JPH01259088A - Steam reforming of hydrocarbon - Google Patents

Steam reforming of hydrocarbon

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Publication number
JPH01259088A
JPH01259088A JP63318818A JP31881888A JPH01259088A JP H01259088 A JPH01259088 A JP H01259088A JP 63318818 A JP63318818 A JP 63318818A JP 31881888 A JP31881888 A JP 31881888A JP H01259088 A JPH01259088 A JP H01259088A
Authority
JP
Japan
Prior art keywords
catalyst
steam reforming
sulfur
desulfurization
naphtha
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.)
Granted
Application number
JP63318818A
Other languages
Japanese (ja)
Other versions
JP2683531B2 (en
Inventor
Osamu Okada
治 岡田
Susumu Takami
晋 高見
Tamotsu Kotani
保 小谷
Michitsugu Mori
理嗣 森
Hiroki Fujita
弘樹 藤田
Naoko Fukumura
福村 尚子
Masamichi Ipponmatsu
正道 一本松
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.)
Osaka Gas Co Ltd
Original Assignee
Osaka Gas Co Ltd
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Priority to JP63318818A priority Critical patent/JP2683531B2/en
Publication of JPH01259088A publication Critical patent/JPH01259088A/en
Application granted granted Critical
Publication of JP2683531B2 publication Critical patent/JP2683531B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

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  • Catalysts (AREA)

Abstract

PURPOSE:To remarkably prolong the life of a catalyst and decrease the necessary amount of steam, by treating a hydrocarbon with a higher-order desulfurizing agent and carrying out steam reforming, thereby effectively preventing the sulfur-poisoning of the steam reforming catalyst and the deposition of carbon. CONSTITUTION:A hydrocarbon is desulfurized with a higher-order desulfurizing agent to a sulfur-content of <=5ppb (most preferably <=0.1ppb) and subjected to steam reforming. The higher-order desulfurizing agent can be produced, e.g., by preparing a mixture of copper oxide, zinc oxide and aluminum oxide prepared from a copper compound, a zinc compound and an aluminum compound by the coprecipitation process and reducing the resultant mixture with hydrogen.

Description

【発明の詳細な説明】 産業上の利用分野 本発明は、高度に脱硫した炭化水素の水蒸気改質方法に
関する。
DETAILED DESCRIPTION OF THE INVENTION Field of the Invention The present invention relates to a process for steam reforming of highly desulfurized hydrocarbons.

従来技術とその問題点 従来炭化水素を水蒸気改質するに先立ち行われている代
表的な脱硫方法は、Ni−Mo系またはCo−Mo系触
媒の存在下に炭化水素中の有機硫黄を水添分解した後、
生成するH2SをZnOに吸着させて、除去する方法で
ある。
Prior art and its problems A typical desulfurization method conventionally used prior to steam reforming of hydrocarbons involves hydrogenation of organic sulfur in hydrocarbons in the presence of a Ni-Mo or Co-Mo catalyst. After disassembling
This is a method of removing generated H2S by adsorbing it onto ZnO.

しかしながら、この様な従来方法には、多くの問題点が
ある。すなわち、水添脱硫工程において、炭化水素中に
一定量以上の有機硫黄、特にチオフエンなどの難分解性
の有機硫黄が含まれている場合には、未分解のものがス
リップして、ZnOに吸着されることなく、素通りする
。また、吸着脱硫に際しては、例えば、 Z n O+ H2S : Z n S + H20Z
nO+CO8:  ZnS+CO2 で示される平衡のため、H2S、CO8などの量も一定
値以下とはならない。特に、H2O及びCO2が存在す
る場合には、この傾向は、著しい。
However, such conventional methods have many problems. In other words, in the hydrodesulfurization process, if the hydrocarbon contains more than a certain amount of organic sulfur, especially difficult-to-decompose organic sulfur such as thiophene, undecomposed substances slip and are adsorbed onto ZnO. Pass by without being affected. In addition, for adsorption desulfurization, for example, Z n O + H2S: Z n S + H20Z
Due to the equilibrium represented by nO+CO8:ZnS+CO2, the amounts of H2S, CO8, etc. do not fall below a certain value. This tendency is particularly pronounced when H2O and CO2 are present.

さらに、装置のスタートアップ、シャットダウンなどに
際して脱硫系が不安定である場合には、水添脱硫装置及
び吸着脱硫触媒から硫黄が飛散して、精製物中の硫黄濃
度が増大することもある。したがって、現在の水蒸気改
質プロセスにおける脱硫工程は、精製後の炭化水素中の
硫黄濃度が数ppm乃至0.lppmとなる様なレベル
で管理せざるを得ない。
Furthermore, if the desulfurization system is unstable during startup or shutdown of the device, sulfur may be scattered from the hydrodesulfurization device and the adsorption desulfurization catalyst, increasing the sulfur concentration in the purified product. Therefore, in the desulfurization step in the current steam reforming process, the sulfur concentration in the refined hydrocarbons ranges from several ppm to 0.5 ppm. There is no choice but to manage it at a level such that it becomes lppm.

上記のようにして脱硫された炭化水素は、次いで、Ru
系、Ni系などの触媒の存在下に水蒸気改質に供される
。しかるに、マカーティら(McCarty at a
l  ; J、Chem、Phys、 vol 72.
No、12゜6332.1980: J、Chem、P
hys、 vol 74.No、lO,5877,19
81)の研究が明らかにしている様に、Ni及びRuの
硫黄吸着力は、強力であるので、炭化水素中の硫黄含有
回が極微全てあっても、触媒表面の大部分は、硫黄によ
り覆われる。具体的には、−般の水蒸気改質プロセスの
入口条件(450℃近傍)において、現在の最善のレベ
ルである硫黄含有ff10.lppm程度の状態では、
NiまたはRU触媒の表面の約90%が、硫黄により、
短時間内に覆われてしまう。このことは、現行の炭化水
素の脱硫レベルでは、水蒸気改質工程における触媒の硫
黄被毒を防止することが出来ないことを意味している。
The hydrocarbons desulfurized as described above are then treated with Ru
It is subjected to steam reforming in the presence of a catalyst such as Ni-based or Ni-based catalyst. However, McCarty at a
l ; J, Chem, Phys, vol 72.
No. 12゜6332.1980: J, Chem, P
hys, vol 74. No, IO, 5877, 19
81), the sulfur adsorption power of Ni and Ru is strong, so even if the amount of sulfur contained in the hydrocarbon is extremely small, most of the catalyst surface will be covered with sulfur. be exposed. Specifically, under the inlet conditions of a typical steam reforming process (near 450°C), the current best level of sulfur content ff10. At about lppm,
Approximately 90% of the surface of Ni or RU catalyst is covered by sulfur.
It will be covered within a short time. This means that current hydrocarbon desulfurization levels cannot prevent sulfur poisoning of the catalyst in the steam reforming process.

この様な問題点を考慮して、特開昭62−17003号
公報には、0.5ppm以下に脱硫した炭化水素を使用
する水蒸気改質方法が提案されている。しかしながら、
ここに記載されている方法では、炭化水素の脱硫度が不
十分で、水蒸気改質触媒の被毒を十分に防止することが
出来ず、また後述するように水蒸気使用量の低減も実現
されない。
In consideration of such problems, Japanese Patent Laid-Open No. 17003/1983 proposes a steam reforming method using hydrocarbons desulfurized to 0.5 ppm or less. however,
In the method described herein, the degree of desulfurization of hydrocarbons is insufficient, it is not possible to sufficiently prevent poisoning of the steam reforming catalyst, and, as will be described later, it is not possible to reduce the amount of steam used.

問題点を解決する為の手段 本発明者は、上記の如き技術の現状に鑑みて鋭意研究を
重ねた結果、水蒸気改質に供される炭化水素中の硫黄含
有足を5ppb以下、より好ましくは1ppb以下、更
に好ましくはO,1ppb以下という低いレベルとする
場合には、水蒸気改質触媒の硫黄被毒を実質的に防止し
得るのみならず、触媒への炭素の析出をも防止し得るこ
とを見出した。
Means for Solving the Problems As a result of extensive research in view of the current state of the technology as described above, the inventor of the present invention has determined that the sulfur content in the hydrocarbons subjected to steam reforming should be reduced to 5 ppb or less, more preferably. When the level is set to a low level of 1 ppb or less, more preferably 1 ppb or less, it is possible not only to substantially prevent sulfur poisoning of the steam reforming catalyst but also to prevent carbon precipitation on the catalyst. I found out.

すなわち、本発明は、炭化水素を高次脱硫剤により硫黄
含有ff15 ppb以下に脱硫した後、水蒸気改質を
行うことを特徴とする炭化水素の水蒸気改質方法に係る
That is, the present invention relates to a method for steam reforming hydrocarbons, which comprises desulfurizing the hydrocarbons to a sulfur content of ff15 ppb or less using a high-order desulfurization agent, and then steam reforming the hydrocarbons.

従来から、硫黄被毒が、水蒸気改質用触媒の主な劣化要
因であることは、良く知られている。しかるに、水蒸気
改質に供される炭化水素中の硫黄含量を5ppb以下、
より好ましくは1ppb以下、さらに好ましくはO,1
ppb以下とすることにより、硫黄被毒のみならず、炭
素の析出までもが防止されるということは、従来まった
く予期し得なかった新しい知見である。したがって、本
発明方法によれば、炭化水素の水蒸気改質において、触
媒への炭素析出による活性劣化、反応器閉塞等が制約と
なって採用出来なかった低水蒸気比運転や低水素比運転
及び灯軽油留分等の重質な炭化水素原料を使用する運転
が可能となる。この結果、水蒸気改質プロセスの経済性
は、大巾に改善される。
It has been well known that sulfur poisoning is the main cause of deterioration of steam reforming catalysts. However, if the sulfur content in the hydrocarbons subjected to steam reforming is 5 ppb or less,
More preferably 1 ppb or less, even more preferably O,1
The fact that not only sulfur poisoning but also carbon precipitation can be prevented by reducing the amount to ppb or less is a new finding that could not have been predicted in the past. Therefore, according to the method of the present invention, in the steam reforming of hydrocarbons, low steam ratio operation, low hydrogen ratio operation, and light It becomes possible to operate using heavy hydrocarbon raw materials such as light oil fractions. As a result, the economics of the steam reforming process is greatly improved.

以下図面に示すフローチャートを参照しつつ、本発明を
さらに詳細に説明する。
The present invention will be described in more detail below with reference to the flowcharts shown in the drawings.

第1図は、全硫黄化合物含有量が10ppm以下(硫黄
として:以下向じ)である炭化水素を原料とする本発明
方法の一実施態様を示す。この場合には、原料は、硫黄
含有量を5ppb以下、より好ましくは1ppb以下更
に好ましくは0.1ppb以下にまで減少させる為の脱
硫工程に供される(以下これを高次脱硫という)。この
様な高次脱硫を行う手段としては、炭化水素中の硫黄含
有量を5ppb以下、好ましくは1ppb以下、より好
ましくは0.1ppb以下とすることができる限り、特
に限定されるものではなく、例えば、銅系脱硫剤、銀糸
脱硫剤、ルテニウム系脱硫剤、ニッケル系脱硫剤、活性
炭などに吸着させる方法を採用することができる。より
好ましくは、特願昭62−279867号及び特願昭6
2−279868号に開示された銅−亜鉛系および銅−
亜鉛−アルミニウム系脱硫剤を使用する脱硫方法が挙げ
られる。この様な脱硫剤は、下記に示す様な方法により
、調製される。
FIG. 1 shows an embodiment of the method of the present invention using a hydrocarbon having a total sulfur compound content of 10 ppm or less (as sulfur: hereinafter referred to) as a raw material. In this case, the raw material is subjected to a desulfurization step to reduce the sulfur content to 5 ppb or less, more preferably 1 ppb or less, and even more preferably 0.1 ppb or less (hereinafter referred to as higher desulfurization). The means for performing such high-order desulfurization is not particularly limited as long as it can reduce the sulfur content in the hydrocarbon to 5 ppb or less, preferably 1 ppb or less, more preferably 0.1 ppb or less, For example, a method of adsorption to a copper-based desulfurization agent, a silver thread desulfurization agent, a ruthenium-based desulfurization agent, a nickel-based desulfurization agent, activated carbon, etc. can be adopted. More preferably, Japanese Patent Application No. 62-279867 and Japanese Patent Application No. 6
Copper-zinc-based and copper disclosed in No. 2-279868
A desulfurization method using a zinc-aluminum desulfurization agent is mentioned. Such a desulfurizing agent is prepared by the method shown below.

(1)銅−亜鉛系脱硫剤 銅化合物(例えば、硝酸銅、酢酸銅等)及び亜鉛化合物
(例えば、硝酸亜鉛、酢酸亜鉛等)を含む水溶液とアル
カリ物質(例えば、炭酸ナトリウム、炭酸カリウム等)
の水溶液を使用して、常法による共沈法により沈澱を生
じさせる。生成した沈澱を乾燥し、300℃程度で焼成
して、酸化銅−酸化亜鉛混合物(原子比で通常鋼−亜鉛
=1:約03〜10、好ましくは1:約0.5〜3、よ
り好ましくは1:約1〜2.3)を得た後、水素含有量
6容量%以下、より好ましくは0.5〜4容量%程度と
なる様に不活性ガス(例えば、窒素ガス等)により希釈
された水素ガスの存在下に150〜300℃程度で上記
混合物を還元処理する。この様にして得られる銅−亜鉛
系脱硫剤には、他の担体成分としである種の金属酸化物
、例えば、酸化クロムなどを含有させても良い。
(1) Copper-zinc desulfurization agent Aqueous solution containing copper compounds (e.g., copper nitrate, copper acetate, etc.) and zinc compounds (e.g., zinc nitrate, zinc acetate, etc.) and alkaline substances (e.g., sodium carbonate, potassium carbonate, etc.)
A precipitate is produced by a conventional coprecipitation method using an aqueous solution of. The generated precipitate is dried and calcined at about 300°C to form a copper oxide-zinc oxide mixture (in atomic ratio normal steel-zinc = 1: about 03-10, preferably 1: about 0.5-3, more preferably 1: about 1 to 2.3), diluted with an inert gas (e.g., nitrogen gas, etc.) so that the hydrogen content is 6% by volume or less, more preferably about 0.5 to 4% by volume. The above mixture is subjected to a reduction treatment at about 150 to 300°C in the presence of hydrogen gas. The copper-zinc desulfurization agent obtained in this manner may contain certain metal oxides, such as chromium oxide, as other carrier components.

(2)銅−亜鉛−アルミニウム系脱硫剤銅化合物(例え
ば、硝酸銅、酢酸銅等)、亜鉛化合物(例えば、硝酸亜
鉛、酢酸亜鉛等)及びアルミニウム化合物(例えば、硝
酸アルミニウム、アルミン酸ナトリウム等)を含む水溶
液とアルカリ物質(例えば、炭酸ナトリウム、炭酸カリ
ウム等)の水溶液を使用して、常法による共沈法により
、沈澱を生じさせる。生成した沈澱を乾燥し、約300
℃で焼成して、酸化銅−酸化亜鉛−酸化アルミニウム混
合物(原子比で通常鋼:亜鉛ニアルミニウム=1:約0
.3〜10:約0.05〜2、より好ましくは1:約0
.6〜3:約0.3〜1)を得た後、水素含有量6容量
%以下、より好ましくは0.5〜4容量%程度となる様
に不活性ガスにより希釈された水素ガスの存在下に15
0〜300℃程度で上記混合物を還元処理する。この様
にして得られる銅−亜鉛−アルミニウム系脱硫剤には、
他の担体成分としである種の金属酸化物、例えば、酸化
クロムなどを含有させても良い。
(2) Copper-zinc-aluminum desulfurization agent Copper compounds (e.g., copper nitrate, copper acetate, etc.), zinc compounds (e.g., zinc nitrate, zinc acetate, etc.), and aluminum compounds (e.g., aluminum nitrate, sodium aluminate, etc.) and an aqueous solution of an alkaline substance (eg, sodium carbonate, potassium carbonate, etc.) to form a precipitate by a conventional coprecipitation method. The formed precipitate was dried and
It is fired at ℃ to form a copper oxide-zinc oxide-aluminum oxide mixture (at an atomic ratio of normal steel:zinc nialium=1:approximately 0).
.. 3-10: about 0.05-2, more preferably 1: about 0
.. 6-3: After obtaining about 0.3-1), the presence of hydrogen gas diluted with an inert gas so that the hydrogen content is 6% by volume or less, more preferably about 0.5-4% by volume. 15 below
The above mixture is subjected to a reduction treatment at about 0 to 300°C. The copper-zinc-aluminum desulfurization agent obtained in this way has
Certain metal oxides, such as chromium oxide, may also be included as other carrier components.

上記(1)及び(2)の方法で得られる銅系脱硫剤は、
大きな表面積を有する微粒子状の銅が、酸化亜鉛(及び
酸化アルミニウム)中に均一に分散しているとともに、
酸化亜鉛(及び酸化アルミニウム)との化学的な相互作
用により高活性状態になっている。従って、これらの脱
硫剤を使用する場合には、炭化水素中の硫黄含有量を確
実に5ppb以下、適切な条件を選択すれば1ppb以
下、さらに最適条件下には容易にO,1ppb以下とす
ることができ、またチオフェン等の難分解性の硫黄化合
物をも確実に除去することができる。
The copper-based desulfurization agent obtained by the methods (1) and (2) above is
Fine-particle copper with a large surface area is uniformly dispersed in zinc oxide (and aluminum oxide), and
It becomes highly active due to chemical interaction with zinc oxide (and aluminum oxide). Therefore, when using these desulfurization agents, the sulfur content in hydrocarbons can be ensured to be 5 ppb or less, if appropriate conditions are selected, 1 ppb or less, and under optimal conditions it can be easily reduced to 0.1 ppb or less. It is also possible to reliably remove refractory sulfur compounds such as thiophene.

特に、銅−亜鉛−アルミニウム系脱硫剤にあっては、酸
化アルミニウムの作用により、耐熱性に優れ、高温での
強度低下及び硫黄吸着力の低下を著るしく減少させるこ
とができるという利点が得られる。
In particular, copper-zinc-aluminum desulfurization agents have the advantage that they have excellent heat resistance due to the action of aluminum oxide, and can significantly reduce the decrease in strength and sulfur adsorption capacity at high temperatures. It will be done.

上記の銅系脱硫剤を用いる高次脱硫は、通常温度200
〜400℃程度、圧力1〜50kg/cTl・G程度、
GH8V100O〜5000程度の条件下に行なわれる
High-order desulfurization using the above copper-based desulfurization agent is usually carried out at a temperature of 200
~400℃, pressure 1~50kg/cTl・G,
It is carried out under conditions of about GH8V1000 to 5000.

第2図は、全硫黄化合物含有量が10ppm以上である
が、難分解性の有機硫黄化合物含有量が10ppm未満
である炭化水素を原料とする本発明方法の一実施態様を
示す。この場合には、まず、原料炭化水素を例えばZn
O系脱硫剤を使用する常法による一次吸着脱硫に供する
。この際の条件は、特に限定されるものではないが、後
続の高次脱硫工程での硫黄化合物吸着効果を最大限に発
揮させるために、炭化水素中の硫黄含有量を1〜0、l
ppm程度に低下させておくことが望ましい。従って、
−次吸着脱硫においては、ZnO系脱硫剤の存在下温度
250℃〜400℃程度、圧力10kg/cシ・G程度
、GH8V100O程度の条件を採用することが好まし
いが、その他の条件を採用することも、当然可能である
。次いで、−次吸着脱硫を終えた炭化水素を上記と同様
の高次脱硫工程に送り、硫黄含有量を5ppb以下、好
ましくは1ppb以下、より好ましくは0.1ppb以
下とした後、常法による水蒸気改質を行う。
FIG. 2 shows an embodiment of the method of the present invention using a hydrocarbon as a raw material having a total sulfur compound content of 10 ppm or more but a refractory organic sulfur compound content of less than 10 ppm. In this case, first, the raw material hydrocarbon is
It is subjected to primary adsorption desulfurization using a conventional method using an O-based desulfurization agent. The conditions at this time are not particularly limited, but in order to maximize the sulfur compound adsorption effect in the subsequent high-level desulfurization step, the sulfur content in the hydrocarbon is 1 to 0, 1.
It is desirable to reduce the amount to about ppm. Therefore,
- In the second adsorption desulfurization, it is preferable to adopt conditions such as temperature of about 250 to 400 degrees Celsius, pressure of about 10 kg/c/g, and GH of about 8V100O in the presence of a ZnO-based desulfurization agent, but other conditions may also be adopted. Of course, it is also possible. Next, the hydrocarbons that have undergone the -order adsorption desulfurization are sent to the same higher order desulfurization step as described above to reduce the sulfur content to 5 ppb or less, preferably 1 ppb or less, more preferably 0.1 ppb or less, and then steamed by a conventional method. Perform modification.

第3図は、難分解性の有機硫黄化合物を主とする全硫黄
化合物の含有量が10ppm以上である炭化水素を原料
とする本発明方法の一実施態様を示す。この場合には、
まず、原料炭化水素は、常法に従って、例えば、Ni−
Mo系、Co−M。
FIG. 3 shows an embodiment of the method of the present invention in which the raw material is a hydrocarbon containing 10 ppm or more of total sulfur compounds, mainly organic sulfur compounds that are difficult to decompose. In this case,
First, the raw material hydrocarbon is prepared using a conventional method such as Ni-
Mo-based, Co-M.

系等の触媒の存在下温度350〜400℃程度、圧力1
0kg/cJ e G程度、GH3V3000程度の条
件下に水添脱硫される。次に、第2図に関連して述べた
と同様の一次吸着脱硫を行った後、高次脱硫を行い、炭
化水素中の硫黄含有量を5ppb以下、好ましくは1p
pb以下、より好ましくはO,1ppb以下とする。こ
の際、吸着脱硫処理された炭化水素は高温となっている
ので、耐熱性に優れた銅−亜鉛−アルミニウム系脱硫剤
を使用して、高次脱硫を行うことが好ましい。高次脱硫
された炭化水素は、常法による水蒸気改質に供される。
In the presence of a catalyst such as a system, the temperature is about 350 to 400℃, the pressure is 1
Hydrodesulfurization is performed under conditions of about 0 kg/cJ e G and about GH3V3000. Next, after primary adsorption desulfurization similar to that described in connection with FIG.
pb or less, more preferably O,1 ppb or less. At this time, since the hydrocarbons subjected to adsorption and desulfurization treatment are at a high temperature, it is preferable to perform high-order desulfurization using a copper-zinc-aluminum desulfurization agent having excellent heat resistance. The hydrocarbons subjected to high-order desulfurization are subjected to steam reforming using a conventional method.

本発明において原料として使用する炭化水素としては、
天然ガス、エタン、プロパン、ブタン、LPG (液化
石油ガス)、ライトナフサ、ヘビーナフサ、軽灯油、コ
ークス炉ガス、各種の都市ガス等が例示される。
Hydrocarbons used as raw materials in the present invention include:
Examples include natural gas, ethane, propane, butane, LPG (liquefied petroleum gas), light naphtha, heavy naphtha, light kerosene, coke oven gas, and various city gases.

発明の効果 本発明によれば、水蒸気改質触媒の硫黄被毒及び該触媒
に対する炭素の析出が極めて効果的に防止されるので、
触媒寿命が大巾に延長される。また、必要水蒸気量を減
少させることができる。即ち、従来の水蒸気改質方法で
は、長時間の運転を行うためには、S/C(炭化水素中
の炭素1モル当りの水蒸気のモル数)を3.5以上とす
る必要があったが、本発明方法によれば、S/Cが0.
7〜3.5でも、長時間安定に運転することができる。
Effects of the Invention According to the present invention, sulfur poisoning of the steam reforming catalyst and carbon deposition on the catalyst are extremely effectively prevented.
Catalyst life is greatly extended. Moreover, the required amount of water vapor can be reduced. That is, in conventional steam reforming methods, in order to operate for a long time, it was necessary to increase the S/C (number of moles of steam per mole of carbon in hydrocarbons) to 3.5 or more. , according to the method of the present invention, S/C is 0.
7 to 3.5, it is possible to operate stably for a long time.

実施例 以下参考例、実施例及び比較例を示し、本発明の特徴と
するところをより一層明らかにする。
EXAMPLES Below, reference examples, working examples, and comparative examples will be shown to further clarify the characteristics of the present invention.

参考例 現在の測定技術では、炭化水素の様な可燃性物質中に含
まれるppbオーダーの硫黄を直接的に測定することは
、困難である。従って、本明細書において、炭化水素中
のppbオーダーの硫黄含有量の測定は、下記の方法に
基いて計算した値である。
Reference Example With current measurement techniques, it is difficult to directly measure ppb-order sulfur contained in combustible substances such as hydrocarbons. Therefore, in this specification, the measurement of ppb-order sulfur content in hydrocarbons is a value calculated based on the following method.

常法により予備精製されたコークス炉ガスを特願昭62
−279868号に開示された銅−亜鉛−アルミニウム
系脱硫剤を用いて高次脱硫した。
A patent application was made in 1982 for coke oven gas pre-purified by conventional methods.
High-order desulfurization was carried out using the copper-zinc-aluminum desulfurization agent disclosed in No. 279868.

得られた高次脱硫コークス炉ガスを500ONi/hr
にて、2 w t 1%Ru/A Q 203触媒3.
5t(かさ密度0.8kg/R)を充填した改質反応器
(内径160cmφ)に導入し、入口温度300℃で1
6000時間改質反応を行なった。
The obtained high-order desulfurization coke oven gas was heated at 500ONi/hr.
2 wt 1% Ru/A Q 203 catalyst 3.
5 tons (bulk density 0.8 kg/R) was introduced into a reforming reactor (inner diameter 160 cmφ), and at an inlet temperature of 300°C.
The reforming reaction was carried out for 6000 hours.

使用した触媒の飽和被毒量は、 約0.002g−8/g−触媒である。The saturated poisoning amount of the catalyst used is Approximately 0.002 g-8/g-catalyst.

ルテニウムは極めて硫黄吸着能力が高く、気相に伜かな
濃度の硫黄が存在すると直ちに吸着する。
Ruthenium has an extremely high sulfur adsorption capacity, and if a high concentration of sulfur is present in the gas phase, it will adsorb it immediately.

従って、硫黄は触媒層の表面の極く薄い層(表層から1
0cmまでの深さ)に吸着されているものと考えられる
Therefore, sulfur is present in a very thin layer on the surface of the catalyst layer (one layer from the surface layer).
It is thought that the particles are adsorbed at a depth of up to 0 cm.

そこで、上記の反応の終了後、触媒層の表面から10c
mまでの周部について螢光X線分析法により硫黄を分析
した。その結果、螢光X線分析法による硫黄の検出限界
(0,00005g−8/g−触媒)以下であった。従
って、高次脱硫した原料ガス中に含まれる硫黄含有合は
、下記式により算出され、O,1ppb以下であること
が判明した。
Therefore, after the completion of the above reaction, 10 cm from the surface of the catalyst layer
Sulfur was analyzed by fluorescent X-ray analysis on the circumference up to m. The result was below the detection limit of sulfur (0,00005 g-8/g-catalyst) by fluorescent X-ray analysis. Therefore, the sulfur content contained in the highly desulfurized raw material gas was calculated using the following formula, and was found to be 0.1 ppb or less.

コークス炉ガス以外のLPG、ナフサなどを使用する場
合についても、同様の手法に従って硫黄含有mの計算を
行なった。
In the case of using LPG, naphtha, etc. other than coke oven gas, the sulfur content m was calculated using the same method.

実施例1 硫黄含有m 100 p p mのナフサを、常法にし
たがって、まずNi−Mo系水添脱硫触媒の存在下に温
度380℃、圧力10kg/cJ * cy。
Example 1 Naphtha containing 100 ppm of sulfur was first heated at 380° C. and at a pressure of 10 kg/cJ*cy in the presence of a Ni-Mo hydrodesulfurization catalyst according to a conventional method.

LH8V2、水素/ナフサ−0,1(モル比)の条件下
に水添分解した後、ZnO系吸着脱硫剤に接触させて、
−次吸着脱硫した。得られた一次吸着脱硫ナフサ中の硫
黄濃度は、約2ppmであった。
After hydrogenolysis under the conditions of LH8V2, hydrogen/naphtha-0.1 (molar ratio), contact with a ZnO-based adsorption desulfurization agent,
-Next adsorption desulfurization. The sulfur concentration in the obtained primary adsorption desulfurization naphtha was about 2 ppm.

一方、硝酸銅、硝酸亜鉛及び硝酸アルミニウムを溶解す
る混合水溶液にアルカリ物質として炭酸ナトリウムを加
え、生じた沈澱を洗浄及び濾過した後、高さ1/8イン
チX直径1/8インチの大きさに打錠成形し、約400
℃で焼成した。次いで、該焼成体(酸化銅45%、酸化
亜鉛45%、酸化アルミニウム10%)100ccを充
填した脱硫装置に水素2%を含む窒素ガスを流通させ、
温度的200℃で還元した後、上記で得た一次吸着脱硫
ナフサ400 Q / h rを通じ、温度350°C
1圧力8kg/cJ−Gの条件下に高次脱硫した。
On the other hand, sodium carbonate was added as an alkaline substance to a mixed aqueous solution in which copper nitrate, zinc nitrate, and aluminum nitrate were dissolved, and the resulting precipitate was washed and filtered. Molded into tablets, approximately 400
Calcined at ℃. Next, nitrogen gas containing 2% hydrogen was passed through a desulfurizer filled with 100 cc of the fired body (45% copper oxide, 45% zinc oxide, 10% aluminum oxide),
After reduction at a temperature of 200°C, the above obtained primary adsorption desulfurization naphtha was passed through 400 Q/hr at a temperature of 350°C.
High-order desulfurization was carried out under the condition of 1 pressure of 8 kg/cJ-G.

得られた高次脱硫ナフサ中の硫黄濃度は、7000時間
の運転にわたり、平均0.1ppb以下であった。
The sulfur concentration in the obtained high-order desulfurization naphtha was 0.1 ppb or less on average over 7000 hours of operation.

次いで、得られた高次脱硫ナフサを原料とし、流通式疑
似断熱型の反応器(直径20mm)を使用して、ルテニ
ウム触媒(γ−アルミナ担体にルテニウム2重量%を担
持)の存在下に第1表に示す条件で低温水蒸気改質を行
ない、メタンを製造した。
Next, using the obtained high-order desulfurized naphtha as a raw material, a flow-through pseudo-adiabatic reactor (diameter 20 mm) was used to conduct a second reaction in the presence of a ruthenium catalyst (ruthenium 2% by weight supported on a γ-alumina carrier). Methane was produced by performing low temperature steam reforming under the conditions shown in Table 1.

第1表 反応温度(入口)    490°C(断熱)反応圧力
        8 kg / cシ・Gナフサ流量 
      160 c c / h r触媒量   
      100cc S/C1,7 H2/ナフサ      0.1(モル比)第4図に結
果を示す。第4図において、曲線A−1は、反応開始直
後の反応器内触媒層の温度プロフィールを示し、曲線A
−2は、反応開始400時間後の反応器内触媒層の温度
プロフィールを示す。
Table 1 Reaction temperature (inlet) 490°C (adiabatic) Reaction pressure 8 kg/c C/G naphtha flow rate
160cc/hr catalyst amount
100cc S/C1,7 H2/naphtha 0.1 (molar ratio) The results are shown in FIG. In FIG. 4, curve A-1 shows the temperature profile of the catalyst layer in the reactor immediately after the start of the reaction;
-2 shows the temperature profile of the catalyst layer in the reactor 400 hours after the start of the reaction.

本発明方法によれば、400時間経過後にも、改質触媒
が十分に高い活性を維持し続けているので、反応開始直
後と同様に、触媒層の入口で吸熱反応であるナフサの分
解が起きて温度が下がり、引き続いて起こる発熱反応で
あるメタン化反応、CO変性反応等により、温度が上昇
している。
According to the method of the present invention, even after 400 hours have passed, the reforming catalyst continues to maintain a sufficiently high activity, so that naphtha decomposition, which is an endothermic reaction, occurs at the inlet of the catalyst bed, just as it did immediately after the start of the reaction. The temperature then decreases, and the temperature rises due to subsequent exothermic reactions such as methanation and CO modification reactions.

この様な改質触媒の高活性状態は、400時間経過後の
触媒上の各位置における炭素析出量(反□  応益入口
においてのみ0.4重世%以下)及び硫黄析出量(反応
器入口においても螢光X線分析の検出限界以下)によっ
ても裏付けられている。従って、本発明によれば、炭素
析出防止の為の大量の水素又は水蒸気を必要とせず、改
質触媒の消耗曾が大巾に低下し、必要触媒口も減少して
反応器の小形化が可能となる。
Such a highly active state of the reforming catalyst is due to the amount of carbon deposited at each location on the catalyst after 400 hours (0.4% or less only at the reactor inlet) and the amount of sulfur deposited (at the reactor inlet). This is also supported by the detection limit of fluorescent X-ray analysis). Therefore, according to the present invention, there is no need for large amounts of hydrogen or steam to prevent carbon deposition, the consumption rate of the reforming catalyst is greatly reduced, the number of required catalyst ports is reduced, and the size of the reactor can be reduced. It becomes possible.

比較例1 硫黄含有ffi 100 p p mのナフサを、常法
にしたがって、まずNi−Mo系水添脱硫触媒の存在下
に温度380℃、圧力10kg/cシ・G、LH8V 
 2、水素/ナフサ=0. 1 (モル比)の条件下に
水添分解した後、ZnO系吸着脱硫剤に接触させて、−
次吸着脱硫した。得られた一次脱硫ナフサ中の硫黄濃度
は、約2ppmであった。
Comparative Example 1 Sulfur-containing naphtha with an ffi of 100 ppm was first heated in the presence of a Ni-Mo hydrodesulfurization catalyst at a temperature of 380°C and a pressure of 10 kg/c, LH8V, according to a conventional method.
2. Hydrogen/naphtha = 0. After hydrogenolysis under the conditions of 1 (molar ratio), it is brought into contact with a ZnO-based adsorption desulfurization agent, and -
Next, adsorption desulfurization was performed. The sulfur concentration in the obtained primary desulfurized naphtha was about 2 ppm.

かくして得た一次脱硫ナフサを実施例1と同様にして、
水蒸気改質に供した。
The thus obtained primary desulfurized naphtha was treated in the same manner as in Example 1,
It was subjected to steam reforming.

結果は、第5図に示す通りである。第5図において、曲
線B−1は、反応開始直後の反応器内触媒層の温度プロ
フィールを示し、曲線B−2は、反応開始200時間後
の反応器内触媒層の温度プロフィールを示す。
The results are shown in FIG. In FIG. 5, curve B-1 shows the temperature profile of the catalyst layer in the reactor immediately after the start of the reaction, and curve B-2 shows the temperature profile of the catalyst layer in the reactor 200 hours after the start of the reaction.

曲線B−1から明らかな様に、反応開始直後には、改質
触媒が十分に活性を有しているので、触媒層の入口で吸
熱反応であるナフサの分解が起きて温度が下がり、その
後引き続いて起こる発熱反応であるメタン化反応、CO
変性反応等により温度は上昇している。
As is clear from curve B-1, immediately after the start of the reaction, the reforming catalyst is sufficiently active, so an endothermic reaction of naphtha decomposition occurs at the inlet of the catalyst bed, the temperature decreases, and then The subsequent exothermic methanation reaction, CO
The temperature is rising due to denaturation reactions, etc.

これに対し、曲線B−2から明らかな様に、200時間
経過後には、改質触媒はほぼ完全に失活しており、吸熱
反応及び発熱反応による触媒層の温度変化も認められず
、−次脱硫ナフサが未反応のまま改質反応器から出てく
る。
On the other hand, as is clear from curve B-2, after 200 hours, the reforming catalyst is almost completely deactivated, and no temperature change in the catalyst layer due to endothermic or exothermic reactions is observed. Next, the desulfurized naphtha comes out of the reforming reactor unreacted.

この様な改質触媒の失活状態は、200時間経過後の触
媒上の各位置における炭素析出量(触媒重量に対する%
)を示す曲線B−3及d硫黄析出量(触媒重量に対する
%)を示す曲線B−4によっても裏付けられている。
Such a deactivated state of the reforming catalyst is determined by the amount of carbon deposited at each position on the catalyst (% of the catalyst weight) after 200 hours.
) and curve B-4 showing the amount of sulfur deposited (in % of the catalyst weight).

この様な大量の炭素析出は、触媒の細孔を閉塞して、触
媒活性低下の原因となるのみならず、触媒の粉化延いて
は反応器の閉塞、差圧の増大の原因ともなる。従って、
これらは、長時間の運転を行うためには、極力防止すべ
き事項であり、一般に大量の水蒸気又は水素を使用して
その防止を図っている。
Such a large amount of carbon deposits not only blocks the pores of the catalyst and causes a decrease in catalyst activity, but also causes powdering of the catalyst, which in turn causes blockage of the reactor and an increase in differential pressure. Therefore,
These are matters that should be prevented as much as possible in order to operate for a long time, and they are generally prevented by using a large amount of steam or hydrogen.

実施例2 実施例1で使用したものと同様の水蒸気改質触媒を予め
硫黄被毒させ又はさせることなく、実施例1と同様の水
蒸気改質に使用した。夫々の触媒の詳細は、以下の通り
である。
Example 2 A steam reforming catalyst similar to that used in Example 1 was used for steam reforming in the same manner as in Example 1, with or without prior sulfur poisoning. Details of each catalyst are as follows.

触媒I・・・硫黄被毒なし 触媒■・・・硫黄付着量0.05重量%触媒■・・・硫
黄付着量0.2重量% 結果を第6図に示す。触媒Iを使用する場合には、30
0時間経過後にも、炭素の析出はほとんど認められなか
ったのに対し、触媒■及び触媒■の場合には、多量の炭
素が析出した。このことは、少量の硫黄の触媒への付着
が炭素析出を促進することを明らかにしている。従って
、炭化水素の高次の脱硫を行った後、水蒸気改質を行う
本発明は、触媒への炭素析出を効果的に防止し、以て改
質触媒の寿命延長に大きく貢献するものである。
Catalyst I: Catalyst without sulfur poisoning ■: Sulfur deposition amount: 0.05% by weight Catalyst ■: Sulfur deposition amount: 0.2% by weight The results are shown in FIG. When using catalyst I, 30
Even after 0 hours had elapsed, almost no carbon precipitation was observed, whereas in the case of catalysts (1) and (2), a large amount of carbon was deposited. This reveals that the attachment of small amounts of sulfur to the catalyst promotes carbon deposition. Therefore, the present invention, which performs steam reforming after high-level desulfurization of hydrocarbons, effectively prevents carbon deposition on the catalyst, thereby greatly contributing to extending the life of the reforming catalyst. .

実施例3 実施例1と同様にして高次脱硫吸着を行なったナフサを
原料として使用し、S/Cを種々変える以外は実施例1
と同様にして、水蒸気改質を行なった。反応器入口部に
おけるRu系触媒上の炭素析出量とS/Cとの関係を第
7図に曲線Cとして示す。
Example 3 Example 1 except that naphtha subjected to high-order desulfurization and adsorption in the same manner as Example 1 was used as a raw material, and the S/C was variously changed.
Steam reforming was carried out in the same manner as above. The relationship between the amount of carbon deposited on the Ru-based catalyst at the inlet of the reactor and S/C is shown as curve C in FIG.

第7図から明らかなごとく、高次脱硫を終えたナフサを
原料とする場合には、S/Cを0.7程度にまで低下さ
せても、触媒上への炭素析出は実質的に生じない。
As is clear from Figure 7, when naphtha that has undergone high-level desulfurization is used as a raw material, carbon deposition on the catalyst does not substantially occur even if the S/C is reduced to about 0.7. .

これに対し、比較例1と同様にして得た一次脱硫ナフサ
を原料として同一条件により水蒸気改質を行う場合には
、上記と同様の炭素析出防止効果を達成するために、運
転初期においてもS/Cを1.5以上とする必要があり
、さらに長期間安定して運転を行うためには、S/Cを
2.5以上とする必要があった。
On the other hand, when steam reforming is performed under the same conditions using the primary desulfurized naphtha obtained in the same manner as in Comparative Example 1, in order to achieve the same carbon precipitation prevention effect as above, S /C was required to be 1.5 or more, and in order to operate stably for a long period of time, S/C was required to be 2.5 or more.

実施例4 水蒸気改質用の触媒として最も一般的なNi系触媒(共
沈法により製造、NLO濃度50重足%)を使用する以
外は、実施例3と同様にして精製ナフサの水蒸気改質を
行った。反応器入口部におけるNi系触媒上の炭素析出
曾とS/Cとの関係を第7図に曲線りとして示す。
Example 4 Steam reforming of purified naphtha was carried out in the same manner as in Example 3, except that a Ni-based catalyst (manufactured by coprecipitation method, NLO concentration 50% by weight), which is the most common catalyst for steam reforming, was used. I did it. The relationship between the amount of carbon deposited on the Ni-based catalyst at the inlet of the reactor and S/C is shown as a curve in FIG.

炭素析出を安定して抑制するに必要なS/C=1.5と
いう値は、高活性のRu系触媒を使用する場合に比べれ
ば、高い。しかしながら、比較例1と同様にして得られ
た一次吸着脱硫ナフサを原料として使用する場合に必要
とされるS/C=2以上(運転初期)に比べれば、かな
り低く、更に長期間安定して運転するために必要なS/
C=3.5以上に比べると、かなり低い。
The value of S/C=1.5 required to stably suppress carbon deposition is higher than when using a highly active Ru-based catalyst. However, compared to S/C=2 or more (at the beginning of operation) required when using the primary adsorption desulfurization naphtha obtained in the same manner as Comparative Example 1 as a raw material, it is considerably lower and stable for a longer period of time. S/ necessary for driving
This is considerably lower than C=3.5 or higher.

実施例5 実施例1と同様にして得られた高次脱硫精製ナフサと比
較例1と同様にして得られた一次脱硫精製ナフサとを夫
々原料とし、且つ実施例1と同様なRu系触媒を充填し
た外熱式反応器(管径1.5インチ)を使用して、第2
表に示す条件下にナフサの高温水蒸気改質を行った。
Example 5 High-order desulfurized purified naphtha obtained in the same manner as in Example 1 and primary desulfurized purified naphtha obtained in the same manner as in Comparative Example 1 were used as raw materials, and the same Ru-based catalyst as in Example 1 was used as raw materials. Using a packed externally heated reactor (tube diameter 1.5 inch),
High-temperature steam reforming of naphtha was carried out under the conditions shown in the table.

2ppmの硫黄を含む一次脱硫精製ナフサを原料とする
場合には、200時間後に触媒の活性が失われて、はと
んど全9のナフサが未反応のまま反応器外に出てきたの
みならず、触媒層内に差圧が生じ始めた。また、反応器
入口付近の触媒には、20重全%以上もの大量の炭素の
析出が認められた。
When primary desulfurized naphtha containing 2 ppm of sulfur is used as a raw material, the activity of the catalyst is lost after 200 hours, and almost all 9 naphthas come out of the reactor unreacted. First, a pressure difference began to occur within the catalyst layer. In addition, a large amount of carbon (more than 20% by weight or more) was observed to be deposited on the catalyst near the reactor inlet.

一方、高次脱硫精製ナフサを原料とする場合には、40
0時間経過後にも、ナフサのスリップなどの活性劣化現
象はみられず、また、触媒への炭素析出も認められなか
った。
On the other hand, when high-level desulfurization refined naphtha is used as raw material, 40
Even after 0 hours had elapsed, no activity deterioration phenomena such as naphtha slip were observed, and no carbon deposition on the catalyst was observed.

第2表 反応温度     入口=400℃ 出口:700℃ 反応圧力     8 kg/cJ a GS/C2,
O H2/ナフサ   0,1(モル比) LH8V      1.2 触媒量      100cc 実施例6 実施例5と同様にしてナフサの高温水蒸気改質を第3表
に示す条件下に行なった。
Table 2 Reaction temperature Inlet = 400℃ Outlet: 700℃ Reaction pressure 8 kg/cJ a GS/C2,
O H2/naphtha 0.1 (mole ratio) LH8V 1.2 Catalyst amount 100 cc Example 6 High temperature steam reforming of naphtha was carried out in the same manner as in Example 5 under the conditions shown in Table 3.

高次脱硫精製ナフサを原料とする場合には、2000時
間経過後にも、ナフサのスリップなどの活性劣化現象は
みられず、また、触媒への炭素析出も認められなかった
When highly desulfurized refined naphtha was used as a raw material, no activity deterioration phenomena such as naphtha slip were observed even after 2000 hours, and no carbon deposition on the catalyst was observed.

一方、水添脱硫時のLH8Vを1とする以外は比較例1
と同様にして脱硫した一次脱硫精製ナフサ(硫黄含有f
io、lppm)を原料とする場合には、2000時間
経過後には、触媒層での差圧が増大して運転が不可能と
なった。この際、大量の未反応ナフサが反応器外に出て
きていた。また、このようにして使用した触媒を分析し
たところ、10〜20重量%の炭素析出が認められた。
On the other hand, Comparative Example 1 except that LH8V during hydrodesulfurization was set to 1.
Primary desulfurized purified naphtha (sulfur-containing f) desulfurized in the same manner as
io, lppm) as the raw material, the differential pressure at the catalyst layer increased after 2000 hours, making operation impossible. At this time, a large amount of unreacted naphtha came out of the reactor. Further, when the catalyst thus used was analyzed, 10 to 20% by weight of carbon was observed to be deposited.

第3表 反応温度     人口:400°C 出ロ:745°C 反応圧力     8 kg / c♂・GS/C2,
O H2/ナフサ   0.1(モル比) LH3V      2. 0 触媒量      100cc 実施例7 実施例1と同様にして得られた高次脱硫精製ナフサと比
較例1と同様にして得られた一次脱硫精製ナフサとをそ
れぞれ原料とし、流通式疑似断熱反応器(直径20mm
)を使用して、実施例4で使用した市販Ni触媒の存在
下に第4表に示す条件で水蒸気改質を行なった。
Table 3 Reaction temperature Population: 400°C Output temperature: 745°C Reaction pressure 8 kg/c♂・GS/C2,
O H2/naphtha 0.1 (molar ratio) LH3V 2. 0 Catalyst amount 100cc Example 7 High-level desulfurized purified naphtha obtained in the same manner as in Example 1 and primary desulfurized purified naphtha obtained in the same manner as in Comparative Example 1 were used as raw materials, respectively, and a flow-through pseudo-adiabatic reactor ( Diameter 20mm
), steam reforming was carried out under the conditions shown in Table 4 in the presence of the commercially available Ni catalyst used in Example 4.

第4表 反応温度     入口:490℃(断熱)反応圧力 
    8kg/ca−G ナフサ流量    160 c c / h r触媒量
      100cc S/C2,5 H2/ナフサ   0.1(モル比) 第8図よび第9図にその結果を示す。
Table 4 Reaction temperature Inlet: 490℃ (adiabatic) Reaction pressure
8 kg/ca-G Naphtha flow rate 160 cc/hr Catalyst amount 100 cc S/C2,5 H2/naphtha 0.1 (molar ratio) The results are shown in FIGS. 8 and 9.

第8図において、曲線E−1および曲線E−2は、それ
ぞれ反応開始直後と反応開始400時間後の反応器内触
媒層の温度プロフィールを示す。
In FIG. 8, curve E-1 and curve E-2 show the temperature profiles of the catalyst layer in the reactor immediately after the start of the reaction and 400 hours after the start of the reaction, respectively.

高次脱硫精製ナフサを使用する場合には、実施例1にお
けると同様に、400時間経過後にも、温度プロフィー
ルは変化せず、改質触媒は十分に高い活性を維持し続け
ている。従って、本発明によれば、Ni触媒を使用する
場合にも、炭素析出防止のために従来使用されている様
な大量の水素または水蒸気を必要せず、改質触媒の消耗
口の低下、必要触媒量の減少による反応器の小型化が可
能となる。
When using highly desulfurized refined naphtha, the temperature profile did not change even after 400 hours, as in Example 1, and the reforming catalyst continued to maintain sufficiently high activity. Therefore, according to the present invention, even when using a Ni catalyst, there is no need for a large amount of hydrogen or water vapor, which is conventionally used to prevent carbon deposition, and the consumption of the reforming catalyst is reduced. It is possible to downsize the reactor by reducing the amount of catalyst.

一方、−次脱硫ナフサを使用した場合の結果は、第9図
に示す通りである。第9図において、曲線F−1および
曲線F−2は、それぞれ反応開始直後と反応開始400
時間後の反応器内触媒層の温度プロフィールを示す。
On the other hand, the results when using -order desulfurization naphtha are as shown in FIG. In FIG. 9, curve F-1 and curve F-2 are curves immediately after the start of the reaction and 400 minutes after the start of the reaction, respectively.
The temperature profile of the catalyst layer in the reactor after time is shown.

曲線F−1と曲線F−2との対比から明らかな様に、4
00時間後には、反応器入口付近の改質触媒が失活して
おり、吸熱反応および発熱反応による温度変化の領域が
触媒層の出口の方向に移動している。また、この際、1
0重量%以上の大量の炭素が析出しており、差圧の増大
により、これ以上の運転の継続は不可能であった。
As is clear from the comparison between curve F-1 and curve F-2, 4
After 00 hours, the reforming catalyst near the reactor inlet has been deactivated, and the region of temperature change due to endothermic and exothermic reactions has moved toward the outlet of the catalyst layer. Also, at this time, 1
A large amount of carbon (more than 0% by weight) had been precipitated, and due to the increase in differential pressure, it was impossible to continue the operation any further.

実施例8 実施例1と同様にして得た高次脱硫精製ナフサを原料と
し、市販Ni触媒(Ni4度14重量%、天然ガス用水
蒸気改質触媒)を充填した外熱式反応器(管径1.5イ
ンチ)を使用して、第5表に示す条件下にナフサの高温
水蒸気改質を行なった。
Example 8 An external heating reactor (pipe diameter: 1.5 inch), high-temperature steam reforming of naphtha was carried out under the conditions shown in Table 5.

その結果、600時間経過後にもナフサのスリップなど
の活性劣化現象は発生せず、また、触媒への炭素析出も
認められなかった。
As a result, no activity deterioration phenomena such as naphtha slip occurred even after 600 hours, and no carbon deposition on the catalyst was observed.

第5表 反応温度     入口:490℃ 出ロ:750°C 反応圧力     8kg/cj−G S/C2,5 H2/ナフサ   0.1(モル比) LH8V      1.0 触媒量      300cc 実施例9 硫黄含有ffi 200 p p mのコークス炉ガス
を、常法に従って、まずNi−Mo系水添脱硫触媒の存
在下に温度380℃、圧力8kg/cJ−G。
Table 5 Reaction temperature Inlet: 490°C Outlet: 750°C Reaction pressure 8kg/cj-G S/C2,5 H2/naphtha 0.1 (mole ratio) LH8V 1.0 Catalyst amount 300cc Example 9 Sulfur-containing ffi 200 ppm of coke oven gas was first heated at a temperature of 380°C and a pressure of 8 kg/cJ-G in the presence of a Ni-Mo hydrodesulfurization catalyst according to a conventional method.

GH8V100の条件下に水添分解した後、ZnO系吸
着脱硫剤に接触させて、−次吸着脱硫した。得られた一
次吸着脱硫コークス炉ガス中の硫黄化合物濃度は、約0
.lppmであった。
After hydrogenolysis under the conditions of GH8V100, it was brought into contact with a ZnO-based adsorption desulfurization agent to carry out second adsorption desulfurization. The concentration of sulfur compounds in the obtained primary adsorption desulfurization coke oven gas was approximately 0.
.. It was lppm.

一方、硝酸銅及び硝酸亜鉛を溶解する混合水溶液にアル
カリ物質として炭酸ナトリウムを加え、生じた沈澱を洗
浄及び濾過した後、高さ1/8インチ×直径1/8イン
チの大きさに打錠成形し、約300℃で焼成した。次い
で、該焼成体(酸化銅50%、酸化亜鉛50%)100
ccを充填した高次脱硫装置(脱硫層長さ30cm)に
水素2%を含む窒素ガスを通じ、温度的200℃で還元
した後、上記で得た一次吸着脱硫コークス炉ガス400
 Q / h rを通じ、温度250℃、圧力8kg/
ci−Gの条件下に高次脱硫した。
On the other hand, sodium carbonate is added as an alkaline substance to a mixed aqueous solution in which copper nitrate and zinc nitrate are dissolved, and the resulting precipitate is washed and filtered, and then formed into tablets with a size of 1/8 inch in height x 1/8 inch in diameter. and fired at about 300°C. Next, the fired body (copper oxide 50%, zinc oxide 50%) 100
The primary adsorption desulfurization coke oven gas obtained above was reduced at a temperature of 200°C by passing nitrogen gas containing 2% hydrogen through a high-order desulfurization equipment (desulfurization layer length 30 cm) filled with cc.
Through Q/hr, temperature 250℃, pressure 8kg/
High-order desulfurization was carried out under ci-G conditions.

その結果、最終的に得られた精製ガス中の硫黄濃度は、
10000時間の運転にわたり、0. 1ppb以下で
あった。
As a result, the sulfur concentration in the final purified gas is
Over 10,000 hours of operation, 0. It was less than 1 ppb.

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

第1図、第2図及び第3図は、本発明の実施態様を示す
フローチャートである。第4図及び第5図は、炭化水素
の精製度が水蒸気改質に及ぼす影響を示すグラフである
。第6図は、硫黄被毒程度の異なる触媒における水蒸気
改質反応中の炭素析出量の経時変化を示すグラフである
。第7図は、高温水蒸気改質におけるS/C(炭化水素
中の炭素1モル当りの水蒸気のモル数)と触媒への炭素
析出量との関係を示すグラフである。第8図及び第9図
は、炭化水素の精製度が水蒸気改質に及ぼす影響を示す
他のグラフである。 (以上) 第4図 触媒M玉 (cm) δ し490 づ ”’480 【 第5図 触媒N五(cm) 第6図 □□□−■ 一〇〇 反応時間(h「) 第7図 ′ア 騒 第8図 魅側口(cm) 第9図 触媒I長(cm)
1, 2, and 3 are flowcharts illustrating embodiments of the present invention. FIGS. 4 and 5 are graphs showing the influence of the degree of purification of hydrocarbons on steam reforming. FIG. 6 is a graph showing changes over time in the amount of carbon deposited during the steam reforming reaction in catalysts with different degrees of sulfur poisoning. FIG. 7 is a graph showing the relationship between S/C (number of moles of steam per mole of carbon in hydrocarbons) and the amount of carbon deposited on the catalyst in high-temperature steam reforming. FIGS. 8 and 9 are other graphs showing the influence of the degree of purification of hydrocarbons on steam reforming. (Over) Figure 4 Catalyst M ball (cm) δ 490 zu"'480 Figure 5 Catalyst N5 (cm) Figure 6 □□□-■ 100 reaction time (h") Figure 7' Fig. 8 Side opening (cm) Fig. 9 Catalyst I length (cm)

Claims (5)

【特許請求の範囲】[Claims] (1)炭化水素を高次脱硫剤により硫黄含有量5ppb
以下に脱硫した後、水蒸気改質を行うことを特徴とする
炭化水素の水蒸気改質方法。
(1) The sulfur content of hydrocarbons is reduced to 5 ppb using a high-order desulfurization agent.
A method for steam reforming hydrocarbons, which comprises performing steam reforming after desulfurization.
(2)硫黄含有量1ppb以下に脱硫した後、水蒸気改
質を行う特許請求の範囲第1項に記載の炭化水素の水蒸
気改質方法。
(2) The method for steam reforming hydrocarbons according to claim 1, wherein steam reforming is performed after desulfurization to a sulfur content of 1 ppb or less.
(3)硫黄含有量0.1ppb以下に脱硫した後、水蒸
気改質を行う特許請求の範囲第2項に記載の炭化水素の
水蒸気改質方法。
(3) The method for steam reforming hydrocarbons according to claim 2, wherein steam reforming is performed after desulfurization to reduce the sulfur content to 0.1 ppb or less.
(4)銅化合物、亜鉛化合物及びアルミニウム化合物を
原料として共沈法により調製した酸化銅−酸化亜鉛−酸
化アルミニウム混合物を水素還元して得た高次脱硫剤を
使用する特許請求の範囲第1項乃至第3項のいずれかに
記載の炭化水素の水蒸気改質方法。
(4) Claim 1 that uses a high-order desulfurization agent obtained by hydrogen reduction of a copper oxide-zinc oxide-aluminum oxide mixture prepared by a coprecipitation method using a copper compound, a zinc compound, and an aluminum compound as raw materials. The method for steam reforming hydrocarbons according to any one of items 3 to 3.
(5)銅化合物及び亜鉛化合物を原料として共沈法によ
り調製した酸化銅−酸化亜鉛混合物を水素還元して得た
高次脱硫剤を使用する特許請求の範囲第1項乃至第3項
のいずれかに記載の炭化水素の水蒸気改質方法。
(5) Any one of claims 1 to 3 which uses a high-order desulfurization agent obtained by hydrogen reduction of a copper oxide-zinc oxide mixture prepared by a coprecipitation method using a copper compound and a zinc compound as raw materials. A method for steam reforming hydrocarbons as described in .
JP63318818A 1987-12-17 1988-12-16 Hydrocarbon steam reforming method Expired - Lifetime JP2683531B2 (en)

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JP62-320282 1987-12-17
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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2001205004A (en) * 2000-01-28 2001-07-31 Japan Energy Corp Method for removing sulfur compounds
JP2001262161A (en) * 2000-03-15 2001-09-26 Idemitsu Kosan Co Ltd Fuel oil for fuel cells
JP2007126330A (en) * 2005-11-04 2007-05-24 T Rad Co Ltd Operation method of reformer and reformer

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4446005A (en) * 1982-09-17 1984-05-01 Exxon Research And Engineering Co. Guard bed for the removal of sulfur and nickel from feeds previously contacted with nickel containing sulfur adsorption catalysts
US4456527A (en) * 1982-10-20 1984-06-26 Chevron Research Company Hydrocarbon conversion process
JPS6217003A (en) * 1985-07-12 1987-01-26 Jgc Corp Steam reforming method for hydrocarbon using ruthenium catalyst

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4446005A (en) * 1982-09-17 1984-05-01 Exxon Research And Engineering Co. Guard bed for the removal of sulfur and nickel from feeds previously contacted with nickel containing sulfur adsorption catalysts
US4456527A (en) * 1982-10-20 1984-06-26 Chevron Research Company Hydrocarbon conversion process
US4456527B1 (en) * 1982-10-20 1986-05-20
JPS6217003A (en) * 1985-07-12 1987-01-26 Jgc Corp Steam reforming method for hydrocarbon using ruthenium catalyst

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2001205004A (en) * 2000-01-28 2001-07-31 Japan Energy Corp Method for removing sulfur compounds
JP2001262161A (en) * 2000-03-15 2001-09-26 Idemitsu Kosan Co Ltd Fuel oil for fuel cells
JP2007126330A (en) * 2005-11-04 2007-05-24 T Rad Co Ltd Operation method of reformer and reformer

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