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JPS6249097B2 - - Google Patents
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JPS6249097B2 - - Google Patents

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Publication number
JPS6249097B2
JPS6249097B2 JP58031340A JP3134083A JPS6249097B2 JP S6249097 B2 JPS6249097 B2 JP S6249097B2 JP 58031340 A JP58031340 A JP 58031340A JP 3134083 A JP3134083 A JP 3134083A JP S6249097 B2 JPS6249097 B2 JP S6249097B2
Authority
JP
Japan
Prior art keywords
furnace
temperature
absorbent
supply pipe
hcl gas
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired
Application number
JP58031340A
Other languages
Japanese (ja)
Other versions
JPS59156416A (en
Inventor
Yoshitoshi Sekiguchi
Kunio Sasaki
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Kanadevia Corp
Original Assignee
Hitachi Shipbuilding and Engineering Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Hitachi Shipbuilding and Engineering Co Ltd filed Critical Hitachi Shipbuilding and Engineering Co Ltd
Priority to JP58031340A priority Critical patent/JPS59156416A/en
Publication of JPS59156416A publication Critical patent/JPS59156416A/en
Publication of JPS6249097B2 publication Critical patent/JPS6249097B2/ja
Granted legal-status Critical Current

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Description

【発明の詳細な説明】 この発明は燃焼炉内における脱硫法に関する。[Detailed description of the invention] The present invention relates to a method for desulfurization in a combustion furnace.

硫黄分を含有する燃料の燃焼に伴つて発生する
硫黄酸化物(以下SOxと称する)は、公害の原因
物質であるため、これを効果的に除去する方法が
要望せられ、従来多くのSOx除去技術が提案ない
し実用化されている。しかしこれらの方法はいず
れも液体ないし気体燃料を対象としたものである
ため、固体燃焼炉からの排ガスのように多量のダ
ストを含んだ排ガスの脱硫に適用すると、ダスト
による脱硫装置の閉塞や脱硫率の低下などの問題
をまねいた。そこでこの問題の解決策として、炭
酸カルシウム(石灰石)、消石灰、ドロマイトな
どの固形のCa含有SOx吸収剤を火炉内へ直接噴
射供給する乾式炉内脱硫法が提案された。しかし
この方法では高温の酸化雰囲気中へ吸収剤を直接
供給するため、Caの反応率は15%以下と極めて
低く、実用化は困難であつた。
Sulfur oxides (hereinafter referred to as SOx) generated when sulfur-containing fuel is burned are a substance that causes pollution, so there is a need for a method to effectively remove them. A technology has been proposed or put into practical use. However, all of these methods target liquid or gaseous fuels, so when applied to the desulfurization of exhaust gas that contains a large amount of dust, such as exhaust gas from a solid combustion furnace, the desulfurization equipment may be clogged with dust or desulfurization may occur. This led to problems such as a decline in the rate. As a solution to this problem, a dry in-furnace desulfurization method was proposed in which a solid Ca-containing SOx absorbent such as calcium carbonate (limestone), slaked lime, or dolomite is directly injected into the furnace. However, since this method directly supplies the absorbent into a high-temperature oxidizing atmosphere, the reaction rate of Ca is extremely low at less than 15%, making it difficult to put it into practical use.

この発明は、上記のような点からなされたもの
で、脱硫率の極めて高い燃焼炉内脱硫法を提供す
ることを目的とする。
The present invention was made in view of the above points, and an object of the present invention is to provide a combustion furnace desulfurization method with an extremely high desulfurization rate.

この発明による脱硫法は、HClガスを温度150
〜500℃の範囲でCa含有SOx吸収剤に吸収させて
おき、同吸収剤を炉内温度900〜1300℃の範囲で
炉内に供給することを特徴とするものである。
The desulfurization method according to this invention uses HCl gas at a temperature of 150
It is characterized by allowing the Ca-containing SOx absorbent to absorb the SOx at a temperature in the range of ~500°C, and supplying the same absorbent into the furnace at an internal temperature of 900 to 1300°C.

Ca含有SOx吸収剤へのHClガス吸収において、
温度が150℃以下であると、吸収剤供給管その他
の低温腐食が生じ、逆に500℃以上では高温腐食
を生じる。したがつて上記温度は150〜500℃の範
囲に限定される。この温度範囲の調整は、Ca含
有SOx吸収剤の加熱またはHClガスの加熱によつ
てなされる。燃料としては、石炭を微粉化した微
粉炭のような固体燃料がよく用いられるが、これ
は限定的なものではない。
In HCl gas absorption into Ca-containing SOx absorbent,
If the temperature is below 150°C, low-temperature corrosion of the absorbent supply pipe and other parts will occur, whereas if the temperature is above 500°C, high-temperature corrosion will occur. Therefore, the above temperature is limited to a range of 150 to 500°C. Adjustment of this temperature range is achieved by heating the Ca-containing SOx absorbent or heating the HCl gas. As the fuel, solid fuel such as pulverized coal, which is obtained by pulverizing coal, is often used, but this is not limiting.

炉内温度が900℃以下ではSOx吸収反応が長く
かかつて実用的でない。炉内温度が1300℃を越え
るとCaの反応率が低下する。したがつて炉内温
度は900〜1300℃に限定され、特に好適な温度は
1000〜1200℃である。Ca含有SOx吸収剤として
は、CaCO3、Ca(OH)2、ドロマイトなどがよく
用いられる。
If the temperature inside the furnace is below 900℃, the SOx absorption reaction will take a long time or it will not be practical. When the temperature inside the furnace exceeds 1300℃, the reaction rate of Ca decreases. Therefore, the temperature inside the furnace is limited to 900 to 1300℃, and the particularly suitable temperature is
The temperature is 1000-1200℃. CaCO 3 , Ca(OH) 2 , dolomite, and the like are often used as Ca-containing SOx absorbents.

つぎに、この発明において使用する燃焼炉の構
造について説明する。
Next, the structure of the combustion furnace used in this invention will be explained.

第1図に示す横型円筒炉において、1は円筒状
周壁2とその両端に設けられた前壁3と後壁4と
からなる炉本体で、吸熱用ウオータ・ジヤケツト
で覆われている。5は前壁3の中央にあけられた
開口で、2次空気供給用の前方突出部6を有す
る。7は同前方突部6の中心部に炉内向きに配さ
れたバーナで、ここから微粉炭と燃料輸送用1次
空気の混合物が供給される。8は前壁3の前面に
設けられた風箱で、開口5を介して炉内に通じて
いる。9は周壁2の長さの中央部から炉内軸心部
に配された吸収剤供給管で、先端にバーナ向きの
ノズル10を有する。11は吸収剤を輸送するた
めのブロアで、これに吸収剤供給管9の基端部が
接続されている。12は同供給管9に設けられた
吸収剤供給フイーダ、13はブロア11とフイー
ダ12の間で吸収剤供給管9に設けられたヒー
タ、14はフイーダ12と炉本体1の間で吸収剤
供給管9に接続されたHClガス供給管である。
In the horizontal cylindrical furnace shown in FIG. 1, numeral 1 denotes a furnace body consisting of a cylindrical peripheral wall 2, a front wall 3 and a rear wall 4 provided at both ends thereof, and is covered with a water jacket for absorbing heat. 5 is an opening made in the center of the front wall 3, and has a front protrusion 6 for supplying secondary air. Reference numeral 7 denotes a burner arranged in the center of the front protrusion 6 facing inward of the furnace, from which a mixture of pulverized coal and primary air for fuel transportation is supplied. Reference numeral 8 denotes a wind box provided on the front side of the front wall 3, which communicates with the inside of the furnace through an opening 5. Reference numeral 9 denotes an absorbent supply pipe arranged from the center of the length of the peripheral wall 2 to the axial center of the furnace, and has a nozzle 10 facing the burner at its tip. Reference numeral 11 denotes a blower for transporting the absorbent, to which the base end of the absorbent supply pipe 9 is connected. 12 is an absorbent supply feeder provided in the supply pipe 9; 13 is a heater provided in the absorbent supply pipe 9 between the blower 11 and the feeder 12; and 14 is an absorbent supply feeder provided between the feeder 12 and the furnace main body 1. This is an HCl gas supply pipe connected to pipe 9.

第2図は燃焼炉の変形を示すもので、この場合
ヒータ13はHClガス供給管14に設けられてい
る。
FIG. 2 shows a modification of the combustion furnace, in which the heater 13 is installed in the HCl gas supply pipe 14.

第3図は燃焼炉の第2の変形を示すものであ
る。この炉21は箱形の大型垂直炉であつて、や
はりウオータ・ジヤケツトで覆われており、前壁
22の下端部に第1図の燃焼炉のものと同じ構造
の燃焼用2次空気供給口23とバーナ24と風箱
25が設けられ、バーナ24から微粉炭と燃料輸
送用1次空気の混合物が供給される。また風箱2
5の上方において前壁22に吸収剤供給管26が
配され、同供給管26には、第1図の場合と同じ
く、基端部のブロア27とヒータ28と吸収剤供
給フイーダ29とHClガス供給管30が設けられ
ている。
FIG. 3 shows a second variant of the combustion furnace. This furnace 21 is a box-shaped large vertical furnace, which is also covered with a water jacket, and has a secondary air supply port for combustion at the lower end of the front wall 22, which has the same structure as that of the combustion furnace shown in FIG. 23, a burner 24, and a wind box 25 are provided, and a mixture of pulverized coal and primary air for fuel transportation is supplied from the burner 24. Also Kazebako 2
An absorbent supply pipe 26 is disposed on the front wall 22 above 5, and the supply pipe 26 includes a blower 27 at the base end, a heater 28, an absorbent supply feeder 29, and an HCl gas supply pipe 26, as in the case of FIG. A supply pipe 30 is provided.

実験 1 第1図に示す横型円筒炉(内径1.5m、長さ7
m)において、バーナ7から炉内へ微粉炭(200
Kg/h)と1次空気の混合物を供給し、さらに風
箱8から炉内へ2次空気を供給して燃焼を行なつ
た。排ガスの酸素濃度は4.5%で、脱硫前のSO2
の濃度は900ppmであつた。
Experiment 1 A horizontal cylindrical furnace (inner diameter 1.5 m, length 7
m), pulverized coal (200 m) is transferred from burner 7 into the furnace.
Kg/h) and primary air were supplied, and secondary air was further supplied into the furnace from the wind box 8 to carry out combustion. The oxygen concentration in the exhaust gas is 4.5%, and SO 2 before desulfurization
The concentration of was 900ppm.

一方、吸収剤供給フイーダ12からSOx吸収剤
としてCaCO3をCa/S(当量比)=3.0の割合で
温度150〜500℃の範囲で炉内に供給するととも
に、CaCO3の供給路上においてHClガスを供給し
てCaCO3に吸収せしめた(炉内反応時間1.7〜2
秒)。炉内温度を800〜1400℃の範囲で所定値に調
節し、各炉内温度におけるCa反応率(CaSO4
CaCO3)を測定した。またHClガスを供給せずに
上記操作を操返した。これらの実験の結果を第4
図に示す。同図から明らかなように、SOx吸収剤
は炉内温度900〜1300℃特に1000〜1200℃におい
て高い反応性を示した。
On the other hand, CaCO 3 is supplied as an SOx absorbent from the absorbent supply feeder 12 into the furnace at a ratio of Ca/S (equivalent ratio) = 3.0 at a temperature in the range of 150 to 500°C, and HCl gas is supplied on the CaCO 3 supply path. was supplied and absorbed into CaCO 3 (in-furnace reaction time 1.7-2
seconds). The furnace temperature was adjusted to a predetermined value in the range of 800 to 1400℃, and the Ca reaction rate (CaSO 4 /
CaCO 3 ) was measured. The above operation was also repeated without supplying HCl gas. The results of these experiments are summarized in the fourth
As shown in the figure. As is clear from the figure, the SOx absorbent showed high reactivity at the furnace temperature of 900 to 1300°C, especially at 1000 to 1200°C.

実験 2 つぎに炉内温度を1000℃に調節し、SOx吸収剤
をCa/S(当量比)=1〜4の範囲で所定値に調
節して供給し(反応時間=2秒)、その他の条件
を実験1と同じにし、各Ca/S値におけるCa反
応率を測定した。またHClガスを供給せずに上記
操作を繰返した。これらの実験の結果を第5図に
示す。同図から明らかなように、HClガスを供給
する場合、供給しない場合に比べて、高いCa反
応率が示された。
Experiment 2 Next, the temperature inside the furnace was adjusted to 1000℃, and the SOx absorbent was adjusted to a predetermined value in the range of Ca/S (equivalence ratio) = 1 to 4 and supplied (reaction time = 2 seconds). The conditions were the same as in Experiment 1, and the Ca reaction rate at each Ca/S value was measured. The above operation was also repeated without supplying HCl gas. The results of these experiments are shown in FIG. As is clear from the figure, a higher Ca reaction rate was shown when HCl gas was supplied than when it was not supplied.

以上のとおり、この発明の脱硫法によれば、
HClガスを所定温度範囲でCa含有SOx吸収剤に吸
収させるので、HClガスによる吸収剤供給管の腐
食を回避することができる。さらに脱硫率は温度
900〜1300℃において極めて高く、反応時間は秒
単位で十分である。
As described above, according to the desulfurization method of this invention,
Since HCl gas is absorbed into the Ca-containing SOx absorbent within a predetermined temperature range, corrosion of the absorbent supply pipe due to HCl gas can be avoided. Furthermore, the desulfurization rate is determined by the temperature
The temperature is extremely high at 900-1300°C, and the reaction time is sufficient on the order of seconds.

【図面の簡単な説明】[Brief explanation of the drawing]

第1図、第2図および第3図は燃焼炉をそれぞ
れ示す垂直断面図、第4図は炉内温度とCa反応
率の関係を示すグラフ、第5図はCa/S当量比
とCa反応率の関係を示すグラフである。 7,24……バーナ、9,26……吸収剤供給
管、14,30……HClガス供給管。
Figures 1, 2, and 3 are vertical cross-sectional views showing the combustion furnace, Figure 4 is a graph showing the relationship between furnace temperature and Ca reaction rate, and Figure 5 is a graph showing the relationship between Ca/S equivalence ratio and Ca reaction. It is a graph showing the relationship between rates. 7, 24... Burner, 9, 26... Absorbent supply pipe, 14, 30... HCl gas supply pipe.

Claims (1)

【特許請求の範囲】[Claims] 1 HClガスを温度150〜500℃の範囲でCa含有
SOx吸収剤に吸収させておき、同吸収剤を炉内温
度900〜1300℃の範囲で炉内に供給することを特
徴とする燃焼炉内脱硫法。
1 HCl gas containing Ca at a temperature range of 150 to 500℃
A combustion furnace desulfurization method characterized by absorbing SOx in an absorbent and supplying the absorbent into the furnace at a furnace temperature in the range of 900 to 1300°C.
JP58031340A 1983-02-25 1983-02-25 Combustion furnace desulfurization method Granted JPS59156416A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP58031340A JPS59156416A (en) 1983-02-25 1983-02-25 Combustion furnace desulfurization method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP58031340A JPS59156416A (en) 1983-02-25 1983-02-25 Combustion furnace desulfurization method

Publications (2)

Publication Number Publication Date
JPS59156416A JPS59156416A (en) 1984-09-05
JPS6249097B2 true JPS6249097B2 (en) 1987-10-16

Family

ID=12328506

Family Applications (1)

Application Number Title Priority Date Filing Date
JP58031340A Granted JPS59156416A (en) 1983-02-25 1983-02-25 Combustion furnace desulfurization method

Country Status (1)

Country Link
JP (1) JPS59156416A (en)

Also Published As

Publication number Publication date
JPS59156416A (en) 1984-09-05

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