JPH0131560B2 - - Google Patents
Info
- Publication number
- JPH0131560B2 JPH0131560B2 JP55155188A JP15518880A JPH0131560B2 JP H0131560 B2 JPH0131560 B2 JP H0131560B2 JP 55155188 A JP55155188 A JP 55155188A JP 15518880 A JP15518880 A JP 15518880A JP H0131560 B2 JPH0131560 B2 JP H0131560B2
- Authority
- JP
- Japan
- Prior art keywords
- exhaust gas
- process fluid
- preheater
- catalyst layer
- reducing agent
- 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
Links
Landscapes
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
- Production Of Liquid Hydrocarbon Mixture For Refining Petroleum (AREA)
Description
【発明の詳細な説明】
この発明は水蒸気改質炉から排出される窒素酸
化物(以下NOxと略称する)の量を低減するの
に好適な構造を有する蒸気改質炉に関する。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a steam reforming furnace having a structure suitable for reducing the amount of nitrogen oxides (hereinafter abbreviated as NOx) discharged from the steam reforming furnace.
炭化水素系ガスに蒸気を添加してこのガスを改
質する改質炉は、炭化水素系ガスと蒸気の混合気
体を加熱する必要上この加熱源として燃料を燃焼
し、このため他の形式の炉と同様燃焼排ガス中の
NOxを低減する装置にする必要がある。 Reforming furnaces, which add steam to hydrocarbon gas to reform this gas, burn fuel as a heating source in order to heat the mixture of hydrocarbon gas and steam, and for this reason, other types of reformers are used. Similar to furnaces, combustion exhaust gas
It is necessary to use equipment that reduces NOx.
従来各種の形式の炉から排出されるNOxを低
減する方法としてはバーナ構造の改善、燃焼用空
気量の制限、排ガスの再循環等燃焼の段階で
NOxの発生量を低減する方法と、発生したNOx
を還元剤等を添加することにより除去する方法が
主として採用されている。ここで水蒸気改質炉に
あつては、反応温度を正確に保持し、かつ反応部
を形成する管体を保護する必要上、加熱体として
は輻射型短炎バーナを採用し、このバーナの燃焼
を正確に制御している。このため、NOx低減の
観点から燃焼を制御する余地が少なく、NOxの
低減はもつぱら触媒法脱硝装置を利用している。
しかしこの方法は触媒自体が高価であるため不経
済であり、かつ還元剤の注入に当つても注入すべ
き温度域を誤ると還元剤が熱分解してかえつて
NOxの量を増加させる等の問題がある。 Conventional methods to reduce NOx emitted from various types of furnaces include improving the burner structure, limiting the amount of combustion air, and recirculating exhaust gas at the combustion stage.
How to reduce the amount of NOx generated and NOx generated
The most commonly used method is to remove this by adding a reducing agent or the like. In the case of a steam reforming furnace, a radiant short flame burner is used as the heating element in order to accurately maintain the reaction temperature and protect the tube that forms the reaction part. is precisely controlled. For this reason, there is little room to control combustion from the perspective of reducing NOx, and catalytic denitrification equipment is used exclusively to reduce NOx.
However, this method is uneconomical because the catalyst itself is expensive, and if the temperature range at which the reducing agent is injected is incorrect, the reducing agent may thermally decompose and cause damage.
There are problems such as increasing the amount of NOx.
この発明の目的は上述した問題点を解決し、少
ない触媒量で大きな脱硝率を得ることができる。
蒸気改質炉を提供することにある。 An object of the present invention is to solve the above-mentioned problems and to obtain a high denitrification rate with a small amount of catalyst.
Our objective is to provide a steam reforming furnace.
要するにこの発明は下降流排ガス通路内での触
媒反応温度の特性を考慮して触媒層を排ガス流路
中の300〜400℃程度の温度域に配置し、かつ還元
剤をこの触媒層近傍の上流で噴霧する装置である
ことを特徴とするものである。 In short, this invention takes into account the characteristics of the catalytic reaction temperature in the downflow exhaust gas passage, places the catalyst layer in the exhaust gas passage in a temperature range of about 300 to 400°C, and places the reducing agent upstream near the catalyst layer. The device is characterized in that it is a device that sprays water.
以下この発明の実施例を図面を用いて説明す
る。 Embodiments of the present invention will be described below with reference to the drawings.
第1図は改質炉を示す。炭化水炭系ガスと蒸気
の混合気体はリフオーマチユーブ3内を流れ輻射
型の短炎バーナ2(以下単に「バーナ」と称す
る)の輻射熱により加熱、改質され、改質ガスは
下方に設置されたプロセスガスボイラへと流れ
る。一方バーナ2の燃焼により生じた排ガスは排
ガス出口4に至り排ガスダクト5に流入する。こ
の排ガスダクト5内には排ガスの有する顕熱を回
収する目的で複数段の熱交換器が配置してある。
熱交換器の配列順序は通常図示の如く上段から順
に蒸気過熱器6、廃熱回収ボイラ7、複数の管群
に分れたプロセス流体(被処理ガス)予熱器8お
よび給水予熱器9の順に配置してある。 Figure 1 shows a reforming furnace. A mixed gas of hydrocarbon-carbon gas and steam flows through the re-formation tube 3 and is heated and reformed by the radiant heat of the radiant short flame burner 2 (hereinafter simply referred to as "burner"), and the reformed gas is installed below. The processed gas flows to the boiler. On the other hand, exhaust gas generated by combustion in the burner 2 reaches an exhaust gas outlet 4 and flows into an exhaust gas duct 5. A plurality of heat exchangers are arranged in the exhaust gas duct 5 for the purpose of recovering sensible heat contained in the exhaust gas.
As shown in the figure, the heat exchangers are normally arranged in the following order from the top: a steam superheater 6, a waste heat recovery boiler 7, a process fluid (gas to be treated) preheater 8 divided into a plurality of tube groups, and a feed water preheater 9. It has been placed.
ここで排ガス中のNOxを除去する選択接触脱
硝装置は脱硝触媒層と、この触媒層上流側に位置
する還元剤噴霧部とから構成してある。このうち
触媒層の反応特性をみると、温度が触媒の反応性
に与える影響は非常に大きく、グラフに示すと第
2図の如くなる。このグラフから明らかなとお
り、300〜400℃の温度域において触媒の活性が高
くなり、触媒層の設置域として好適である。特に
350〜400℃の温度域において触媒の脱硝率は最大
となる。一方触媒層の上流に噴霧されるNH3等
の還元剤はあまり高温となると還元剤自体が熱分
解してしまい、かえつてNOxの生成量が増大す
るという問題がある。つまり触媒層の設置位置か
ら離れて上流側に向うほど高温となるわけである
から、還元剤の均一分散が可能な限り、還元剤は
触媒層に近接した位置で噴霧するのが好ましい。 The selective catalytic denitrification device that removes NOx from exhaust gas is comprised of a denitrification catalyst layer and a reducing agent spray section located upstream of this catalyst layer. Looking at the reaction characteristics of the catalyst layer, temperature has a very large effect on the reactivity of the catalyst, as shown in a graph as shown in FIG. As is clear from this graph, the activity of the catalyst is high in the temperature range of 300 to 400°C, which is a suitable range for the installation of the catalyst layer. especially
The denitrification rate of the catalyst reaches its maximum in the temperature range of 350 to 400°C. On the other hand, if a reducing agent such as NH 3 that is sprayed upstream of the catalyst layer is heated to too high a temperature, the reducing agent itself will be thermally decomposed, resulting in an increase in the amount of NOx produced. In other words, since the temperature increases as the distance from the installation position of the catalyst layer increases toward the upstream side, it is preferable to spray the reducing agent at a position close to the catalyst layer as long as uniform dispersion of the reducing agent is possible.
第3図は、この発明の実施例である第1図に示
した改質炉の排ガスダクト5の温度分布を示し、
排ガスダクト入口部Aで約1000〜1100℃、蒸気加
熱器出口Bで約800〜850℃、廃熱回収ボイラ出口
Cで約600〜650℃、プロセス流体予熱器出口Dで
約250〜300℃、給水予熱器出口Eで約150〜200℃
となつている。従つて第2図に示した反応特性か
ら、触媒層の設置位置はプロセス流体予熱器8の
設置位置もしくはこの近傍が良好である。第1図
においては触媒層(符号10で示す)は複数の伝
熱管群に分れたプロセス流体予熱器8内に配置す
る。次にNH3等の脱硝剤はこの触媒層8に近接
し、しかも還元剤の均一分散が可能な位置におい
て噴霧する。図示の場合はこれを実現するため触
媒層10の上流側に位置するプロセス流体予熱器
8の伝熱管群の上流部に還元剤噴霧装置11を配
置する。 FIG. 3 shows the temperature distribution of the exhaust gas duct 5 of the reformer shown in FIG. 1, which is an embodiment of the present invention.
Approximately 1000 to 1100°C at the exhaust gas duct inlet A, approximately 800 to 850°C at the steam heater outlet B, approximately 600 to 650°C at the waste heat recovery boiler outlet C, and approximately 250 to 300°C at the process fluid preheater outlet D. Approximately 150 to 200℃ at water preheater outlet E
It is becoming. Therefore, from the reaction characteristics shown in FIG. 2, the catalyst layer is preferably installed at or near the process fluid preheater 8. In FIG. 1, a catalyst layer (designated 10) is located within a process fluid preheater 8 that is divided into a plurality of heat transfer tube groups. Next, a denitration agent such as NH 3 is sprayed close to the catalyst layer 8 at a position where the reducing agent can be uniformly dispersed. In the illustrated case, in order to realize this, the reducing agent spraying device 11 is disposed upstream of the heat transfer tube group of the process fluid preheater 8 located upstream of the catalyst layer 10.
この発明を実施することにより蒸気改質炉の如
く燃焼制御によりNOxを低減することが困難な
燃焼装置から排出される排ガス中のNOxを少い
触媒量で効果的に低減することができる。 By implementing the present invention, it is possible to effectively reduce NOx in the exhaust gas discharged from a combustion device, such as a steam reformer, in which it is difficult to reduce NOx through combustion control, with a small amount of catalyst.
また排ガス通路内は鉛直の下降流となつてお
り、かつこの通路内に熱を交換する装置が複数前
記の如く配置され、単位蒸気改質炉が複数炉ある
ので排ガスの量も一の排ガス下降流通路を流れる
ので排ガス流速を大とし熱交換の効果を挙げるこ
とができ、かつ還元剤噴霧装置は脱硝に好適な排
ガス温度の位置に設けられている。 In addition, the inside of the exhaust gas passage is a vertical downward flow, and multiple devices for exchanging heat are arranged in this passage as described above, and there are multiple unit steam reforming furnaces, so the amount of exhaust gas is also downward. Since the exhaust gas flows through the flow path, the flow rate of the exhaust gas can be increased and the effect of heat exchange can be achieved, and the reducing agent spraying device is provided at a position where the exhaust gas temperature is suitable for denitrification.
一方このような構造にすることは第1図に示す
蒸気改質炉の占める床面積が熱交換器が水平配置
のものに比べ格段に小さく済み、運転休止の場合
には排ガス通路下端に滞留する空気の比重を1と
するときアンモニアは0.596であることから有害
な漏洩アンモニアガスにつきこの空気がガスシー
ルの効果を奏することとなる。 On the other hand, with this structure, the floor area occupied by the steam reforming furnace shown in Figure 1 is much smaller than that of one in which the heat exchanger is arranged horizontally, and in the event of a suspension of operation, the steam reforming furnace will remain at the lower end of the exhaust gas passage. When the specific gravity of air is 1, the specific gravity of ammonia is 0.596, so this air acts as a gas seal against harmful leaked ammonia gas.
第1図は本発明の実施例である蒸気改質炉の断
面図、第2図は脱硝触媒の温度特性を示す線図、
第3図はボイラダクト各部における温度分布を示
す線図である。
5……排ガスダクト、8……プロセス流体予熱
器、10……触媒層、11……還元剤噴霧装置。
FIG. 1 is a cross-sectional view of a steam reforming furnace that is an embodiment of the present invention, and FIG. 2 is a diagram showing the temperature characteristics of the denitrification catalyst.
FIG. 3 is a diagram showing the temperature distribution in each part of the boiler duct. 5...Exhaust gas duct, 8...Process fluid preheater, 10...Catalyst layer, 11...Reducing agent spray device.
Claims (1)
側に複数の輻射型短炎バーナを複数段設けた単位
蒸気改質炉の複数炉の頂部燃焼ガス通路を集合さ
せ一の下降流排ガス通路を形成し、該下降流排ガ
ス通路に上流から順に、蒸気過熱器6、廃熱回収
ボイラ7、第1のプロセス流体予熱器8還元剤噴
霧装置11、第2のプロセス流体予熱器8、350
℃〜400℃の排ガスに接触する触媒層10、第3
のプロセス流体予熱器8、給水予熱器9を位置さ
せたことを特徴とする蒸気改質炉。1 The top combustion gas passages of multiple furnaces of a unit steam reforming furnace in which a re-former tube is located in the furnace and a plurality of radiant short flame burners are installed on both sides of the furnace are assembled to form one downward flow exhaust gas passage. In order from upstream to downstream, the downflow exhaust gas passage includes a steam superheater 6, a waste heat recovery boiler 7, a first process fluid preheater 8, a reducing agent spray device 11, and a second process fluid preheater 8, 350.
The third catalyst layer 10 contacts the exhaust gas at a temperature of ℃ to 400℃.
A steam reforming furnace characterized in that a process fluid preheater 8 and a feed water preheater 9 are located.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP55155188A JPS5778929A (en) | 1980-11-06 | 1980-11-06 | Denitrification of waste gas from steam reforming furnace |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP55155188A JPS5778929A (en) | 1980-11-06 | 1980-11-06 | Denitrification of waste gas from steam reforming furnace |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS5778929A JPS5778929A (en) | 1982-05-17 |
| JPH0131560B2 true JPH0131560B2 (en) | 1989-06-27 |
Family
ID=15600404
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP55155188A Granted JPS5778929A (en) | 1980-11-06 | 1980-11-06 | Denitrification of waste gas from steam reforming furnace |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS5778929A (en) |
Families Citing this family (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH05247471A (en) * | 1991-09-20 | 1993-09-24 | Mitsui Eng & Shipbuild Co Ltd | Ethylene cracker |
| CN108786666B (en) * | 2017-04-28 | 2021-12-10 | 中国石化工程建设有限公司 | Side burning converter |
| CN109425222A (en) * | 2017-08-22 | 2019-03-05 | 中国石化工程建设有限公司 | Burn reforming furnace in side |
Family Cites Families (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS531682A (en) * | 1976-06-28 | 1978-01-09 | Osaka Gas Co Ltd | Decreasing method of no# in combustion exhaust gas from hydrocarbon |
| JPS5364103A (en) * | 1976-09-24 | 1978-06-08 | Hitachi Ltd | Waste heat recovery boiler |
-
1980
- 1980-11-06 JP JP55155188A patent/JPS5778929A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS5778929A (en) | 1982-05-17 |
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