JPH0472878B2 - - Google Patents
Info
- Publication number
- JPH0472878B2 JPH0472878B2 JP21204683A JP21204683A JPH0472878B2 JP H0472878 B2 JPH0472878 B2 JP H0472878B2 JP 21204683 A JP21204683 A JP 21204683A JP 21204683 A JP21204683 A JP 21204683A JP H0472878 B2 JPH0472878 B2 JP H0472878B2
- Authority
- JP
- Japan
- Prior art keywords
- coal
- gas
- gasifier
- desulfurization
- slag
- 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
- 239000003245 coal Substances 0.000 claims description 33
- 239000007789 gas Substances 0.000 claims description 24
- 239000003795 chemical substances by application Substances 0.000 claims description 19
- 238000006477 desulfuration reaction Methods 0.000 claims description 17
- 230000023556 desulfurization Effects 0.000 claims description 17
- 238000000034 method Methods 0.000 claims description 17
- 238000002309 gasification Methods 0.000 claims description 13
- 239000002699 waste material Substances 0.000 claims description 9
- 229910052760 oxygen Inorganic materials 0.000 claims description 4
- 229910052717 sulfur Inorganic materials 0.000 claims description 4
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 claims description 3
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims description 3
- 239000001301 oxygen Substances 0.000 claims description 3
- 239000011593 sulfur Substances 0.000 claims description 3
- 239000002994 raw material Substances 0.000 claims description 2
- 239000002893 slag Substances 0.000 description 16
- 230000000694 effects Effects 0.000 description 6
- 239000000428 dust Substances 0.000 description 5
- 230000008929 regeneration Effects 0.000 description 5
- 238000011069 regeneration method Methods 0.000 description 5
- UQSXHKLRYXJYBZ-UHFFFAOYSA-N Iron oxide Chemical compound [Fe]=O UQSXHKLRYXJYBZ-UHFFFAOYSA-N 0.000 description 4
- 238000010586 diagram Methods 0.000 description 4
- 238000006243 chemical reaction Methods 0.000 description 3
- 230000003009 desulfurizing effect Effects 0.000 description 3
- 239000000446 fuel Substances 0.000 description 3
- XEEYBQQBJWHFJM-UHFFFAOYSA-N iron Substances [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 3
- 241000766026 Coregonus nasus Species 0.000 description 2
- 238000010521 absorption reaction Methods 0.000 description 2
- 229910002091 carbon monoxide Inorganic materials 0.000 description 2
- 230000007423 decrease Effects 0.000 description 2
- 229910000514 dolomite Inorganic materials 0.000 description 2
- 239000010459 dolomite Substances 0.000 description 2
- 229910052739 hydrogen Inorganic materials 0.000 description 2
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 2
- 238000012545 processing Methods 0.000 description 2
- 238000011084 recovery Methods 0.000 description 2
- 238000011160 research Methods 0.000 description 2
- 238000012360 testing method Methods 0.000 description 2
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 1
- 235000021538 Chard Nutrition 0.000 description 1
- QPLDLSVMHZLSFG-UHFFFAOYSA-N Copper oxide Chemical compound [Cu]=O QPLDLSVMHZLSFG-UHFFFAOYSA-N 0.000 description 1
- XLOMVQKBTHCTTD-UHFFFAOYSA-N Zinc monoxide Chemical compound [Zn]=O XLOMVQKBTHCTTD-UHFFFAOYSA-N 0.000 description 1
- 239000003513 alkali Substances 0.000 description 1
- 150000004649 carbonic acid derivatives Chemical class 0.000 description 1
- 239000013064 chemical raw material Substances 0.000 description 1
- 238000002485 combustion reaction Methods 0.000 description 1
- 238000007599 discharging Methods 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 239000001257 hydrogen Substances 0.000 description 1
- 125000004435 hydrogen atom Chemical class [H]* 0.000 description 1
- 229910052742 iron Inorganic materials 0.000 description 1
- 238000002844 melting Methods 0.000 description 1
- 230000008018 melting Effects 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 239000012256 powdered iron Substances 0.000 description 1
- 238000010248 power generation Methods 0.000 description 1
- 230000002265 prevention Effects 0.000 description 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 1
Landscapes
- Treating Waste Gases (AREA)
Description
【発明の詳細な説明】
本発明は石炭ガス化プロセスに係り、特に噴流
床式の石炭ガス化プロセスに関するものである。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a coal gasification process, and more particularly to an spouted bed type coal gasification process.
一般に、石炭を空気或いは酸素等のガス化剤で
ガス化して可燃性ガスを生成する石炭ガス化装置
は、生成ガスの用途に応じて種々のガス化方式が
あり、型式別では例えば噴流床式、流動床式、固
定床式等がある。噴流床式は微粉炭をガス化剤と
一緒にノズルより噴出してガス化させる方式であ
る。 In general, coal gasifiers that generate combustible gas by gasifying coal with a gasifying agent such as air or oxygen have various gasification methods depending on the use of the produced gas. , fluidized bed type, fixed bed type, etc. The spouted bed type is a method in which pulverized coal is jetted out from a nozzle together with a gasifying agent to gasify it.
第1図は従来の噴流床式石炭ガス化プロセスの
説明図であり、第1図において1は噴流床式石炭
ガス化炉である。この噴流床式石炭ガス化炉(以
下ガス化炉という。)1は、ガス化反応に必要な
高温域を形成するコンバスタ部2とコンバスタ部
2の高温を利用して微粉炭をガス化させるリアク
タ部3とから構成されている。コンバスタ部2に
は微粉炭を空気等のガス化剤と一緒に噴出する噴
出ノズル4が設けられており、5,6はそれぞれ
微粉炭及びガス化剤の供給ラインである。なお、
コンバスタ2での空気比(空気と微粉炭の化学量
論比)は通常0.6〜0.7に調整されている。微粉炭
とガス化剤はまた、リアクタ下部のノズル7より
も供給され全体としての(コンバスタ部とリアク
タ部に供給される空気と微粉炭の化学量論比)空
気比0.4〜0.6に調整される。8,9はそれぞれガ
ス化剤、微粉炭の供給ラインである。また、リア
クタ3の上部には生成ガスを取出す生成ガス取出
しライン10、未反応のチヤーを回収するサイク
ロン11、チヤー回収ライン12とが設けられて
いる。このチヤー回収ライン12の他端はコンバ
スタ部2に接続されており、回収された未反応の
チヤーは補助燃料としてライン13を経由して少
量のガス化剤とともにコンバスタ部2に供給され
る。一方、生成ガスは集塵装置101、湿式脱硫
装置102を経て精製され、精製ガスとしてライ
ン103から所要の目的に供される。 FIG. 1 is an explanatory diagram of a conventional spouted bed type coal gasification process, and in FIG. 1, 1 is a spouted bed type coal gasifier. This entrained bed coal gasifier (hereinafter referred to as gasifier) 1 is a combustor section 2 that forms a high temperature region necessary for gasification reaction, and a reactor that gasifies pulverized coal using the high temperature of the combustor section 2. It consists of Section 3. The combustor section 2 is provided with an ejection nozzle 4 for ejecting pulverized coal together with a gasifying agent such as air, and 5 and 6 are supply lines for the pulverized coal and the gasifying agent, respectively. In addition,
The air ratio (stoichiometric ratio of air and pulverized coal) in the combustor 2 is normally adjusted to 0.6 to 0.7. Pulverized coal and gasification agent are also supplied from the nozzle 7 at the bottom of the reactor, and the overall air ratio (stoichiometric ratio of air supplied to the combustor section and reactor section and pulverized coal) is adjusted to 0.4 to 0.6. . 8 and 9 are gasifying agent and pulverized coal supply lines, respectively. Further, in the upper part of the reactor 3, there are provided a produced gas take-off line 10 for taking out produced gas, a cyclone 11 for collecting unreacted chir, and a chir collection line 12. The other end of this chear recovery line 12 is connected to the combustor section 2, and the recovered unreacted chard is supplied to the combustor section 2 along with a small amount of gasifying agent via the line 13 as auxiliary fuel. On the other hand, the generated gas is purified through a dust collector 101 and a wet desulfurization device 102, and is supplied as purified gas to a desired purpose through a line 103.
このように構成したガス化炉によつてコンバス
タ部2では微粉炭を燃焼してガス化反応(吸熱反
応)に必要な高温域を形成し、リアクタ部3では
噴出ノズル7より噴出された微粉炭をコンバスタ
部2の燃焼熱(1500〜1700℃)によつて空気等の
ガス化剤でガス化させ、水素、一酸化炭素、メタ
ン等を主とする生成ガスを得る。なおコンバスタ
部2で燃焼された微粉炭とチヤー中の灰分は溶融
スラグとなつて溶融スラグ排出口14から排出さ
れ、水中に落して回収される。 With the gasifier configured in this way, the combustor section 2 burns the pulverized coal to form a high temperature region necessary for the gasification reaction (endothermic reaction), and the reactor section 3 burns the pulverized coal ejected from the ejection nozzle 7. is gasified with a gasifying agent such as air using the combustion heat (1500 to 1700°C) of the combustor section 2 to obtain a generated gas mainly containing hydrogen, carbon monoxide, methane, etc. The pulverized coal burned in the combustor section 2 and the ash in the char become molten slag and are discharged from the molten slag discharge port 14, dropped into water, and recovered.
以上は、噴流床ガス化炉の一形式について略述
したものであるが、現時点ではこのガス化炉本体
についても研究課題は残されており、炉底からの
円滑なスラグ排出もその一つである。実際豪州炭
など融点が高く粘性が低い灰成分を有する石炭に
ついては、コンバスタ内を非常な高温に維持する
などスラグ排出に工夫を要する。 The above is a brief description of one type of entrained bed gasifier, but at present there are still research issues to be solved regarding the gasifier itself, and one of them is the smooth discharge of slag from the bottom of the furnace. be. In fact, for coal such as Australian coal, which has a high melting point and low viscosity and an ash component, special measures are required to discharge the slag, such as maintaining the inside of the combustor at a very high temperature.
本発明者らはスラグの円滑な排出方法について
鋭意研究を重ねた結果、ガス化炉に後置されるク
リンナツプ系装置の一つである脱硫装置からの使
用済み廃棄脱硫剤が、スラグ粘度を下げスラグ排
出を容易にする効果をもつことを見出し、この知
見に基づいて本発明に到つたものである。また、
本発明は処分の困難な硫黄分含有の該使用済み脱
硫剤の廃棄を不要とする利点をも有し、工業上極
めて有用な発明である。 The inventors of the present invention have conducted intensive research on methods for smoothly discharging slag, and have found that the used waste desulfurization agent from the desulfurization equipment, which is one of the cleanup systems installed after the gasifier, reduces the slag viscosity. It was discovered that this has the effect of facilitating slag discharge, and based on this knowledge, the present invention was developed. Also,
The present invention has the advantage that it is not necessary to dispose of the used desulfurizing agent containing sulfur, which is difficult to dispose of, and is an extremely useful invention industrially.
すなわち、本発明は原料である石炭を、その化
学量論量より少量の空気および/又は酸素によつ
てガス化させ、CO、H2を主成分とするガスを得
るスラグタツプ方式の石炭ガス化プロセスにおい
て、粗製ガス中の硫黄分を除去するための脱硫剤
の使用済み廃棄物を、ガス化炉の高温部に投入す
ることを特徴とする噴流床方式石炭ガス化プロセ
スを提案するものである。 That is, the present invention provides a slug-tap coal gasification process in which coal, which is a raw material, is gasified with a smaller amount of air and/or oxygen than its stoichiometric amount to obtain a gas whose main components are CO and H2 . In this paper, we propose a spouted bed type coal gasification process characterized by charging spent waste of desulfurization agent for removing sulfur content from crude gas into the high-temperature section of a gasifier.
以下図面により本発明の実施態様例について詳
細に説明する。第2図は本発明の1実施態様例の
説明図である。第2図において第1図と同一符号
のものは第1図と同一の機能を有する部分を示
す。第2図においてライン15は粗製のガス化生
成ガスであり、主要成分であるCO、H2、CH4、
CO2、H2O、N2のほか、ダストH2S、NH3等の
微量成分を含む。これらの微量成分は生成ガスを
どのような目的例えば、コンバインド発電用のガ
スタービン燃料、都市ガス燃料、化学原料として
使用するにせよ、相当低濃度に迄低減する必要が
ある。16は精密脱塵装置であり、17は捕集し
たダストの抜き出しラインである。18,19は
H2S除去用の乾式脱硫装置であり、図では2塔の
流動床連続再生方式の例を示しているが、これに
限られるものではなく、本発明のプロセスでは勿
論他の型式例えば、固定床間欠切替え方式も適用
可能である。18はH2S吸収装置であり、19は
吸収したH2Sを再生用ガス(例えば、空気)によ
つて放出させ、脱硫剤活性を復帰させることを目
的とする再生装置である。また、20は再生用ガ
スの供給ライン、21はS分回収装置へ到る高濃
度のS分を含有するガスの流路である。 Embodiments of the present invention will be described in detail below with reference to the drawings. FIG. 2 is an explanatory diagram of one embodiment of the present invention. In FIG. 2, the same reference numerals as in FIG. 1 indicate parts having the same functions as in FIG. In FIG. 2, line 15 is the crude gasification product gas, and the main components are CO, H 2 , CH 4 ,
In addition to CO 2 , H 2 O, and N 2 , it also contains trace components such as dust H 2 S and NH 3 . These trace components need to be reduced to a fairly low concentration no matter what purpose the produced gas is used for, for example, as gas turbine fuel for combined power generation, city gas fuel, or chemical raw material. 16 is a precision dust removing device, and 17 is a line for extracting the collected dust. 18 and 19 are
This is a dry desulfurization equipment for H 2 S removal, and although the figure shows an example of a two-column fluidized bed continuous regeneration system, it is not limited to this, and of course other types such as fixed An intermittent switching method is also applicable. 18 is a H 2 S absorption device, and 19 is a regeneration device whose purpose is to release the absorbed H 2 S using a regeneration gas (for example, air) to restore the desulfurizing agent activity. Further, 20 is a supply line for regeneration gas, and 21 is a flow path for gas containing a high concentration of S to reach the S recovery device.
こうして脱塵、脱硫の過程を経て精浄となつた
精製ガスは流路20を経て上記した所要の目的に
供せられる。 The purified gas thus purified through the processes of dust removal and desulfurization is supplied to the above-mentioned required purpose via the flow path 20.
ここで脱硫剤としては一般に、酸化鉄
(Fe2O3)、アルカリ炭酸塩(CaCO3、MgCO3)、
酸化亜鉛(ZnO)、酸化銅(CuO)などが用いら
れるが、時間の経過とともにこれらの一部は活性
を失し、廃棄せざるを得ず、系外へ排出すること
が必要となる。22はその廃棄物排出ラインであ
るが、この使用ずみ脱硫剤はS分及び操作条件に
よつては微少量のCl分、CN分等を含み公害防止
上容易に環境へは戻し難いものである。 Here, desulfurization agents generally include iron oxide (Fe 2 O 3 ), alkali carbonates (CaCO 3 , MgCO 3 ),
Zinc oxide (ZnO), copper oxide (CuO), etc. are used, but some of these lose their activity over time and must be discarded and discharged from the system. 22 is the waste discharge line, but this used desulfurization agent contains S content and, depending on the operating conditions, trace amounts of Cl content, CN content, etc., and is difficult to easily return to the environment for pollution prevention reasons. .
本発明では、これをコンバスタ部2に供給し微
粉炭或いはチヤーとともにコンバスタにおいて高
温処理する。これにより、スラグ粘度は低下し、
脱硫廃棄物の処理も不要となる。スラグ粘度の低
下はガス化炉の円滑な連続運転を可能とするとと
もに、コンバスタをさほど高温度に維持する必要
がなくなるため、コンバスタでの所要空気量が減
少し、結果的に生成ガスの発熱量の上昇、全体効
率の向上につながりプロセス上極めて望ましいこ
とである。勿論廃棄脱硫剤中のFe分、Ca分など
はスラグ中に捕捉される。また、S分、Cl分、
CN分等は生成ガス中に放出されるが、これらは
主流中の各成分量に比較すれば極めて少量であり
問題はない。 In the present invention, this is supplied to the combustor section 2 and subjected to high temperature treatment in the combustor together with pulverized coal or coal. This reduces the slag viscosity and
There is also no need to process desulfurization waste. The reduction in slag viscosity enables smooth continuous operation of the gasifier, and since it is no longer necessary to maintain the combustor at a very high temperature, the amount of air required in the combustor is reduced, resulting in the calorific value of the produced gas. This is extremely desirable in terms of the process, as it leads to an increase in the overall efficiency. Of course, Fe, Ca, etc. in the waste desulfurization agent are captured in the slag. In addition, S minute, Cl minute,
Although CN components and the like are released into the generated gas, these are extremely small amounts compared to the amount of each component in the main stream and pose no problem.
以上詳細に説明したように本発明のプロセスに
よれば、噴流床式ガス化炉の最も大きな課題の一
つである、スラグ排出特性を改善しスラグの排出
を円滑にし、併せて廃棄脱硫剤の処理も不要とす
るという特有の効果を奏することができ、本発明
は工業上極めて有用なプロセスを提供するもので
ある。 As explained in detail above, the process of the present invention improves the slag discharge characteristics, which is one of the biggest problems of entrained bed gasifiers, and makes the slag discharge smoother. The present invention provides an industrially extremely useful process, which has the unique effect of eliminating the need for treatment.
以下、実施例により本発明の効果について詳細
に説明する。 Hereinafter, the effects of the present invention will be explained in detail using Examples.
実施例 1
まず小型の固定床式脱硫装置(処理ガス量15N
/分)を試作し、脱硫テストを実施した。脱硫
剤としては粉末状酸化鉄(Fe2O3)を用いた。約
250時間に連続テストの後、脱硫性能が初期の80
%程度に低下したので、これを100Kg/Hの処理
能力を有する常圧型噴流床ガス化炉に微粉炭(豪
州一般炭)とともに、2Kg/Hの速度で約1時間
投入した。Example 1 First, a small fixed bed desulfurization equipment (processing gas amount 15N
/min) and conducted a desulfurization test. Powdered iron oxide (Fe 2 O 3 ) was used as the desulfurizing agent. about
After 250 hours of continuous testing, the desulfurization performance was the initial 80
%, this was fed into an atmospheric pressure spouted bed gasifier having a processing capacity of 100 kg/H together with pulverized coal (Australian steam coal) at a rate of 2 kg/H for about 1 hour.
その結果、投入前には、コンバスタを高温度
(約1700℃)に維持するため、全体の空気比が
0.56に相当する量の空気がガス化剤として必要で
あつたが、脱硫廃棄物の添加によつてスラグの粘
度が低下する効果により、全体の空気比が0.47で
円滑な運転が可能となり、また生成ガスの発熱量
も880Kcal/Nm3から1012Kcal/Nm3に向上し
た。なお、実験後、とり出したスラグの粘度を計
測した所、脱硫廃棄物添加前のスラグの粘度が
1400℃において230ポアズであつたのに対し、添
加後は同一温度において115ポアズであり粘度が
低下していた。 As a result, since the combustor is maintained at a high temperature (approximately 1700℃) before it is turned on, the overall air ratio is
An amount of air equivalent to 0.56 was required as a gasifying agent, but due to the effect of reducing the viscosity of the slag by adding desulfurization waste, smooth operation was possible with an overall air ratio of 0.47. The calorific value of the generated gas also improved from 880 Kcal/Nm 3 to 1012 Kcal/Nm 3 . After the experiment, we measured the viscosity of the slag taken out and found that the viscosity of the slag before adding desulfurization waste was
The viscosity was 230 poise at 1400°C, but after addition it was 115 poise at the same temperature, indicating a decrease in viscosity.
実施例 2
実施例1と殆ど同一の操作を脱硫剤として粉状
ドロマイトを用いて実施した。使用済みドロマイ
トのガス化炉コンバスタ部への添加により、炉底
からのスラグの流下が極めて円滑となり、生成ガ
スの発熱量も投入前876Kcal/Nm3から
1005Kcal/Nm3と向上した。Example 2 Almost the same operation as in Example 1 was carried out using powdered dolomite as the desulfurization agent. By adding used dolomite to the combustor section of the gasifier, the flow of slag from the bottom of the furnace becomes extremely smooth, and the calorific value of the generated gas decreases from 876 Kcal/Nm 3 before input.
Improved to 1005Kcal/Nm 3 .
第1図は従来の噴流床式石炭ガス化プロセスの
説明図、第2図は本発明の1実施態様例の説明図
である。
1……噴流床式石炭ガス化炉、2……コンバス
タ部、3……リアクタ部、5,9……微粉炭供給
ライン、6,8……ガス化剤供給ライン、18…
…H2S吸収装置、19……再生装置、22……廃
棄物排出ライン。
FIG. 1 is an explanatory diagram of a conventional spouted bed type coal gasification process, and FIG. 2 is an explanatory diagram of one embodiment of the present invention. DESCRIPTION OF SYMBOLS 1... Entrained bed coal gasifier, 2... Combustor section, 3... Reactor section, 5, 9... Pulverized coal supply line, 6, 8... Gasifier supply line, 18...
... H2S absorption device, 19...regeneration device, 22...waste discharge line.
Claims (1)
の空気および/又は酸素によつてガス化させ、
CO、H2を主成分とするガスを得るスラグタツプ
方式の石炭ガス化プロセスにおいて、粗製ガス中
の硫黄分を除去するための脱硫剤の使用済み廃棄
物を、ガス化炉の高温部に投入することを特徴と
する噴流床方式石炭ガス化プロセス。1. Gasifying the raw material coal with a smaller amount of air and/or oxygen than its stoichiometric amount,
In the slug-tap coal gasification process that produces gas whose main components are CO and H2 , used waste from desulfurization agents to remove the sulfur content from the crude gas is fed into the high-temperature section of the gasifier. A spouted bed coal gasification process characterized by:
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP21204683A JPS60104188A (en) | 1983-11-11 | 1983-11-11 | Coal gasification process |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP21204683A JPS60104188A (en) | 1983-11-11 | 1983-11-11 | Coal gasification process |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS60104188A JPS60104188A (en) | 1985-06-08 |
| JPH0472878B2 true JPH0472878B2 (en) | 1992-11-19 |
Family
ID=16615968
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP21204683A Granted JPS60104188A (en) | 1983-11-11 | 1983-11-11 | Coal gasification process |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS60104188A (en) |
Families Citing this family (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| ZA854014B (en) * | 1984-07-19 | 1986-10-29 | Texaco Development Corp | Coal gasification process |
| JPS6319550U (en) * | 1986-07-21 | 1988-02-09 | ||
| JPH0613240Y2 (en) * | 1986-10-23 | 1994-04-06 | バブコツク日立株式会社 | Gasifier for coal, etc. |
| JPH086101B2 (en) * | 1986-11-27 | 1996-01-24 | バブコツク日立株式会社 | Coal gasification desulfurization method |
| US20230114144A1 (en) * | 2020-03-24 | 2023-04-13 | Sekisui Chemical Co., Ltd. | Pyrolysis gas purification/cooling device, pyrolysis gas purification/cooling method, organic substance production device, and method for producing organic substance |
-
1983
- 1983-11-11 JP JP21204683A patent/JPS60104188A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS60104188A (en) | 1985-06-08 |
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