microbicarbonate is based on the application knowledge of the company's micronized sodium bicarbonate, and the HCl removal rate (αg) is determined according to the exhaust gas reaction fine powder sodium bicarbonate addition equivalent (Jg) and the exhaust gas. The relationship (Fig. 3) and the relationship between the reaction equivalent of sodium bicarbonate addition equivalent (Js) on the filter bag and the reaction HCl removal rate (αs) on the filter bag (Fig. 4) were used. In addition, the reaction of HCl with micronized sodium bicarbonate is instantaneous. First, the HCl concentration (Hg) after the reaction in the exhaust gas is derived from the fine powder sodium hydrogencarbonate addition equivalent (Jg) of the exhaust gas reaction and the exhaust gas reaction HCl removal rate (αg) (the following formula (2)). In addition, the fine powder sodium hydrogencarbonate addition equivalent (Jg) of the exhaust gas reaction is calculated according to the following formula (3).

Hg=Hi×(1-αg÷100) (2) Hg=Hi×(1-αg÷100) (2)

Hi:入口HCl濃度(ppm) Hi: inlet HCl concentration (ppm)

Hg:廢氣反應後HCl濃度(ppm) Hg: HCl concentration after exhaust gas reaction (ppm)

αg:廢氣反應中的HCl除去率(%) Gg: HCl removal rate in exhaust gas reaction (%)

[根據廢氣反應微粉碳酸氫鈉添加當量與HCl除去率的關係(圖3)進行設定] [Set according to the relationship between the addition amount of the sodium carbonate sodium hydrogencarbonate and the HCl removal rate (Fig. 3)]

Jg=Ag÷{Hi÷0.614÷1000÷M1×M2×F÷1000} (3) Jg=Ag÷{Hi÷0.614÷1000÷M1×M2×F÷1000} (3)

Jg:廢氣反應微粉碳酸氫鈉添加當量 Jg: exhaust gas reaction fine powder sodium bicarbonate addition equivalent

Ag:微粉碳酸氫鈉添加量(kg/h) Ag: Micronized sodium bicarbonate added (kg/h)

Hi:入口HCl濃度(ppm) Hi: inlet HCl concentration (ppm)

M1:HCl分子量[設定為36.5] M1: HCl molecular weight [set to 36.5]

M2:碳酸氫鈉分子量[設定為84] M2: molecular weight of sodium bicarbonate [set to 84]

F:廢氣量(Nm3/h)[設定為55,000Nm3/h] F: amount of exhaust gas (Nm 3 /h) [set to 55,000 Nm 3 /h]

另外,藉由廢氣反應而殘存的微粉碳酸氫鈉會隨時蓄積在過濾袋上。在BF上蓄積的微粉碳酸氫鈉與廢氣反應後的HCl反應,而決定過濾袋出口的HCl濃度(Ho)。此時,BF上蓄積微粉碳酸氫鈉量(As)是由廢氣反應中蓄積的微粉碳酸氫鈉減去在BF上與HCl反應的微粉碳酸氫鈉量。另外,根據由本過濾袋上蓄積微粉碳酸氫鈉量(As)與廢氣反應後的HCl濃度(Hg)估算的過濾袋上微粉碳酸氫鈉添加當量(Js)(下述式(5)),決定過濾袋上的HCl除去率(αs),並決定過濾袋出口的HCl濃度(Ho)(下述式(4))。 Further, the fine powder of sodium hydrogencarbonate remaining by the exhaust gas reaction accumulates on the filter bag at any time. The fine powder of sodium hydrogencarbonate accumulated on the BF reacts with the HCl reacted with the exhaust gas to determine the HCl concentration (Ho) at the outlet of the filter bag. At this time, the amount of sodium bicarbonate (As) accumulated on the BF is the amount of the fine powder of sodium bicarbonate which is reacted with HCl on the BF by the fine powder of sodium hydrogencarbonate accumulated in the exhaust gas reaction. Further, it is determined based on the addition amount (Js) of the fine powder sodium bicarbonate (Js) (hereinafter referred to as the following formula (5)) estimated on the filter bag by the amount of the sodium hydrogen carbonate (As) accumulated on the filter bag and the HCl concentration (Hg) after the reaction with the exhaust gas. The HCl removal rate (αs) on the filter bag determines the HCl concentration (Ho) at the outlet of the filter bag (the following formula (4)).

Ho=Hg×(1-αs÷100) (4) Ho=Hg×(1-αs÷100) (4)

Hg:廢氣反應後HCl濃度(ppm) Hg: HCl concentration after exhaust gas reaction (ppm)

Ho:過濾袋出口HCl濃度(ppm) Ho: filter bag outlet HCl concentration (ppm)

αs:過濾袋上反應的HCl除去率(%) Ss: HCl removal rate (%) of the reaction on the filter bag

[根據過濾袋上微粉碳酸氫鈉添加當量與HCl除去率 的關係(圖4)進行設定] [According to the addition of equivalent amount of sodium bicarbonate on the filter bag and the removal rate of HCl Relationship (Figure 4) is set]

Js=As÷{Hg÷0.614÷1000÷M1×M2×F÷1000} (5) Js=As÷{Hg÷0.614÷1000÷M1×M2×F÷1000} (5)

Js:過濾袋上微粉碳酸氫鈉添加當量 Js: Adding equivalent of sodium microbicarbonate on the filter bag

As:過濾袋上微粉碳酸氫鈉量(kg/h) As: The amount of micro-powder sodium bicarbonate on the filter bag (kg/h)

Hg:廢氣反應後HCl濃度(ppm) Hg: HCl concentration after exhaust gas reaction (ppm)

M1:HCl分子量[設定為36.5] M1: HCl molecular weight [set to 36.5]

M2:碳酸氫鈉分子量[設定為84] M2: molecular weight of sodium bicarbonate [set to 84]

F:廢氣量(Nm3/h)[設定為55,000Nm3/h] F: amount of exhaust gas (Nm 3 /h) [set to 55,000 Nm 3 /h]

As=Zn÷Ts×3600 (6) As=Z n ÷Ts×3600 (6)

Zn:過濾袋上微粉碳酸氫鈉蓄積量(kg) Z n : the amount of micro-powder sodium bicarbonate accumulated on the filter bag (kg)

Ts:單位模擬時間(=資料取樣時間)(sec) Ts: unit simulation time (= data sampling time) (sec)

[設定為0.5sec] [Set to 0.5sec]

Zn=Zn'×(1-2.3÷T4×Ts) (7) Z n =Z n' ×(1-2.3÷T4×Ts) (7)

Zn':未反應微粉碳酸氫鈉量(kg) Z n' : amount of unreacted micropowder sodium bicarbonate (kg)

T4:過濾袋上蓄積微粉碳酸氫鈉90%消失時間常數(sec) T4: Accumulated micronized sodium bicarbonate 90% disappearance time constant (sec) on the filter bag

[設定為7,200sec] [Set to 7,200sec]

Ts:單位模擬時間(=資料取樣時間)(sec) Ts: unit simulation time (= data sampling time) (sec)

[設定為0.5sec] [Set to 0.5sec]

Zn'=(Ag÷3600×Ts-Rg)+(Zn-1-Rs) (8) Z n' =(Ag÷3600×Ts-Rg)+(Z n-1 -Rs) (8)

Ag:微粉碳酸氫鈉添加量(kg/h) Ag: Micronized sodium bicarbonate added (kg/h)

Ts:單位模擬時間(=資料取樣時間)(sec) Ts: unit simulation time (= data sampling time) (sec)

[設定為0.5sec] [Set to 0.5sec]

Rg:廢氣反應中的碳酸氫鈉反應量(kg/h) Rg: sodium bicarbonate reaction amount in exhaust gas reaction (kg/h)

Zn-1:Ts(Sec)前的過濾袋上微粉碳酸氫鈉蓄積量(kg) Z n-1 : The amount of powdered sodium bicarbonate in the filter bag before Ts (Sec) (kg)

Rs:過濾袋上反應中的碳酸氫鈉反應量(kg/h) Rs: sodium bicarbonate reaction amount in the reaction on the filter bag (kg/h)

Rg=(Hi÷0.614÷1000÷M1×M2×F÷1000)÷3600×Ts×αg÷100 (9) Rg=(Hi÷0.614÷1000÷M1×M2×F÷1000)÷3600×Ts×αg÷100 (9)

Hi:入口HCl濃度(ppm) Hi: inlet HCl concentration (ppm)

M1:HCl分子量[設定為36.5] M1: HCl molecular weight [set to 36.5]

M2:碳酸氫鈉分子量[設定為84] M2: molecular weight of sodium bicarbonate [set to 84]

F:廢氣量(Nm3/h)[設定為55,000Nm3/h] F: amount of exhaust gas (Nm 3 /h) [set to 55,000 Nm 3 /h]

αg:廢氣反應中的HCl除去率(%) Gg: HCl removal rate in exhaust gas reaction (%)

Rs=(Hg÷0.614÷1000÷M1×M2×F÷1000)÷3600×Ts×αs÷100 (10) Rs=(Hg÷0.614÷1000÷M1×M2×F÷1000)÷3600×Ts×αs÷100 (10)

Hg:廢氣反應後HCl濃度(ppm) Hg: HCl concentration after exhaust gas reaction (ppm)

M1:HCl分子量[設定為36.5] M1: HCl molecular weight [set to 36.5]

M2:碳酸氫鈉分子量[設定為84] M2: molecular weight of sodium bicarbonate [set to 84]

F:廢氣量(Nm3/h)[設定為55,000Nm3/h] F: amount of exhaust gas (Nm 3 /h) [set to 55,000 Nm 3 /h]

αs:過濾袋上反應的HCl除去率(%) Ss: HCl removal rate (%) of the reaction on the filter bag

本反應後的過濾袋出口的HCl濃度藉由離子電極式HCl濃度測定設備14進行測定。然而,在離子電極式HCl濃度測定設備14中,存在因設備引起的延遲時間(T1)、因廢氣取樣引起的計測延遲時間(T2α)、及因離子電極式測定引起的計測延遲時間(T2β,響應時間),而產生反饋特有的控制延遲。 The HCl concentration at the outlet of the filter bag after the reaction was measured by an ion electrode type HCl concentration measuring device 14. However, in the ion electrode type HCl concentration measuring device 14, there are a delay time (T1) due to the device, a measurement delay time (T2α) due to exhaust gas sampling, and a measurement delay time (T2β due to ion electrode type measurement). Response time), which produces a feedback-specific control delay.

因此,本模擬的HCl濃度測定設備14的延遲時間(T)設為因設備引起的延遲時間(T1)與HCl濃度測定設備14的計測延遲時間(T2)的合計(下述式(11))。另外,HCl濃度測定設備14的計測延遲時間(T2)設定自煙道將HCl處理後的廢氣取樣的計測延遲時間(T2α)與離子電極式HCl濃度測定設備(T2β)的計測延遲時間(響應時間),並設為這些計測延遲時間的和(下述式(12))。通常使用的離子電極式的90%響應時間(計測延遲)受到HCl氣體朝吸收液中的擴散的影響,因此設為T2β(下述式(13))。本模擬中,計測延遲時間較長的離子電極式根據實機設備的狀況,而設為T1=30秒、T2α=390秒(取樣延遲210秒+溴廢氣通過延遲180秒)、T2β=180秒的計600秒(10分鐘:T1=0.5分鐘、T2=9.5分鐘)。 Therefore, the delay time (T) of the HCl concentration measuring device 14 of the present simulation is the sum of the delay time (T1) caused by the device and the measurement delay time (T2) of the HCl concentration measuring device 14 (the following formula (11)) . Further, the measurement delay time (T2) of the HCl concentration measuring device 14 sets the measurement delay time (T2α) of the exhaust gas sample after the HCl treatment from the flue and the measurement delay time (response time) of the ion electrode type HCl concentration measuring device (T2β). ), and set the sum of these measurement delay times (the following formula (12)). The 90% response time (measurement delay) of the ion electrode type which is generally used is affected by the diffusion of HCl gas into the absorption liquid, and is therefore set to T2β (the following formula (13)). In this simulation, the ion electrode type with a long delay time is set to T1=30 seconds, T2α=390 seconds (sampling delay 210 seconds + bromine exhaust passage delay 180 seconds), T2β=180 seconds according to the condition of the actual equipment. 600 seconds (10 minutes: T1 = 0.5 minutes, T2 = 9.5 minutes).

另外,在使用計測延遲時間較離子電極式短的HCl濃度測定設備時,改變計測延遲時間並確認行為。 Further, when the HCl concentration measuring apparatus having a shorter measurement delay time than the ion electrode type is used, the measurement delay time is changed and the behavior is confirmed.

[HCl濃度測定設備(低速響應、模擬離子電極式)] [HCl concentration measuring device (low speed response, analog ion electrode type)]

T=T1+T2 (11) T=T1+T2 (11)

T:HCl濃度測定設備的模擬反應系統的延遲時間(sec) T: Delay time (sec) of the simulated reaction system of the HCl concentration measuring device

T1:設備的延遲時間(sec)[設定為30sec] T1: Delay time (sec) of the device [set to 30sec]

T2:HCl濃度測定設備的計測延遲時間(sec) T2: Measurement delay time (sec) of the HCl concentration measuring device

T2=T2α+T2β (12) T2=T2α+T2β (12)

T2α:HCl濃度測定設備的廢氣取樣時間(sec) T2α: Exhaust gas sampling time (sec) of HCl concentration measuring equipment

[設定為390sec] [Set to 390sec]

T2β:HCl濃度測定設備的90%響應時間(sec)[設定為180sec] T2β: 90% response time (sec) of the HCl concentration measuring device [set to 180 sec]

T2β=2.3×τ (13) T2β=2.3×τ (13)

Yn=Yn-1+(Xn-Yn-1)÷τ×Ts (14) Y n =Y n-1 +(X n -Y n-1 )÷τ×Ts (14)

τ:時間常數(sec) τ: time constant (sec)

Ts:單位模擬時間(=資料取樣時間)(sec) Ts: unit simulation time (= data sampling time) (sec)

[設定為0.5sec] [Set to 0.5sec]

Xn:當前的測定裝置輸入HCl濃度(ppm) Xn: current assay device input HCl concentration (ppm)

Yn:當前的測定裝置輸出HCl濃度(ppm) Yn: current measuring device output HCl concentration (ppm)

Yn-1:前次(Ts(sec)前)的測定裝置輸出HCl濃度(ppm) Y n-1 : The output of the previous device (before Ts (sec)) HCl concentration (ppm)

另外,處理酸性氣體的鹼劑的添加量是根據藉由反饋而求出的添加輸出進行規定(上述式(1)),該反饋是根據藉由HCl計測設備測定的濃度進行估算而得。本發明的基礎添加量是將移動平均添加量×係數(1倍以下)作為反饋控制的下限進行運算。 Further, the amount of the alkaline agent to be treated for the acid gas is defined based on the added output obtained by the feedback (the above formula (1)), and the feedback is obtained by estimating the concentration measured by the HCl measuring device. The basis addition amount of the present invention is calculated by using the moving average addition amount × coefficient (1 time or less) as the lower limit of the feedback control.

另外,使用如圖5所示般變動的入口HCl濃度,根據實機中的PID的添加行為及HCl產生狀況(圖6)及本模擬反應系統的結果(圖7),設定廢氣反應與BF上反應的HCl的反應效率。將本研究結果示於圖6及圖7。本設備中,廢氣的HCl除去效率為80%、BF上反應的除去效率為65%,實機與模擬的行為一致(圖6、圖7)。因此,在本條件下進行以下模擬。另外,在本模擬中,為了使利用控制方法的控制響應性明確,而使用變動相對較大的時間帶的入口HCl濃度(Hi)進行實施。 In addition, using the inlet HCl concentration as shown in Fig. 5, the exhaust gas reaction and the BF are set according to the PID addition behavior and the HCl generation condition (Fig. 6) and the results of the simulation reaction system (Fig. 7) in the actual machine. The reaction efficiency of the reacted HCl. The results of this study are shown in Figures 6 and 7. In this apparatus, the HCl removal efficiency of the exhaust gas is 80%, and the removal efficiency of the reaction on the BF is 65%, and the actual machine is in accordance with the simulated behavior (Fig. 6, Fig. 7). Therefore, the following simulation was performed under the conditions. Further, in the present simulation, in order to clarify the control responsiveness by the control method, the inlet HCl concentration (Hi) of the time zone having a relatively large fluctuation is used.

以下,列舉實例對本發明進行更具體地說明,但本發明並不限定於此。 Hereinafter, the present invention will be specifically described by way of examples, but the present invention is not limited thereto.

以下的實例中的研究是根據實機研究結果製作模擬反應系統,研究利用各控制方法的控制結果。另外,由於具有基礎添加量中的平均添加量的平均時間較長的條件(3小時、6小時),因此反覆使用入口HCl濃度,藉由經過6小時~9小時之時的結果進行評價。 The study in the following examples is based on the results of actual machine research to make a simulated reaction system, and to study the control results using each control method. In addition, since the average time of the average addition amount in the base addition amount was long (3 hours, 6 hours), the inlet HCl concentration was repeatedly used, and the evaluation was performed by the result of 6 hours to 9 hours.

[比較例1] [Comparative Example 1]

使用圖8所示的入口HCl濃度,根據在上述模擬中藉由HCl測定設備(測定設備計測延遲時間計9.5分鐘)計測的HCl濃度,在PID控制方式「P(比例增益)=100%、I=0.1秒、D=0.1秒、添加量輸出下限200kg/h、添加量輸出上限480kg/h」中,將出口HCl濃度的控制目標值(SV)設定為200ppm而進行反饋控制。 Using the inlet HCl concentration shown in Fig. 8, the PID control method "P (proportional gain) = 100%, I is based on the HCl concentration measured by the HCl measuring device (measuring device measurement delay time 9.5 minutes) in the above simulation. In the case of =0.1 sec, D = 0.1 sec, the lower limit of the amount of output, 200 kg/h, and the upper limit of the amount of addition, 480 kg/h, the control target value (SV) of the outlet HCl concentration was set to 200 ppm, and feedback control was performed.

將微粉碳酸氫鈉添加量與藉由微粉碳酸氫鈉處理後的過濾袋出口HCl濃度(平均、1小時平均最大、瞬間最大、1小時平均最少、瞬間最少)示於表1。 The HCl concentration (average, 1 hour average maximum, instantaneous maximum, 1 hour average minimum, minimum moment) of the micropowder sodium bicarbonate addition amount and the filter bag outlet after treatment with the fine powder sodium hydrogencarbonate are shown in Table 1.

另外,將本控制時的微粉碳酸氫鈉添加量與過濾袋出口HCl濃度的行為示於圖9。 Further, the behavior of the amount of the fine powder of sodium hydrogencarbonate added in the present control and the concentration of the HCl at the outlet of the filter bag is shown in Fig. 9 .

可較佳地用作酸性氣體的排出管理值的出口HCl濃度的1小時平均值的最大值為212ppm、瞬間最大為384ppm。 The maximum value of the 1-hour average value of the outlet HCl concentration which can be preferably used as the discharge management value of the acid gas is 212 ppm, and the maximum value is 384 ppm in an instant.

[實例1] [Example 1]

30分鐘移動平均添加量(kg/h)乘以80%的係數而作為基礎添加量,並用作添加量輸出下限,除此以外,在比較例1所示的相同設定條件下運算並進行反饋控制。 The 30-minute moving average addition amount (kg/h) was multiplied by a coefficient of 80% as a base addition amount, and used as a lower limit of the addition amount output, and the calculation was performed under the same setting conditions as in Comparative Example 1 and feedback control was performed. .

將微粉碳酸氫鈉添加量與藉由微粉碳酸氫鈉處理後的過濾袋出口HCl濃度示於表1。另外,將本控制時的微粉碳酸氫鈉添加量與過濾袋出口HCl濃度的行為示於圖10。 The HCl concentration of the fine powder sodium bicarbonate added to the filter bag outlet after treatment with the fine powder of sodium hydrogencarbonate is shown in Table 1. Further, the behavior of the amount of the fine powder of sodium hydrogencarbonate added during the control and the concentration of the HCl at the outlet of the filter bag is shown in Fig. 10 .

根據實例1,1小時平均值的HCl的最大值為189ppm、瞬間最大為309ppm,與比較例1相比,酸性氣體處理性能提高,並且添加量亦自330kg/h削減至315kg/h。 According to Example 1, the maximum value of HCl of 1 hour average was 189 ppm, and the maximum value was 309 ppm in an instant. Compared with Comparative Example 1, the acid gas treatment performance was improved, and the addition amount was also reduced from 330 kg/h to 315 kg/h.

此處,對步進控制方式的概要進行說明。比較例2、比較例3及比較例6、實例2、實例3、實例9~實例11、實例17、實例18、實例20~實例24中,利用步進控制方式代替PID控制方式進行控制。 Here, an outline of the step control method will be described. In Comparative Example 2, Comparative Example 3 and Comparative Example 6, Example 2, Example 3, Example 9 to Example 11, Example 17, Example 18, and Example 20 to Example 24, the step control method was used instead of the PID control method for control.

步進方式與PID控制方式不同,設定為根據出口的HCl濃度階段性規定輸出的控制方式。若藉由比較例2、實例2、實例20(表2)進行說明,則在HCl濃度為SV控制目標值[控制輸出開始濃度(輸出下限以上)]~SM1間時,在LO與LM1間階段性地輸出控制輸出。在HCl濃度為SM1~SM2間時,輸出以LM2設定的控制輸出,在SM2以上時,則設為輸出LH(控制輸出上限)的形式。另外,通常的PID控制式中並無輸出限制,僅設定LO與LH。另外,藉由HCl斜率的控制運算中所使用的HCl濃度與決定控制輸出的表的修正是藉由SVA1與SVA2來進行,在HCl斜率為正時,自運算中使用的HCl濃度減去SVA1,在HCl斜率為負時,將運算中使用的HCl濃度加上SVA2。藉此,在輸入相同的HCl濃度時所運算的控制輸出設為如下形式:在HCl斜率的值較大時(酸性氣體濃度增加傾向)的控制輸出值與HCl斜率的值較小時的控制輸出值相比而增大。 The stepping method is different from the PID control method, and is set to a control method that outputs the output according to the HCl concentration of the outlet. According to Comparative Example 2, Example 2, and Example 20 (Table 2), when the HCl concentration is between the SV control target value [control output start concentration (output lower limit or higher)]~SM1, between LO and LM1. Output output control. When the HCl concentration is between SM1 and SM2, the control output set by LM2 is output. When it is above SM2, the output LH (control output upper limit) is used. In addition, there is no output limitation in the normal PID control formula, and only LO and LH are set. In addition, the HCl concentration used in the control calculation of the HCl slope and the correction of the table for determining the control output are performed by SVA1 and SVA2, and when the HCl slope is positive, the HCl concentration used in the calculation is subtracted from SVA1. When the HCl slope is negative, the concentration of HCl used in the calculation is added to SVA2. Thereby, the control output calculated when the same HCl concentration is input is set to a control output when the value of the HCl slope is large (the acid gas concentration tends to increase) and the control output value and the HCl slope value are small. The value increases compared to the value.

另外,微粉碳酸氫鈉添加量(Ag)藉由上述式(1)求出。 Further, the amount of fine sodium hydrogencarbonate added (Ag) was determined by the above formula (1).

[比較例2] [Comparative Example 2]

在上述模擬中根據藉由HCl測定設備(測定設備計測 延遲時間9.5分鐘)計測的HCl濃度,在步進方式的控制中將控制目標值(本方式中鹼劑的控制輸出是將添加至輸出下限以上的濃度規定為SV)設定為200ppm而進行反饋控制(參照表2)。 In the above simulation, according to the HCl measuring device (measurement device measurement) The HCl concentration measured by the delay time of 9.5 minutes is controlled by the control target value (in the present embodiment, the control output of the alkaline agent is set to SV at a concentration equal to or higher than the lower limit of the output), and feedback control is performed. (Refer to Table 2).

將微粉碳酸氫鈉添加量與藉由微粉碳酸氫鈉處理後的過濾袋出口HCl濃度示於表1。另外,將本控制時的微粉碳酸氫鈉添加量與過濾袋出口HCl濃度的行為示於圖11。 The HCl concentration of the fine powder sodium bicarbonate added to the filter bag outlet after treatment with the fine powder of sodium hydrogencarbonate is shown in Table 1. Further, the behavior of the amount of the fine powder of sodium hydrogencarbonate added in the present control and the concentration of the HCl at the outlet of the filter bag is shown in Fig. 11 .

步進方式的出口HCl濃度的1小時平均值的最大值為212ppm、瞬間最大為383ppm。 The maximum value of the 1-hour average value of the outlet HCl concentration in the stepwise mode was 212 ppm, and the maximum instantaneous value was 383 ppm.

[實例2] [Example 2]

30分鐘移動平均添加量(kg/h)乘以80%的係數而作為基礎添加量,並用作添加量輸出下限,除此以外,在比較例2所示的步進方式的相同設定條件下運算並進行反饋控制。 The 30-minute moving average addition amount (kg/h) was multiplied by a coefficient of 80% as a base addition amount, and used as a lower limit of the addition amount output, and the calculation was performed under the same setting conditions of the stepping method shown in Comparative Example 2. And feedback control.

將微粉碳酸氫鈉添加量與藉由微粉碳酸氫鈉處理後的過濾袋出口HCl濃度示於表1。另外,將本控制時的微粉碳酸氫鈉添加量與過濾袋出口HCl濃度的行為示於圖12。 The HCl concentration of the fine powder sodium bicarbonate added to the filter bag outlet after treatment with the fine powder of sodium hydrogencarbonate is shown in Table 1. Further, the behavior of the amount of the fine powder of sodium hydrogencarbonate added in the present control and the concentration of the HCl at the outlet of the filter bag is shown in Fig. 12 .

根據實例2,步進方式中出口HCl濃度的1小時平均值的最大值為195ppm、瞬間最大為320ppm,與比較例2相比,酸性氣體處理性能提高,並且添加量亦自295kg/h削減至289kg/h。 According to Example 2, the maximum value of the 1-hour average value of the outlet HCl concentration in the stepwise mode was 195 ppm, and the instantaneous maximum was 320 ppm. Compared with Comparative Example 2, the acid gas treatment performance was improved, and the addition amount was also reduced from 295 kg/h to 289kg/h.

[比較例3] [Comparative Example 3]

在上述模擬中根據藉由HCl測定設備(測定設備計測延遲時間9.5分鐘)計測的HCl濃度,在步進方式的控制 中在最接近的HCl濃度的斜率的6秒平均為正時,將控制目標值(SV)設為180ppm(SV-20ppm),在最接近的HCl濃度的斜率的6秒平均為負時,將控制目標值(SV)設為220ppm(SV+20ppm),而進行反饋控制(參照表3)。 In the above simulation, the HCl concentration measured by the HCl measuring device (measurement device measurement delay time 9.5 minutes) is controlled in the step mode. When the average of 6 seconds of the slope of the closest HCl concentration is positive, the control target value (SV) is set to 180 ppm (SV-20 ppm), and when the average of the slope of the closest HCl concentration is negative for 6 seconds, The control target value (SV) was set to 220 ppm (SV + 20 ppm), and feedback control was performed (refer to Table 3).

將微粉碳酸氫鈉添加量與藉由微粉碳酸氫鈉處理後的過濾袋出口HCl濃度示於表1。另外,將本控制時的微粉碳酸氫鈉添加量與過濾袋出口HCl濃度的行為示於圖13。 The HCl concentration of the fine powder sodium bicarbonate added to the filter bag outlet after treatment with the fine powder of sodium hydrogencarbonate is shown in Table 1. Further, the behavior of the amount of the fine powder of sodium hydrogencarbonate added in the present control and the concentration of the HCl at the outlet of the filter bag is shown in Fig. 13 .

除了本步進方式外,根據HCl濃度的斜率對控制目標值進行變更(以下稱為SV變更),藉由變更所得的本反饋控制的出口HCl濃度的1小時平均值的最大值為216ppm、瞬間最大為381ppm。 In addition to the current stepping method, the control target value is changed according to the slope of the HCl concentration (hereinafter referred to as SV change), and the maximum value of the 1-hour average value of the outlet HCl concentration controlled by the feedback control is 216 ppm. The maximum is 381ppm.

[實例3] [Example 3]

30分鐘移動平均添加量(kg/h)乘以80%的係數而作為基礎添加量,並用作添加量輸出下限,除此以外,在比較例3所示的反饋形式的相同設定條件下運算並進行反饋控制。 The 30-minute moving average addition amount (kg/h) was multiplied by a coefficient of 80% as a base addition amount, and used as a lower limit of the addition amount output, and was calculated under the same setting conditions of the feedback form shown in Comparative Example 3, and Perform feedback control.

將微粉碳酸氫鈉添加量與藉由微粉碳酸氫鈉處理後的過濾袋出口HCl濃度示於表1。另外,將本控制時的微粉碳酸氫鈉添加量與過濾袋出口HCl濃度的行為示於圖14。 The HCl concentration of the fine powder sodium bicarbonate added to the filter bag outlet after treatment with the fine powder of sodium hydrogencarbonate is shown in Table 1. Further, the behavior of the amount of the fine powder of sodium hydrogencarbonate added in the present control and the concentration of the HCl at the outlet of the filter bag is shown in Fig. 14 .

根據實例3,在上述反饋方式中,出口HCl濃度的1小時平均值的最大值為198ppm、瞬間最大為283ppm,與比較例3相比,酸性氣體處理性能提高,並且添加量亦自301kg/h削減至289kg/h。 According to Example 3, in the above feedback mode, the maximum value of the 1-hour average value of the outlet HCl concentration was 198 ppm, and the maximum instantaneous value was 283 ppm. Compared with Comparative Example 3, the acid gas treatment performance was improved, and the addition amount was also from 301 kg/h. Reduced to 289kg / h.

[實例4~實例8] [Example 4 to Example 8]

將改變了平均時間的移動平均添加量(kg/h)[實例4:5分鐘、實例5:15分鐘、實例6:1小時、實例7:3小時、實例8:6小時]乘以80%的係數,而作為基礎添加量,並用作添加量輸出下限,除此以外,在比較例1所示的相同設定條件下運算並進行反饋控制。 The moving average addition amount (kg/h) of the average time will be changed [Example 4: 5 minutes, Example 5: 15 minutes, Example 6: 1 hour, Example 7: 3 hours, Example 8: 6 hours] Multiplied by 80% The coefficient is used as the base addition amount and used as the addition amount output lower limit. Otherwise, the feedback control is performed under the same setting conditions as in Comparative Example 1.

將微粉碳酸氫鈉添加量與藉由微粉碳酸氫鈉處理後的過濾袋出口HCl濃度示於表1。另外,將本控制時的微粉碳酸氫鈉添加量與過濾袋出口HCl濃度的行為示於圖15~圖19。 The HCl concentration of the fine powder sodium bicarbonate added to the filter bag outlet after treatment with the fine powder of sodium hydrogencarbonate is shown in Table 1. Further, the behavior of the amount of the fine powder of sodium hydrogencarbonate added in the present control and the concentration of the HCl at the outlet of the filter bag are shown in Figs. 15 to 19 .

根據實例4~實例8,使將平均添加量乘以1倍以下的係數而得的基礎添加量用作反饋控制的因素,並運算鹼劑的添加量,藉此可實現酸性氣體的穩定處理。 According to the examples 4 to 8, the base addition amount obtained by multiplying the average addition amount by a factor of 1 or less is used as a factor of feedback control, and the addition amount of the alkali agent is calculated, whereby the acid gas stabilization treatment can be realized.

實例4~實例8的效果是藉由在反饋中應用平均添加量的因素而獲得,平均時間並無特別限制。在添加量平均時間5分鐘(實例4)中,藉由同等的添加量,出口HCl濃度1小時平均值最大為186ppm、瞬間最大為369ppm,可獲得酸性氣體的穩定處理效果。而且,在添加量平均時間6小時(實例8)中,出口HCl濃度的1小時平均值最大為194ppm、瞬間最大為308ppm,可獲得穩定處理效果,並且添加量亦削減為311kg/h。添加量的平均時間較佳為5分鐘以上,特佳為15分鐘~6小時。 The effects of Examples 4 to 8 were obtained by applying the factor of the average addition amount in the feedback, and the average time is not particularly limited. In the average addition time of 5 minutes (Example 4), the equivalent amount of the outlet HCl concentration was 186 ppm at a maximum value of 1 hour, and the maximum instantaneous value was 369 ppm, whereby a stable treatment effect of the acid gas was obtained. Further, in the average addition time of 6 hours (Example 8), the 1-hour average value of the outlet HCl concentration was 194 ppm at the maximum and 308 ppm at the maximum, and a stable treatment effect was obtained, and the addition amount was also reduced to 311 kg/h. The average time of the added amount is preferably 5 minutes or more, and particularly preferably 15 minutes to 6 hours.

[實例9~實例11] [Example 9 to Example 11]

將改變了平均時間的移動平均添加量(kg/h)[實例9:15分鐘、實例10:1小時、實例11:3小時]乘以80%的 係數,而作為基礎添加量,並用作添加量輸出下限,除此以外,在比較例3所示的相同設定條件下運算並進行反饋控制。 The moving average addition amount (kg/h) of the average time is changed [Example 9: 15 minutes, Example 10: 1 hour, Example 11: 3 hours] multiplied by 80% The coefficient was used as the base addition amount and used as the addition amount output lower limit. Otherwise, the feedback control was performed under the same setting conditions as shown in Comparative Example 3.

將微粉碳酸氫鈉添加量與藉由微粉碳酸氫鈉處理後的過濾袋出口HCl濃度示於表1。另外,將本控制時的微粉碳酸氫鈉添加量與過濾袋出口HCl濃度的行為示於圖20~圖22。 The HCl concentration of the fine powder sodium bicarbonate added to the filter bag outlet after treatment with the fine powder of sodium hydrogencarbonate is shown in Table 1. Further, the behavior of the amount of the fine powder of sodium hydrogencarbonate added in the present control and the concentration of the HCl at the outlet of the filter bag are shown in Figs. 20 to 22 .

根據利用步進+SV變更方式的反饋控制中的添加量平均時間在15分鐘~3小時中變化時的實例9~實例11,不論添加量平均時間如何,均可獲得酸性氣體穩定處理效果與添加量削減效果。本方式是特別在添加量為288kg/h~292kg/h時添加量削減效果優異的控制方式。 According to Example 9 to Example 11 when the average amount of addition time in the feedback control using the step + SV change mode is changed from 15 minutes to 3 hours, the acid gas stabilization treatment effect and addition can be obtained regardless of the average time of the addition amount. The amount of reduction effect. This embodiment is a control method which is excellent in the effect of reducing the amount of addition when the amount of addition is 288 kg/h to 292 kg/h.

[實例12~實例16] [Example 12 to Example 16]

改變1小時移動平均添加量(kg/h)所乘以的係數[實例12:95%、實例13:90%、實例14:80%、實例15:70%、實例16:50%]而作為基礎添加量,並用作添加量輸出下限,除此以外,在比較例1所示的相同設定條件下運算並進行反饋控制。 The coefficient multiplied by the 1-hour moving average addition amount (kg/h) was changed [Example 12: 95%, Example 13: 90%, Example 14: 80%, Example 15: 70%, Example 16: 50%] as The base addition amount was used as the lower limit of the addition amount output, and the feedback control was performed under the same setting conditions as shown in Comparative Example 1.

將微粉碳酸氫鈉添加量與藉由微粉碳酸氫鈉處理後的過濾袋出口HCl濃度示於表1。另外,將本控制時的微粉碳酸氫鈉添加量與過濾袋出口HCl濃度的行為示於圖23~圖27。 The HCl concentration of the fine powder sodium bicarbonate added to the filter bag outlet after treatment with the fine powder of sodium hydrogencarbonate is shown in Table 1. Further, the behavior of the amount of the fine powder of sodium hydrogencarbonate added in the present control and the concentration of the HCl at the outlet of the filter bag are shown in Figs. 23 to 27 .

實例12~實例16的效果是藉由在反饋中應用平均添加量的因素而獲得,運算基礎添加量時,平均添加量所乘 以的係數為1倍以下即可,並無特別限制。本係數乘以1倍(100%)以上的係數時,即便入口HCl濃度減少,本基礎添加量所用的平均添加量亦不減少而引起過量添加。 The effects of the example 12 to the example 16 are obtained by applying the factor of the average addition amount in the feedback, and when the basis addition amount is calculated, the average addition amount is multiplied. The coefficient is 1 or less, and is not particularly limited. When the coefficient is multiplied by a factor of 1 time (100%) or more, even if the inlet HCl concentration is decreased, the average addition amount used for the base addition amount is not reduced and excessive addition is caused.

運算本基礎添加量的係數為95%(實例12)~70%(實例15)時,出口HCl濃度的1小時平均值最大及瞬間最大值與比較例1相比均降低,可獲得酸性氣體的穩定處理效果,並且可獲得添加量削減效果。另外,係數為50%(實例16)時,雖然添加量稍有增加,但可獲得酸性氣體穩定處理效果。運算基礎添加量時平均添加量所乘以的係數只要為1倍以下即可。較佳為50%~95%、特佳為70%~90%。 When the coefficient of the base addition amount is 95% (Example 12) to 70% (Example 15), the maximum 1-hour average value of the outlet HCl concentration and the instantaneous maximum value are lower than those of Comparative Example 1, and acid gas can be obtained. The effect of the treatment is stabilized, and the effect of reducing the amount of addition can be obtained. Further, when the coefficient was 50% (Example 16), although the amount of addition was slightly increased, the acid gas stabilizing treatment effect was obtained. The coefficient multiplied by the average addition amount when calculating the basic addition amount may be 1 time or less. It is preferably 50% to 95%, and particularly preferably 70% to 90%.

[實例17、實例18] [Example 17, Example 18]

改變1小時移動平均添加量(kg/h)所乘以的係數[實例17:90%、實例18:70%]而作為基礎添加量,並用作添加量輸出下限,除此以外,在比較例3所示的相同設定條件下運算並進行反饋控制。 The coefficient multiplied by the one-hour moving average addition amount (kg/h) was changed [Example 17: 90%, Example 18: 70%] as the base addition amount, and used as the addition amount output lower limit, in addition, in the comparative example Operate and perform feedback control under the same setting conditions as shown in 3.

將微粉碳酸氫鈉添加量與藉由微粉碳酸氫鈉處理後的過濾袋出口HCl濃度示於表1。另外,將本控制時的微粉碳酸氫鈉添加量與過濾袋出口HCl濃度的行為示於圖28、圖29。 The HCl concentration of the fine powder sodium bicarbonate added to the filter bag outlet after treatment with the fine powder of sodium hydrogencarbonate is shown in Table 1. Further, the behavior of the amount of the fine powder of sodium hydrogencarbonate added in the present control and the concentration of the HCl at the outlet of the filter bag are shown in Figs. 28 and 29 .

根據藉由步進+SV變更方式的反饋控制中運算基礎添加量時所乘以的係數在70%~90%內變化時的實例17、實例18,不論運算基礎添加量的係數如何,均可獲得酸性氣體穩定處理效果與添加量削減效果。另外,本方式是特別在添加量為289kg/h~297kg/h時添加量削減效果優異的 控制方式。 According to the example 17 and the example 18 when the coefficient multiplied by the operation base addition amount in the feedback control by the step + SV change mode is changed within 70% to 90%, regardless of the coefficient of the calculation base addition amount, The acid gas stabilization treatment effect and the addition amount reduction effect are obtained. In addition, this embodiment is excellent in the effect of reducing the amount of addition particularly when the amount of addition is 289 kg/h to 297 kg/h. way to control.

[比較例4] [Comparative Example 4]

根據上述模擬中藉由HCl測定設備(測定設備計測延遲時間計2秒)計測的HCl濃度,在PID控制方式「P(比例增益)=100%、I=0.1秒、D=0.1秒、添加量輸出下限200kg/h、添加量輸出上限480kg/h」中,將出口HCl濃度的控制目標值(SV)設定為200ppm並進行反饋控制。 According to the HCl concentration measured by the HCl measuring device (measurement device measurement delay time 2 seconds) in the above simulation, the PID control method "P (proportional gain) = 100%, I = 0.1 second, D = 0.1 second, the amount of addition) In the output lower limit of 200 kg/h and the addition amount output upper limit of 480 kg/h, the control target value (SV) of the outlet HCl concentration was set to 200 ppm and feedback control was performed.

將微粉碳酸氫鈉添加量與藉由微粉碳酸氫鈉處理後的過濾袋出口HCl濃度示於表1。另外,將本控制時的微粉碳酸氫鈉添加量與過濾袋出口HCl濃度的行為示於圖30。 The HCl concentration of the fine powder sodium bicarbonate added to the filter bag outlet after treatment with the fine powder of sodium hydrogencarbonate is shown in Table 1. Further, the behavior of the amount of the fine powder of sodium hydrogencarbonate added in the present control and the concentration of the HCl at the outlet of the filter bag is shown in Fig. 30.

對測定設備的計測延遲時間所造成的影響進行了研究。預測到,在使用計測延遲較少的高速響應的HCl測定設備進行反饋控制時,會瞬間引起鹼劑的添加量變化與出口HCl濃度的變化並進行改善。然而,預測到會引起因鹼劑添加變動所導致的添加不良,可較佳用作酸性氣體的排出管理值的出口HCl濃度的1小時平均值的最大值為209ppm、瞬間最大為385ppm。 The effect of the measurement delay time of the measuring device was investigated. It is predicted that when feedback control is performed using an HCl measuring apparatus that measures a high-speed response with less delay, the change in the amount of addition of the alkali agent and the change in the concentration of the outlet HCl are instantaneously caused and improved. However, it is predicted that the addition failure due to the change in the addition of the alkali agent is preferable, and the maximum value of the 1-hour average value of the outlet HCl concentration which is preferably used as the discharge management value of the acid gas is 209 ppm, and the maximum instantaneous value is 385 ppm.

[實例19] [Example 19]

根據上述模擬中藉由HCl測定設備(測定設備計測延遲時間計2秒)計測的HCl濃度,進行PID控制運算,除此以外,在與實例1相同條件下進行反饋控制。 The feedback control was performed under the same conditions as in Example 1 except that the PID control calculation was performed by the HCl concentration measured by the HCl measuring device (measurement device measurement delay time: 2 seconds) in the above simulation.

將微粉碳酸氫鈉添加量與藉由微粉碳酸氫鈉處理後的過濾袋出口HCl濃度示於表1。另外,將本控制時的微粉碳酸氫鈉添加量與過濾袋出口HCl濃度的行為示於圖31。 The HCl concentration of the fine powder sodium bicarbonate added to the filter bag outlet after treatment with the fine powder of sodium hydrogencarbonate is shown in Table 1. Further, the behavior of the amount of the fine powder of sodium hydrogencarbonate added in the present control and the concentration of the HCl at the outlet of the filter bag is shown in Fig. 31.

[實例20] [Example 20]

根據在上述模擬中藉由HCl測定設備(測定設備計測延遲時間計2秒)計測的HCl濃度,進行藉由步進方式的運算,除此以外,在與實例2相同條件下進行反饋控制。 The feedback control was performed under the same conditions as in Example 2 except that the HCl concentration measured by the HCl measuring device (measurement device measurement delay time of 2 seconds) was calculated by the stepwise method in the above simulation.

將微粉碳酸氫鈉添加量與藉由微粉碳酸氫鈉處理後的過濾袋出口HCl濃度示於表1。另外,將本控制時的微粉碳酸氫鈉添加量與過濾袋出口HCl濃度的行為示於圖32。 The HCl concentration of the fine powder sodium bicarbonate added to the filter bag outlet after treatment with the fine powder of sodium hydrogencarbonate is shown in Table 1. Further, the behavior of the amount of the fine powder of sodium hydrogencarbonate added in the present control and the concentration of the HCl at the outlet of the filter bag is shown in Fig. 32.

[實例21] [Example 21]

根據在上述模擬中藉由HCl測定設備(測定設備計測延遲時間計2秒)計測的HCl濃度,進行藉由步進+SV變更方式的運算,除此以外,在與實例3相同條件下進行反饋控制。 The feedback was performed under the same conditions as in Example 3, except that the HCl concentration measured by the HCl measuring device (measurement device measurement delay time: 2 seconds) was calculated by the step + SV change method in the above simulation. control.

將微粉碳酸氫鈉添加量與藉由微粉碳酸氫鈉處理後的過濾袋出口HCl濃度示於表1。另外,將本控制時的微粉碳酸氫鈉添加量與過濾袋出口HCl濃度的行為示於圖33。 The HCl concentration of the fine powder sodium bicarbonate added to the filter bag outlet after treatment with the fine powder of sodium hydrogencarbonate is shown in Table 1. Further, the behavior of the amount of the fine powder of sodium hydrogencarbonate added in the present control and the concentration of the HCl at the outlet of the filter bag is shown in Fig. 33.

根據實例21,不論計測設備的計測延遲時間的長短,均會發揮出效果。並且控制形式若為反饋形式,則均會發揮出效果。實例19~實例21是假定計測延遲時間2秒的結果,抑制因反饋所引起的鹼劑的添加不良,並且均可獲得酸性氣體的穩定處理效果及添加量削減效果。 According to the example 21, the effect is exerted regardless of the length of the measurement delay time of the measuring device. And if the control form is in the form of feedback, it will exert its effect. Examples 19 to 21 are results of assuming a measurement delay time of 2 seconds, suppressing the addition of an alkali agent due to feedback, and obtaining an effect of stabilizing the acid gas and an effect of reducing the amount of addition.

[實例22] [Example 22]

在上述模擬中出口HCl濃度的1小時平均值超過190ppm時,實施480kg/h的鹼劑的添加,除此以外,在與實例10相同條件(延遲時間9.5分鐘、步進+SV變更)下進 行反饋控制。將微粉碳酸氫鈉添加量與藉由微粉碳酸氫鈉處理後的過濾袋出口HCl濃度示於表1。另外,將本控制時的微粉碳酸氫鈉添加量與過濾袋出口HCl濃度的行為示於圖34。 In the above simulation, when the average value of the outlet HCl concentration exceeded 190 ppm, the addition of the 480 kg/h alkali agent was carried out, and the same conditions as in Example 10 (delay time 9.5 minutes, step + SV change) were carried out. Line feedback control. The HCl concentration of the fine powder sodium bicarbonate added to the filter bag outlet after treatment with the fine powder of sodium hydrogencarbonate is shown in Table 1. Further, the behavior of the amount of the fine powder of sodium hydrogencarbonate added in the present control and the concentration of the HCl at the outlet of the filter bag is shown in Fig. 34.

酸性氣體的排出濃度管理具有藉由各酸性氣體濃度(氯化氫、硫氧化物濃度)的1小時平均值進行管理的設備。控制中通常設置控制目標值(SV)進行控制,但控制目標值只不過是目標,有成為超過所控制的結果目標值的濃度的情況。 The discharge concentration management of the acid gas has a device that is managed by a one-hour average value of each acid gas concentration (hydrogen chloride, sulfur oxide concentration). In the control, the control target value (SV) is usually set for control, but the control target value is only the target, and there is a case where the concentration exceeds the target value of the controlled result.

本實例是在出口HCl濃度的1小時平均值超過200ppm的實例10中,實施1小時平均管理(190ppm以上是進行480kg/h添加)的例子。在出口的1小時平均值接近應管理的濃度時,藉由實施添加大量鹼劑的控制,而可實現酸性氣體的更穩定處理效果與有效的鹼劑的利用。 In the present example, in the example 10 in which the 1-hour average value of the outlet HCl concentration exceeded 200 ppm, an example of one-hour average management (190 ppm or more was performed at 480 kg/h) was carried out. When the 1-hour average value of the outlet is close to the concentration to be managed, the more stable treatment effect of the acid gas and the utilization of the effective alkali agent can be achieved by performing the control of adding a large amount of the alkali agent.

以下,對作為實機研究結果的比較例5、比較例6、實例23、實例24進行說明時,對比較例5、比較例6、實例23、實例24中所用的酸性氣體處理系統2的構成進行說明。 Hereinafter, when Comparative Example 5, Comparative Example 6, Example 23, and Example 24, which are the results of the actual machine research, the composition of the acid gas treatment system 2 used in Comparative Example 5, Comparative Example 6, Example 23, and Example 24 will be described. Be explained.

圖35是表示焚燒設備中在作為廢氣的HCl中添加微粉碳酸氫鈉的酸性氣體處理系統2的構成的方塊圖。 Fig. 35 is a block diagram showing the configuration of an acid gas treatment system 2 in which fine powder sodium hydrogencarbonate is added to HCl as an exhaust gas in an incineration facility.

酸性氣體處理系統2包括:控制裝置21、微粉碳酸氫鈉添加裝置22、微粉碳酸氫鈉添加裝置26、過濾袋23、HCl濃度測定設備(離子電極方式)24。控制裝置21根據由HCl濃度測定設備(離子電極方式)24發送的HCl濃度測定信號、及由過去的平均添加量算出的基礎添加量, 藉由反饋控制(PID控制方式或步進方式)算出微粉碳酸氫鈉的添加量輸出值。微粉碳酸氫鈉添加裝置22根據控制裝置21算出的微粉碳酸氫鈉的添加量輸出值在廢氣中的HCl中添加微粉碳酸氫鈉。另外,微粉碳酸氫鈉添加裝置26是在廢氣中的HCl中,添加與控制裝置21所算出的微粉碳酸氫鈉的添加量輸出值無關的固定量的微粉碳酸氫鈉。 The acid gas treatment system 2 includes a control device 21, a fine powder sodium hydrogencarbonate addition device 22, a fine powder sodium hydrogencarbonate addition device 26, a filter bag 23, and an HCl concentration measuring device (ion electrode method) 24. The control device 21 is based on the HCl concentration measurement signal transmitted by the HCl concentration measuring device (ion electrode method) 24 and the basic addition amount calculated from the past average addition amount. The output value of the addition amount of the fine powder sodium hydrogencarbonate is calculated by feedback control (PID control method or step method). The fine powder sodium hydrogencarbonate addition device 22 adds the fine powder sodium hydrogencarbonate to the HCl in the exhaust gas based on the output amount of the fine powder sodium hydrogencarbonate added by the control device 21. Further, the fine powder sodium hydrogencarbonate addition device 26 is a fixed amount of fine powder sodium hydrogencarbonate which is added to the HCl in the exhaust gas irrespective of the output value of the added amount of the fine powder sodium hydrogencarbonate calculated by the controller 21.

另外,基礎添加量是與平均時間(例如移動平均時間)相對應的過去的平均添加量乘以1倍以下的係數而算出。 Further, the base addition amount is calculated by multiplying the average addition amount of the past corresponding to the average time (for example, the moving average time) by a factor of 1 or less.

過濾袋23是將廢氣中的HCl與微粉碳酸氫鈉反應後的粉塵除去。HCl濃度測定設備(離子電極方式)24是測定在過濾袋23上蓄積的微粉碳酸氫鈉(藉由與廢氣中的HCl的反應而殘存的微粉碳酸氫鈉蓄積在過濾袋23上)與廢氣反應後的HCl反應後的HCl濃度(後述的過濾袋出口HCl濃度),並將HCl濃度測定信號發送至控制裝置21。 The filter bag 23 removes dust obtained by reacting HCl in the exhaust gas with fine powder of sodium hydrogencarbonate. The HCl concentration measuring device (ion electrode method) 24 measures the reaction of the fine powder sodium hydrogencarbonate (the fine powder of sodium hydrogencarbonate remaining on the filter bag 23 by the reaction with HCl in the exhaust gas) accumulated on the filter bag 23 with the exhaust gas. The concentration of HCl after the subsequent HCl reaction (concentration of the HCl of the filter bag to be described later) is sent to the control device 21 by the HCl concentration measurement signal.

另外,過濾袋的入口HCl濃度是藉由未圖示的HCl濃度測定設備(雷射方式)進行測定。 Further, the inlet HCl concentration of the filter bag was measured by an HCl concentration measuring device (laser method) not shown.

酸性氣體處理系統2反覆此種循環而進行反饋控制,而控制裝置21進行使微粉碳酸氫鈉添加量的控制輸出值為恰當值的控制。 The acid gas treatment system 2 performs feedback control in response to such a cycle, and the control device 21 performs control for setting the control output value of the fine powder sodium bicarbonate addition amount to an appropriate value.

[比較例5] [Comparative Example 5]

在工業廢棄物焚燒爐中,在減溫塔出口~過濾袋間設置雷射形式的HCl測定設備(京都電子工業製造的KLA-1),測定入口HCl濃度。另外,根據藉由過濾袋出 口的離子電極方式的HCl測定設備(京都電子工業製造的HL-36N)測定的信號,藉由管理排出基準值的氧氣換算值實施反饋控制。另外,將根據出口的SOx濃度信號的反饋添加輸出(SV180ppm)加上根據HCl濃度的添加輸出,而加以實施,但本設備中,由於未產生SOx,因此自本報告刪去。 In an industrial waste incinerator, a HCl measuring device (KLA-1 manufactured by Kyoto Electronics Industry Co., Ltd.) in the form of a laser was placed between the outlet of the desuperheating tower and the filter bag, and the inlet HCl concentration was measured. In addition, according to the filter bag The signal measured by the ion-electrode-type HCl measuring device (HL-36N manufactured by Kyoto Electronics Industry Co., Ltd.) is subjected to feedback control by managing the oxygen-converted value of the discharge reference value. In addition, the feedback addition output (SV180 ppm) based on the SOx concentration signal of the outlet is added to the addition output according to the HCl concentration, but in this apparatus, since SOx is not generated, it is deleted from this report.

另外,處理酸性氣體的鹼劑藉由上述反饋控制添加8μm微粉碳酸氫鈉(栗田工業製造的Hyperther B-200)。鹼劑的添加裝置是由於最大添加量的問題而應用2台,1台設定為180kg/h定量添加,另1台根據上述出口HCl濃度信號藉由「下限20kg/h、上限300kg/h、PID控制設定P(比例增益)=100%、I=0.1秒、D=0.1秒」進行反饋控制。 Further, the alkaline agent for treating the acid gas was added with 8 μm of fine powder sodium hydrogencarbonate (Hyperther B-200 manufactured by Kurita Industries) by the above feedback control. The alkaline agent addition device is applied by two units due to the problem of the maximum amount of addition, one set is set to 180 kg/h quantitatively, and the other one is based on the above-mentioned outlet HCl concentration signal by "lower limit 20 kg/h, upper limit 300 kg/h, PID" The feedback control is performed by controlling the setting P (proportional gain) = 100%, I = 0.1 second, D = 0.1 second.

將過濾袋入口HCl濃度及過濾袋出口HCl濃度與微粉碳酸氫鈉的添加量(2台添加裝置合併計算)示於表4。另外,將本控制實施時的微粉碳酸氫鈉添加量與過濾袋入口出口的HCl濃度的行為示於圖36。 The HCl concentration at the inlet of the filter bag and the HCl concentration at the outlet of the filter bag and the addition amount of the sodium hydrogencarbonate (calculated by two addition devices) are shown in Table 4. Further, the behavior of the amount of the fine powder of sodium hydrogencarbonate added at the time of the present control and the concentration of HCl at the inlet and outlet of the filter bag are shown in Fig. 36.

[比較例6] [Comparative Example 6]

在同一設備中,利用藉由過濾袋出口的離子電極方式的HCl測定設備(京都電子工業製造的HL-36N)測定的HCl濃度信號(氧氣換算值)實施反饋控制。另外,同樣,將根據出口的SOx濃度信號的反饋添加輸出(SV180ppm)加上根據HCl濃度的添加輸出而加以實施。 In the same apparatus, feedback control was performed using an HCl concentration signal (oxygen conversion value) measured by an ion electrode type HCl measuring device (HL-36N manufactured by Kyoto Electronics Industry Co., Ltd.). Further, similarly, the feedback addition output (SV180 ppm) based on the SOx concentration signal of the outlet was added in addition to the addition output according to the HCl concentration.

另外,添加裝置是同樣1台設定為180kg/h定量添加,另1台設定為「步進+SV變更方式(詳細參照表5)」。 In addition, the same device is set to 180 kg/h for the same amount, and the other device is set to "Step + SV change method (see Table 5 for details)".

將過濾袋入口HCl濃度及過濾袋出口HCl濃度與微粉碳酸氫鈉的添加量(2台添加裝置合併計算)示於表4。另外,將本控制實施時的微粉碳酸氫鈉添加量與過濾袋入口出口的HCl濃度的行為示於圖37。 The HCl concentration at the inlet of the filter bag and the HCl concentration at the outlet of the filter bag and the addition amount of the sodium hydrogencarbonate (calculated by two addition devices) are shown in Table 4. Further, the behavior of the amount of the fine powder of sodium hydrogencarbonate added at the time of the present control and the concentration of HCl at the inlet and outlet of the filter bag is shown in Fig. 37 .

[實例23] [Example 23]

在同一設備中,在「步進+SV變更方式」的反饋控制中,應用基礎添加量[30分鐘移動平均添加量、係數70%],出口HCl濃度1小時平均值為213ppm以上[本設備HCl管理值為215ppm以下]並進行300kg/h添加,除此以外,藉由與比較例6相同的設定實施反饋控制。另外,同樣,將根據出口的SOx濃度信號的反饋添加輸出(SV180ppm)加上根據HCl濃度的添加輸出而加以實施。 In the same device, in the feedback control of "Step + SV change mode", the base addition amount [30 minutes moving average addition amount, coefficient 70%] is applied, and the outlet HCl concentration is 1 hour average value is 213 ppm or more [this device HCl The feedback control was carried out by the same setting as in Comparative Example 6, except that the management value was 215 ppm or less] and 300 kg/h was added. Further, similarly, the feedback addition output (SV180 ppm) based on the SOx concentration signal of the outlet was added in addition to the addition output according to the HCl concentration.

另外,添加裝置是同樣1台設定為180kg/h定量添加,另1台設定為「步進+SV變更方式(詳細參照表5)」。 In addition, the same device is set to 180 kg/h for the same amount, and the other device is set to "Step + SV change method (see Table 5 for details)".

將過濾袋入口HCl濃度及過濾袋出口HCl濃度與微粉碳酸氫鈉的添加量(2台添加裝置合併計算)示於表4。另外,將本控制實施時的微粉碳酸氫鈉添加量與過濾袋入口出口的HCl濃度的行為示於圖38。 The HCl concentration at the inlet of the filter bag and the HCl concentration at the outlet of the filter bag and the addition amount of the sodium hydrogencarbonate (calculated by two addition devices) are shown in Table 4. Further, the behavior of the amount of the fine powder of sodium hydrogencarbonate added at the time of the present control and the concentration of HCl at the inlet and outlet of the filter bag is shown in Fig. 38.

本實例是根據本發明的實機的應用結果。與比較例5、比較例6相比,入口HCl濃度的變動更少。根據本實例,藉由本發明的有效的鹼劑的添加,表示鹼劑相對於入口HCl濃度的添加量的添加當量,與比較例5、比較例6相比,可削減並可實現有效的控制。 This example is the result of the application of the real machine according to the present invention. The change in the inlet HCl concentration was smaller than in Comparative Example 5 and Comparative Example 6. According to the present example, the addition of the effective alkali agent of the present invention indicates the addition equivalent of the amount of the alkali agent added to the inlet HCl concentration, and can be reduced and effective control can be achieved as compared with Comparative Example 5 and Comparative Example 6.

[實例24] [Example 24]

在同一設備中,在「步進+SV變更方式」的反饋控制中,併用且應用比表面積為30m2/g以上的高反應氫氧化鈣(奧多摩工業股份有限公司製造的TamakalkECO),除此以外,藉由與實例23相同的設定實施反饋控制。另外,同樣將根據出口的SOx濃度信號的反饋添加輸出(SV180ppm)加上根據HCl濃度的添加輸出,而加以實施。 In the same device, in the feedback control of "Step + SV change method", high-response calcium hydroxide (TamakalkECO manufactured by Odomo Industries Co., Ltd.) having a specific surface area of 30 m 2 /g or more is used in combination, and The feedback control was carried out by the same settings as in Example 23 except for the same. In addition, the feedback addition output (SV180 ppm) based on the SOx concentration signal of the outlet was also added, and the addition output according to the HCl concentration was carried out.

另外,添加裝置1台是將高反應氫氧化鈣設定為170kg/h定量添加,將另1台設定為「步進+SV變更方式(詳細參照表5)」。 In addition, one of the addition devices was set to a high-reaction calcium hydroxide of 170 kg/h, and the other was set to "step + SV change mode (see Table 5 for details).

將過濾袋入口HCl濃度及過濾袋出口HCl濃度與微粉碳酸氫鈉的添加量(2台添加裝置合併計算)示於表4。另外,將本控制實施時的微粉碳酸氫鈉添加量與過濾袋入口出口的HCl濃度的行為示於圖39。 The HCl concentration at the inlet of the filter bag and the HCl concentration at the outlet of the filter bag and the addition amount of the sodium hydrogencarbonate (calculated by two addition devices) are shown in Table 4. Further, the behavior of the amount of the fine powder of sodium hydrogencarbonate added at the time of the present control and the concentration of HCl at the inlet and outlet of the filter bag is shown in Fig. 39.

表1是表示模擬研究結果的比較例及實例的每個例的鹼劑添加量等的表。表2是比較例2、實例2及實例20中步進控制方式的控制設定的表。表3是比較例3、實例3、實例9、實例10、實例11、實例17、實例18、實例21及實例22中步進控制方式的控制設定的表。表4是表示實機研究結果的比較例及實例的每個例的鹼劑添加量等的表。表5是比較例6、實例23及實例24中步進控制方式的控制設定的表。 Table 1 is a table showing the amount of alkali agent added and the like for each of the comparative examples and the examples of the results of the simulation studies. Table 2 is a table of control settings of the step control method in Comparative Example 2, Example 2, and Example 20. Table 3 is a table of control settings of the step control mode in Comparative Example 3, Example 3, Example 9, Example 10, Example 11, Example 17, Example 18, Example 21, and Example 22. Table 4 is a table showing the amount of alkali agent added and the like in each of the comparative examples and the examples of the actual machine research results. Table 5 is a table of control settings of the step control method in Comparative Example 6, Example 23, and Example 24.

表5 table 5

本實例是併用且應用工業上相對較廉價的氫氧化鈣與微粉碳酸氫鈉的事例。本方法中亦可穩定獲得酸性氣體的穩定處理效果。由於應用廉價的氫氧化鈣,並削減酸性氣體處理費用,因此是工業上有效的方法。 This example is an example in which the industrially relatively inexpensive calcium hydroxide and finely divided sodium hydrogencarbonate are used in combination. In the method, the stable treatment effect of the acid gas can also be stably obtained. It is an industrially effective method because it uses inexpensive calcium hydroxide and reduces the cost of acid gas treatment.

1、2‧‧‧酸性氣體處理系統 1, 2‧‧‧ Acid gas treatment system

11、21‧‧‧控制裝置 11, 21‧‧‧ control device

12、22、26‧‧‧微粉碳酸氫鈉添加裝置 12,22,26‧‧‧Micronized sodium bicarbonate addition device

13、23‧‧‧過濾袋 13, 23‧‧‧ filter bags

14、24‧‧‧HCl濃度測定設備 14, 24‧‧‧HCl concentration measuring equipment

圖1是表示焚燒設備中在作為廢氣的HCl中添加微粉碳酸氫鈉的酸性氣體處理系統1的構成的方塊圖。 Fig. 1 is a block diagram showing the configuration of an acid gas treatment system 1 in which a fine powder of sodium hydrogencarbonate is added to HCl as an exhaust gas in an incineration facility.

圖2是模擬反應系統的基本構成圖。 2 is a basic configuration diagram of a simulated reaction system.

圖3是表示廢氣反應中微粉碳酸氫鈉添加當量與HCl除去率的關係的圖表。 Fig. 3 is a graph showing the relationship between the addition amount of fine powder sodium hydrogencarbonate and the HCl removal rate in the exhaust gas reaction.

圖4是表示過濾袋上反應中的微粉碳酸氫鈉添加當量與HCl除去率的關係的圖表。 Fig. 4 is a graph showing the relationship between the addition amount of fine powder sodium hydrogencarbonate and the HCl removal rate in the reaction on the filter bag.

圖5是表示入口HCl濃度的行為的圖表。 Figure 5 is a graph showing the behavior of inlet HCl concentration.

圖6表示實機研究結果的微粉碳酸氫鈉添加量及出口HCl濃度的行為的圖表。 Fig. 6 is a graph showing the behavior of the powdered sodium bicarbonate addition amount and the outlet HCl concentration as a result of actual machine research.

圖7是表示模擬研究結果的微粉碳酸氫鈉添加量及出口HCl濃度的行為的圖表。 Fig. 7 is a graph showing the behavior of the amount of fine powder of sodium hydrogencarbonate added and the concentration of HCl at the outlet of the simulation study.

圖8是表示入口HCl濃度的行為的圖表。 Figure 8 is a graph showing the behavior of the inlet HCl concentration.

圖9是表示比較例1中微粉碳酸氫鈉添加量及出口HCl濃度的行為的圖表。 Fig. 9 is a graph showing the behavior of the amount of fine powder of sodium hydrogencarbonate added and the concentration of HCl at the outlet in Comparative Example 1.

圖10是表示實例1中微粉碳酸氫鈉添加量及出口HCl濃度的行為的圖表。 Fig. 10 is a graph showing the behavior of the amount of fine powder of sodium hydrogencarbonate added and the concentration of HCl at the outlet in Example 1.

圖11是表示比較例2中微粉碳酸氫鈉添加量及出口HCl濃度的行為的圖表。 Fig. 11 is a graph showing the behavior of the amount of fine powder of sodium hydrogencarbonate added and the concentration of HCl at the outlet in Comparative Example 2.

圖12是表示實例2中微粉碳酸氫鈉添加量及出口HCl濃度的行為的圖表。 Fig. 12 is a graph showing the behavior of the amount of fine powder of sodium hydrogencarbonate added and the concentration of HCl at the outlet in Example 2.

圖13是表示比較例3中微粉碳酸氫鈉添加量、入口HCl濃度及出口HCl濃度的行為的圖表。 Fig. 13 is a graph showing the behavior of the amount of fine powder of sodium hydrogencarbonate added, the concentration of the inlet HCl, and the concentration of the outlet HCl in Comparative Example 3.

圖14是表示實例3中微粉碳酸氫鈉添加量及出口HCl濃度的行為的圖表。 Figure 14 is a graph showing the behavior of the amount of fine powder of sodium bicarbonate added and the concentration of HCl at the outlet in Example 3.

圖15是表示實例4中微粉碳酸氫鈉添加量及出口HCl濃度的行為的圖表。 Fig. 15 is a graph showing the behavior of the amount of fine powder of sodium hydrogencarbonate added and the concentration of HCl at the outlet in Example 4.

圖16是表示實例5中微粉碳酸氫鈉添加量及出口HCl濃度的行為的圖表。 Fig. 16 is a graph showing the behavior of the amount of fine powder of sodium hydrogencarbonate added and the concentration of HCl at the outlet in Example 5.

圖17是表示實例6中微粉碳酸氫鈉添加量及出口HCl濃度的行為的圖表。 Figure 17 is a graph showing the behavior of the amount of fine powder of sodium bicarbonate added and the concentration of HCl at the outlet in Example 6.

圖18是表示實例7中微粉碳酸氫鈉添加量及出口HCl濃度的行為的圖表。 Fig. 18 is a graph showing the behavior of the amount of fine powder of sodium hydrogencarbonate added and the concentration of HCl at the outlet in Example 7.

圖19是表示實例8中微粉碳酸氫鈉添加量及出口HCl濃度的行為的圖表。 Fig. 19 is a graph showing the behavior of the amount of fine powder of sodium hydrogencarbonate added and the concentration of HCl at the outlet in Example 8.

圖20是表示實例9中微粉碳酸氫鈉添加量及出口HCl濃度的行為的圖表。 Figure 20 is a graph showing the behavior of the amount of fine powder of sodium bicarbonate added and the concentration of HCl at the outlet in Example 9.

圖21是表示實例10中微粉碳酸氫鈉添加量及出口HCl濃度的行為的圖表。 Figure 21 is a graph showing the behavior of the amount of fine powder of sodium bicarbonate added and the concentration of HCl at the outlet in Example 10.

圖22是表示實例11中微粉碳酸氫鈉添加量及出口HCl濃度的行為的圖表。 Fig. 22 is a graph showing the behavior of the amount of fine powder of sodium hydrogencarbonate added and the concentration of HCl at the outlet in Example 11.

圖23是表示實例12中微粉碳酸氫鈉添加量及出口HCl濃度的行為的圖表。 Figure 23 is a graph showing the behavior of the amount of fine powder of sodium bicarbonate added and the concentration of HCl at the outlet in Example 12.

圖24是表示實例13中微粉碳酸氫鈉添加量及出口HCl濃度的行為的圖表。 Figure 24 is a graph showing the behavior of the amount of fine powder of sodium bicarbonate added and the concentration of HCl at the outlet in Example 13.

圖25是表示實例14中微粉碳酸氫鈉添加量及出口HCl濃度的行為的圖表。 Figure 25 is a graph showing the behavior of the amount of fine powder of sodium bicarbonate added and the concentration of HCl at the outlet in Example 14.

圖26是表示實例15中微粉碳酸氫鈉添加量及出口HCl濃度的行為的圖表。 Fig. 26 is a graph showing the behavior of the amount of fine powder of sodium hydrogencarbonate added and the concentration of HCl at the outlet in Example 15.

圖27是表示實例16中微粉碳酸氫鈉添加量及出口HCl濃度的行為的圖表。 Figure 27 is a graph showing the behavior of the amount of fine powder of sodium bicarbonate added and the concentration of HCl at the outlet in Example 16.

圖28是表示實例17中微粉碳酸氫鈉添加量及出口HCl濃度的行為的圖表。 Figure 28 is a graph showing the behavior of the amount of fine powder of sodium bicarbonate added and the concentration of HCl at the outlet in Example 17.

圖29是表示實例18中微粉碳酸氫鈉添加量及出口HCl濃度的行為的圖表。 Figure 29 is a graph showing the behavior of the amount of fine powder of sodium bicarbonate added and the concentration of HCl at the outlet in Example 18.

圖30是表示比較例4中微粉碳酸氫鈉添加量、入口HCl濃度及出口HCl濃度的行為的圖表。 Fig. 30 is a graph showing the behavior of the amount of fine powder of sodium hydrogencarbonate added, the concentration of the inlet HCl, and the concentration of the outlet HCl in Comparative Example 4.

圖31是表示實例19中微粉碳酸氫鈉添加量及出口HCl濃度的行為的圖表。 Figure 31 is a graph showing the behavior of the amount of fine powder of sodium bicarbonate added and the concentration of HCl at the outlet in Example 19.

圖32是表示實例20中微粉碳酸氫鈉添加量、入口HCl濃度及出口HCl濃度的行為的圖表。 Figure 32 is a graph showing the behavior of the amount of micronized sodium bicarbonate added, the inlet HCl concentration, and the outlet HCl concentration in Example 20.

圖33是表示實例21中微粉碳酸氫鈉添加量、入口HCl濃度及出口HCl濃度的行為的圖表。 Figure 33 is a graph showing the behavior of the amount of micronized sodium bicarbonate added, the inlet HCl concentration, and the outlet HCl concentration in Example 21.

圖34是表示實例22中微粉碳酸氫鈉添加量、入口HCl濃度及出口HCl濃度的行為的圖表。 Figure 34 is a graph showing the behavior of the amount of micronized sodium bicarbonate added, the inlet HCl concentration, and the outlet HCl concentration in Example 22.

圖35是表示焚燒設備中在作為廢氣的HCl中添加微粉碳酸氫鈉的酸性氣體處理系統2的構成的方塊圖。 Fig. 35 is a block diagram showing the configuration of an acid gas treatment system 2 in which fine powder sodium hydrogencarbonate is added to HCl as an exhaust gas in an incineration facility.

圖36是表示比較例5中微粉碳酸氫鈉添加量、入口HCl濃度及出口HCl濃度的行為的圖表。 Fig. 36 is a graph showing the behavior of the amount of fine powder of sodium hydrogencarbonate added, the concentration of the inlet HCl, and the concentration of the outlet HCl in Comparative Example 5.

圖37是表示比較例6中微粉碳酸氫鈉添加量、入口HCl濃度及出口HCl濃度的行為的圖表。 37 is a graph showing the behavior of the amount of fine powder of sodium hydrogencarbonate added, the concentration of the inlet HCl, and the concentration of the outlet HCl in Comparative Example 6.

圖38是表示實例23中微粉碳酸氫鈉添加量、入口HCl濃度及出口HCl濃度的行為的圖表。 Figure 38 is a graph showing the behavior of the amount of micronized sodium bicarbonate added, the inlet HCl concentration, and the outlet HCl concentration in Example 23.

圖39是表示實例24中微粉碳酸氫鈉添加量、入口HCl濃度及出口HCl濃度的行為的圖表。 Figure 39 is a graph showing the behavior of the amount of micronized sodium bicarbonate added, the inlet HCl concentration, and the outlet HCl concentration in Example 24.

1‧‧‧酸性氣體處理系統 1‧‧‧ Acid gas treatment system

11‧‧‧控制裝置 11‧‧‧Control device

12‧‧‧微粉碳酸氫鈉添加裝置 12‧‧‧Micronized sodium bicarbonate addition device

13‧‧‧過濾袋 13‧‧‧Filter bag

14‧‧‧HCl濃度測定設備 14‧‧‧HCl concentration measuring equipment

Claims (9)

一種酸性氣體的處理方法,其在含有酸性氣體的燃燒廢氣中添加鹼劑,根據測定將粉塵集塵後的酸性氣體濃度的酸性氣體濃度測定設備的測定信號,而對鹼劑的添加量進行反饋控制,且上述酸性氣體的處理方法包括:算出至少與平均時間相對應的平均添加量乘以1倍以下的係數而得的基礎添加量的步驟;以及根據算出的上述基礎添加量,藉由反饋運算而算出鹼劑的添加量輸出值的步驟,其中上述藉由反饋運算而算出添加量輸出值的步驟進一步包括:設定至少2個酸性氣體濃度的斜率的範圍的步驟;對上述至少2個斜率的範圍的每個範圍設定酸性氣體濃度的控制目標值的步驟;以及根據至少上述測定信號及上述斜率的範圍的每個範圍的控制目標值,算出上述鹼劑的添加量輸出值的步驟;在上述設定控制目標值的步驟中,在上述酸性氣體濃度的斜率的範圍較大時設定的控制目標值,小於在上述酸性氣體濃度的斜率的範圍較小時設定的控制目標值。 A method for treating an acid gas, which comprises adding an alkali agent to a combustion exhaust gas containing an acid gas, and feeding back a measurement signal of an acid gas concentration measuring device for measuring an acid gas concentration after the dust is collected, and feeding back an amount of the alkali agent. The method for controlling the acid gas includes: a step of calculating a base addition amount obtained by multiplying an average addition amount corresponding to an average time by a factor of 1 or less; and a feedback based on the calculated base addition amount a step of calculating an output value of the addition amount of the alkaline agent, wherein the step of calculating the addition amount output value by the feedback calculation further includes the step of setting a range of slopes of at least two acid gas concentrations; and the at least two slopes a step of setting a control target value of the acid gas concentration for each range of the range; and a step of calculating an output value of the addition amount of the alkaline agent based on at least the control target value of the range of the measurement signal and the slope; In the step of setting the control target value, the range of the slope of the acid gas concentration When the control target value is set large, it is smaller than the target control value is small set in the range of inclination of the acid gas concentration. 一種酸性氣體的處理方法,其在含有酸性氣體的燃燒廢氣中添加鹼劑,根據測定將粉塵集塵後的酸性氣體濃度的酸性氣體濃度測定設備的測定信號,而對鹼劑的添加量進行反饋控制,且上述酸性氣體的處理方法包括:算出至少與平均時間相對應的平均添加量乘以1倍以下的係數而得的基礎添加量的步驟;以及 根據算出的上述基礎添加量,藉由反饋運算而算出鹼劑的添加量輸出值的步驟,其中上述藉由反饋運算而算出添加量輸出值的步驟進一步包括:在根據上述測定信號運算的添加量輸出值的下限值與上限值之間,對應上述酸性氣體濃度而設定1個以上的上述添加量輸出值的新的上限值的步驟。 A method for treating an acid gas, which comprises adding an alkali agent to a combustion exhaust gas containing an acid gas, and feeding back a measurement signal of an acid gas concentration measuring device for measuring an acid gas concentration after the dust is collected, and feeding back an amount of the alkali agent. The method for controlling the acid gas includes a step of calculating a base addition amount obtained by multiplying an average addition amount corresponding to an average time by a factor of 1 or less; a step of calculating an addition amount output value of the alkaline agent by a feedback calculation based on the calculated base addition amount, wherein the step of calculating the addition amount output value by the feedback calculation further includes: adding the amount calculated based on the measurement signal A step of setting a new upper limit value of one or more of the added amount output values corresponding to the acid gas concentration between the lower limit value and the upper limit value of the output value. 一種酸性氣體的處理方法,其在含有酸性氣體的燃燒廢氣中添加鹼劑,根據測定將粉塵集塵後的酸性氣體濃度的酸性氣體濃度測定設備的測定信號,而對鹼劑的添加量進行反饋控制,且上述酸性氣體的處理方法包括:算出至少與平均時間相對應的平均添加量乘以1倍以下的係數而得的基礎添加量的步驟;以及根據算出的上述基礎添加量,藉由反饋運算而算出鹼劑的添加量輸出值的步驟,其中上述藉由反饋運算而算出添加量輸出值的步驟進一步包括:除了上述反饋運算外,使用根據氯化氫濃度運算的控制輸出、與根據硫氧化物濃度運算的控制輸出這兩個輸出來算出鹼劑的添加量輸出值的步驟。 A method for treating an acid gas, which comprises adding an alkali agent to a combustion exhaust gas containing an acid gas, and feeding back a measurement signal of an acid gas concentration measuring device for measuring an acid gas concentration after the dust is collected, and feeding back an amount of the alkali agent. The method for controlling the acid gas includes: a step of calculating a base addition amount obtained by multiplying an average addition amount corresponding to an average time by a factor of 1 or less; and a feedback based on the calculated base addition amount a step of calculating an output value of the addition amount of the alkaline agent, wherein the step of calculating the addition amount output value by the feedback calculation further includes: using the control output calculated according to the hydrogen chloride concentration, and the sulfur oxide according to the feedback operation The control of the concentration calculation outputs the two outputs to calculate the output value of the addition amount of the alkaline agent. 一種酸性氣體的處理方法,其在含有酸性氣體的燃燒廢氣中添加鹼劑,根據測定將粉塵集塵後的酸性氣體濃度的酸性氣體濃度測定設備的測定信號,而對鹼劑的添加量進行反饋控制,且上述酸性氣體的處理方法包括:算出至少與平均時間相對應的平均添加量乘以1倍以下的係數而得的基礎添加量的步驟;以及 根據算出的上述基礎添加量,藉由反饋運算而算出鹼劑的添加量輸出值的步驟,其中上述鹼劑是平均粒徑為5μm~30μm的微粉碳酸氫鈉。 A method for treating an acid gas, which comprises adding an alkali agent to a combustion exhaust gas containing an acid gas, and feeding back a measurement signal of an acid gas concentration measuring device for measuring an acid gas concentration after the dust is collected, and feeding back an amount of the alkali agent. The method for controlling the acid gas includes a step of calculating a base addition amount obtained by multiplying an average addition amount corresponding to an average time by a factor of 1 or less; The step of calculating the output amount of the alkali agent added by the feedback calculation based on the calculated base addition amount, wherein the alkali agent is a fine powder of sodium hydrogencarbonate having an average particle diameter of 5 μm to 30 μm. 如申請專利範圍第4項所述之酸性氣體的處理方法,其中併用與上述微粉碳酸氫鈉不同的其他鹼劑。 A method for treating an acid gas as described in claim 4, wherein a different alkali agent different from the above-mentioned fine powder sodium hydrogencarbonate is used in combination. 如申請專利範圍第5項所述之酸性氣體的處理方法,其中上述其他鹼劑是選自由氫氧化鈣、氫氧化鈉、氫氧化鎂、氧化鎂、碳酸鈉、倍半碳酸鈉、天然蘇打、及粗碳酸氫鈉所組成群組中的至少1種鹼劑。 The method for treating an acid gas according to claim 5, wherein the other alkali agent is selected from the group consisting of calcium hydroxide, sodium hydroxide, magnesium hydroxide, magnesium oxide, sodium carbonate, sodium sesquicarbonate, natural soda, And at least one alkali agent in the group consisting of crude sodium hydrogencarbonate. 如申請專利範圍第1項至第6項中任一項所述之酸性氣體的處理方法,其中在上述藉由反饋運算而算出添加量輸出值的步驟中,將算出的上述基礎添加量設為上述鹼劑的添加量輸出值的下限值。 The method for treating an acid gas according to any one of the preceding claims, wherein, in the step of calculating the addition amount output value by the feedback calculation, the calculated base addition amount is set to The amount of addition of the above-mentioned alkali agent is the lower limit of the output value. 如申請專利範圍第1項至第6項中任一項所述之酸性氣體的處理方法,其中在上述算出基礎添加量的步驟中,將平均時間為5分鐘以上時的平均添加量的0.5倍~0.95倍設為基礎添加量。 The method for treating an acid gas according to any one of the preceding claims, wherein, in the step of calculating the base addition amount, 0.5 times the average addition amount when the average time is 5 minutes or longer ~0.95 times is set as the base addition amount. 如申請專利範圍第1項至第6項中任一項所述之酸性氣體的處理方法,其中上述藉由反饋運算而算出添加量輸出值的步驟進一步包括:除了上述反饋運算外,根據氯化氫濃度及/或硫氧化物濃度的平均值算出原本的鹼劑的添加量輸出值的步驟。 The method for treating an acid gas according to any one of the preceding claims, wherein the step of calculating the added amount output value by the feedback calculation further comprises: in addition to the feedback calculation, according to a hydrogen chloride concentration And/or the average value of the sulfur oxide concentration is a step of calculating the output value of the original alkali agent addition amount.
TW101124563A 2011-07-14 2012-07-09 Method for treating acidic gas TWI565514B (en)

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2011156131A JP5720455B2 (en) 2011-07-14 2011-07-14 Acid gas treatment method

Publications (2)

Publication Number Publication Date
TW201306918A TW201306918A (en) 2013-02-16
TWI565514B true TWI565514B (en) 2017-01-11

Family

ID=47506193

Family Applications (2)

Application Number Title Priority Date Filing Date
TW101124563A TWI565514B (en) 2011-07-14 2012-07-09 Method for treating acidic gas
TW104108558A TWI608861B (en) 2011-07-14 2012-07-09 Method for treating acidic gas

Family Applications After (1)

Application Number Title Priority Date Filing Date
TW104108558A TWI608861B (en) 2011-07-14 2012-07-09 Method for treating acidic gas

Country Status (6)

Country Link
JP (1) JP5720455B2 (en)
KR (1) KR101528743B1 (en)
CN (1) CN103648616B (en)
MY (1) MY163303A (en)
TW (2) TWI565514B (en)
WO (1) WO2013008918A1 (en)

Families Citing this family (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP5983849B2 (en) * 2014-12-10 2016-09-06 栗田工業株式会社 Automatic sampling apparatus and automatic sampling method for fly ash
JP6908820B2 (en) * 2015-12-24 2021-07-28 セントラル硝子株式会社 Formic acid treatment method and formic acid treatment equipment
JP6498626B2 (en) * 2016-03-28 2019-04-10 Jx金属株式会社 Desulfurization agent addition control method
CN110022965A (en) * 2016-12-02 2019-07-16 日立造船株式会社 Emission-control equipment, burning facility and waste gas processing method
JP6517290B2 (en) * 2017-09-04 2019-05-22 株式会社プランテック Exhaust gas treatment method and exhaust gas treatment apparatus
JP6737315B2 (en) * 2018-10-18 2020-08-05 栗田工業株式会社 Inventory management system and inventory management method for treating agents used for treating exhaust gas
CN110687307A (en) * 2019-09-24 2020-01-14 香港大德昌龙生物科技有限公司 In-vitro diagnostic reagent supplementing method, system, equipment and storage medium
TWI834124B (en) * 2022-03-02 2024-03-01 達和環保服務股份有限公司 Incineration system executing flue-gas desulfurization by using sodium hydrogen carbonate
KR20240003494A (en) 2022-07-01 2024-01-09 (주)청해소재 Neutralizing Agent Composition For Acid Gas

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010227749A (en) * 2009-03-26 2010-10-14 Jfe Engineering Corp Method of treating exhaust gas

Family Cites Families (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH084709B2 (en) * 1986-04-23 1996-01-24 バブコツク日立株式会社 Wet Flue Gas Desulfurization Controller
JPH10165752A (en) * 1996-12-16 1998-06-23 Nippon Steel Corp Exhaust gas treatment process for waste disposal facility
JP3976444B2 (en) * 1998-06-23 2007-09-19 株式会社タクマ Exhaust gas treatment method and treatment apparatus
JP4667577B2 (en) * 2000-10-11 2011-04-13 三井造船株式会社 Exhaust gas treatment desalting agent supply amount control method, supply amount control device, and waste treatment system
JP2002361040A (en) * 2001-06-12 2002-12-17 Takuma Co Ltd Control method of waste gas treatment and its control mechanism
JP2003210934A (en) * 2002-01-23 2003-07-29 Mitsubishi Heavy Ind Ltd Equipment for exhaust-gas treatment
JP4821102B2 (en) * 2004-09-10 2011-11-24 Jfeエンジニアリング株式会社 Desalination control device and desalination control method
JP2007237019A (en) * 2006-03-06 2007-09-20 Mitsui Eng & Shipbuild Co Ltd Feed amount control method for exhaust gas treatment chemical and exhaust gas treatment apparatus
JP5302618B2 (en) * 2008-10-16 2013-10-02 三菱重工業株式会社 Nitrogen oxide treatment equipment
JP5338421B2 (en) * 2009-03-24 2013-11-13 栗田工業株式会社 Combustion exhaust gas treatment method and apparatus
JP5443805B2 (en) * 2009-03-25 2014-03-19 公立大学法人大阪府立大学 Collection method of aluminum foil

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010227749A (en) * 2009-03-26 2010-10-14 Jfe Engineering Corp Method of treating exhaust gas

Also Published As

Publication number Publication date
JP2013022471A (en) 2013-02-04
JP5720455B2 (en) 2015-05-20
CN103648616A (en) 2014-03-19
KR20140036313A (en) 2014-03-25
KR101528743B1 (en) 2015-06-15
TWI608861B (en) 2017-12-21
WO2013008918A1 (en) 2013-01-17
TW201524584A (en) 2015-07-01
MY163303A (en) 2017-09-15
CN103648616B (en) 2016-02-17
TW201306918A (en) 2013-02-16

Similar Documents

Publication Publication Date Title
TWI565514B (en) Method for treating acidic gas
TWI450754B (en) Method for treating acidic gas
TWI465283B (en) Treatment method for acidic gas
JP6020085B2 (en) Acid gas stabilization method and combustion exhaust gas treatment facility
JP6700952B2 (en) Exhaust gas desalination apparatus and exhaust gas desalination method
JP2010532460A (en) Use of halogen and nitrogen containing compounds to reduce mercury emissions during coal combustion
CA2813595A1 (en) Use of bromine or bromide containing organic compositions for reducing mercury emissions during coal combustion
JPWO2014046079A1 (en) Smoke exhaust processing method and smoke exhaust processing apparatus
JP5955622B2 (en) Exhaust gas treatment apparatus and exhaust gas treatment method using the same
JP5694276B2 (en) Exhaust gas treatment apparatus and method
JP2013017956A (en) Method for controlling additive rate of chelating agent to fly ash
JP5022339B2 (en) Incineration ash melting method and equipment
WO2013136420A1 (en) Method for treating acidic gas
JP4514529B2 (en) Sewage sludge melting treatment method
JP2020049430A (en) Processor and processing method of fly ashes
TWI845824B (en) Exhaust treatment system and exhaust treatment method
JP6939677B2 (en) Method of controlling the amount of drug added
JP6703748B2 (en) Exhaust gas treatment device and exhaust gas treatment method
JP2005270722A (en) Exhaust gas treatment method and equipment therefor
FI4008425T3 (en) Method for removing mercury from fumes
JP2020179353A (en) Waste incineration system
JP2002028612A (en) Method for treating fly ash
JP2015085258A (en) Insolubilization method of heavy metal in alkali fly ash
JPH10305206A (en) Temperature control method for dust collector of waste incineration furnace
JP2019155259A (en) Exhaust gas processing device and exhaust gas processing method