Deprecated: The each() function is deprecated. This message will be suppressed on further calls in /home/zhenxiangba/zhenxiangba.com/public_html/phproxy-improved-master/index.php on line 456
JPS5844114B2 - How to turn tar sludge into fuel - Google Patents
[go: Go Back, main page]

JPS5844114B2 - How to turn tar sludge into fuel - Google Patents

How to turn tar sludge into fuel

Info

Publication number
JPS5844114B2
JPS5844114B2 JP53139495A JP13949578A JPS5844114B2 JP S5844114 B2 JPS5844114 B2 JP S5844114B2 JP 53139495 A JP53139495 A JP 53139495A JP 13949578 A JP13949578 A JP 13949578A JP S5844114 B2 JPS5844114 B2 JP S5844114B2
Authority
JP
Japan
Prior art keywords
tar
slag
combustion
fuel
viscosity
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
JP53139495A
Other languages
Japanese (ja)
Other versions
JPS5566992A (en
Inventor
芳二 古沢
裕 後藤
欣一 菅原
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.)
Nippon Steel Corp
Original Assignee
Nippon Steel Corp
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 Nippon Steel Corp filed Critical Nippon Steel Corp
Priority to JP53139495A priority Critical patent/JPS5844114B2/en
Publication of JPS5566992A publication Critical patent/JPS5566992A/en
Publication of JPS5844114B2 publication Critical patent/JPS5844114B2/en
Expired legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel

Landscapes

  • Solid Fuels And Fuel-Associated Substances (AREA)
  • Working-Up Tar And Pitch (AREA)

Description

【発明の詳細な説明】 この発明は、コークス製造過程で発生するタールスラグ
を工業窯炉の燃料として活用する方法に関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method of utilizing tar slag generated in a coke manufacturing process as a fuel for an industrial kiln.

コークス炉ガスの精製工程に於て、ガス中に含まれるタ
ールをガス冷却したガス液と共に回収し、タールと、ガ
ス液に重力分離する際、ガス中に随伴する石炭粉、コー
クス粉等の固形物もタールと共に分離回収され、タール
スラグとして系外に排出される。
In the refining process of coke oven gas, when the tar contained in the gas is recovered together with the gas-cooled gas liquid and separated by gravity into tar and gas liquid, solids such as coal powder and coke powder that accompany the gas are collected. Materials are also separated and recovered along with the tar and discharged from the system as tar slag.

このタールスラグは固形分20〜30%、タール分60
〜70φからなり室温では固化状態に近く、運搬等の取
扱いが極めて困難であると共に環境汚染の問題を有して
いる。
This tar slag has a solid content of 20-30% and a tar content of 60%.
It has a diameter of ~70 φ and is almost solidified at room temperature, making it extremely difficult to transport and handle, and also poses the problem of environmental pollution.

そこで固形分とタール分を分離回収するため、スラグを
若干希釈して処理する方法が各種提案されている。
Therefore, various methods have been proposed in which the slag is slightly diluted and treated in order to separate and recover the solid content and tar content.

例えば特公昭49−20361、同49−20362、
同50−14645、同52−19849、同53−9
768号があり、これらはタールスラグにタール、水又
は安水等を加え、加温・粉砕により流動化して取扱いを
容易にしたうえ、固形分をタール中に分散させるか分離
回収することを主眼としている。
For example, Special Publications No. 49-20361, No. 49-20362,
50-14645, 52-19849, 53-9
No. 768, and these are made by adding tar, water, ammonium water, etc. to tar slag, making it fluidized by heating and crushing it to make it easier to handle, and then dispersing the solid content in the tar or separating and recovering it. There is.

しかし乍らこれらの提案に於て、回収固形分の再利用に
ついては原料炭に混入するか、もしくはタール中に分散
させるものであり、前記スラグによる弊害は減少し得て
も充分な有効利用法とはぎえない。
However, in these proposals, the reuse of recovered solids is mixed into coking coal or dispersed in tar, and even though the harmful effects of the slag may be reduced, this is not a sufficient effective method of reuse. I can't tell.

また工業窯炉の燃料に活用するため、コークス工場系外
に抜き出して燃焼させる方法が考えられるが、クールス
ラグそのま\の状態では燃焼に際し以下のような問題を
有している。
In addition, in order to utilize it as fuel for industrial furnaces, a method of extracting it outside the coke factory system and burning it is considered, but the following problems arise when burning cool slag in its original state.

(1)粘度が高いため流動化せずポンプ移送ができない
(1) Due to its high viscosity, it cannot be fluidized and cannot be pumped.

また何等かの方法で移送しても、完全燃焼のための霧化
ができず黒煙を発し易い。
Moreover, even if it is transferred by some method, it cannot be atomized for complete combustion and black smoke is likely to be emitted.

(2)粘度が高いため流量の計測、制御が極めて困難で
ある。
(2) Due to its high viscosity, it is extremely difficult to measure and control the flow rate.

また粘度を下げるため加温しても固形物が部分的に沈積
し、やはり流量を計測、制御できない。
Furthermore, even if heated to lower the viscosity, solids will partially settle, making it impossible to measure and control the flow rate.

(3)加温により流動化しても、固形物の粒度と硬度が
犬であるため、装置やバーナーの磨耗あるいは閉塞が激
しいうえ、フレーム内で燃焼が完結せず火の粉となって
炉内に落下し炉壁を損傷する。
(3) Even if the solids are fluidized by heating, the particle size and hardness of the solids are very low, so the equipment and burners are subject to severe wear or blockage, and combustion is not completed within the flame, turning into sparks and falling into the furnace. and damage the furnace wall.

従って連続かつ円滑な燃焼を維持できない0 以上の弊害によりスラグ単独で工業用炉用燃料に利用し
た試みは無く、僅かに特公昭53−4005号に於てタ
ールスラグを粉砕して多量のタール中に分散した後燃料
に供しているにすぎない。
Therefore, continuous and smooth combustion cannot be maintained.Due to the above-mentioned disadvantages, there has been no attempt to use slag alone as fuel for industrial furnaces. It is simply used as fuel after being dispersed.

以上の如く、タールスラグは取扱い及び燃料化が困難な
ため、工業上タールスラグの燃焼特性を生かした有効な
活用が図れず大半はスラグそのままの状態で原料炭に混
合されている現状であり、黄*しかも環境汚染上の問題
は避けられない。
As mentioned above, tar slag is difficult to handle and turn into fuel, so it cannot be effectively utilized industrially by taking advantage of its combustion characteristics, and most of the slag is mixed with coking coal in its original state. Moreover, environmental pollution problems are unavoidable.

本発明はか\る問題を解決するためになされたものであ
り、タールスラグによる弊害を完全に除去すると同時に
工業窯炉の燃料として活用する方法を提供するものであ
る。
The present invention was made to solve these problems, and provides a method for completely eliminating the harmful effects of tar slag and at the same time utilizing it as fuel for industrial kilns.

以下本発明を実施例に基づいて説明する。The present invention will be explained below based on examples.

コークス工場から発生するタールスラグは常温に於て固
化した状態であり、通常第1表の如き性状を有している
Tar slag generated from coke factories is in a solidified state at room temperature and usually has properties as shown in Table 1.

かSるタールスラグを工業窯炉の燃料として活用するに
は、移送を可能にしたうえ燃焼用バーナー先端で霧化す
る必要がある。
In order to utilize tar slag as a fuel for industrial furnaces, it is necessary to make it possible to transport it and to atomize it at the tip of a combustion burner.

油バーナーでの霧化は、空気流又は蒸気流により油を微
細にせん断することによって行なわれるものであり、こ
のせん断条件は、気流のエネルギ、気流と油との接触性
、油の粘性等によって定まる。
Atomization in an oil burner is performed by finely shearing oil using an air flow or steam flow, and the shearing conditions vary depending on the energy of the air flow, the contact between the air flow and the oil, the viscosity of the oil, etc. Determined.

したがって、ある粘度範囲の油では、気流のエネルギー
及び油との接触性等、バーナーの型式、構造あるいは使
用条件の設定によって、霧化条件を定めることが出来る
Therefore, for oil in a certain viscosity range, the atomization conditions can be determined by setting the burner type, structure, or usage conditions, such as the energy of the air flow and the contact with the oil.

しかしながら本タールスラジの場合、そのままでは通常
の油の粘性より著しく粘性が高いため、油の粘性範囲ま
で粘性を低下させることが必要になるO 第1図に通常使用されているバーナーの油粘度と油噴霧
粒径との関係、また第2図にタールスラグ粘度の温度依
存性を示すが、第1図によれば霧化に適した粘度は25
〜l 30cstであり、本発明者等はこの粘度を得る
ためにはタールスラグの温度を第2図の如く80〜12
0℃にする必要があることを見出した。
However, in the case of this tar sludge, the viscosity is significantly higher than that of ordinary oil, so it is necessary to reduce the viscosity to the viscosity range of oil. Figure 2 shows the relationship with the spray particle size and the temperature dependence of tar slag viscosity. According to Figure 1, the viscosity suitable for atomization is 25.
~l 30 cst, and the inventors have determined that in order to obtain this viscosity, the temperature of the tar slag should be adjusted to 80 to 12 cst as shown in Figure 2.
It was found that the temperature needed to be 0°C.

更にスラグ中の固形分は、微粉砕して比表面積を犬にす
ることにより、前記バーナーの型式の選定、気流条件等
により整えた霧化粒子と同程度の燃焼性を維持すること
が必要になる。
Furthermore, by finely pulverizing the solid content in the slag to increase the specific surface area, it is necessary to maintain the same level of combustibility as the atomized particles, which has been adjusted by selecting the burner model and air flow conditions. Become.

この場合、固形分の燃焼特性については、その性質上微
粉炭燃焼に関する数値を利用することが可能である。
In this case, for the combustion characteristics of the solid content, it is possible to use numerical values related to pulverized coal combustion due to its nature.

微粉炭の燃焼所要時間の一例を石炭粒子径と燃焼時間の
関係にして第3図に示すが、燃焼フレーム内石炭粒子の
滞留時間は11500〜1150秒程度であり、フレー
ム内で石炭粒を完全燃焼するためには石炭を6μ以下に
粉砕することが必要となる。
An example of the time required to burn pulverized coal is shown in Figure 3, showing the relationship between coal particle diameter and combustion time. In order to burn coal, it is necessary to crush it to 6 microns or less.

ところが工業窯炉では雰囲気温度が高く、この雰囲気温
度によって石炭粒の燃焼速度が大幅に影響され、第4図
に示す如く温度の高いほど石炭粒の燃焼が速まることか
ら、第3図のとおり雰囲気温度の高い工業窯炉では微粉
炭バーナーの使用によって、石炭の平均粒子径が50〜
200μでも燃焼を完了し得ることが判明した。
However, in industrial kilns, the ambient temperature is high, and the combustion speed of coal grains is greatly affected by this atmospheric temperature. As shown in Figure 4, the higher the temperature, the faster the coal grains burn. In high-temperature industrial kilns, the average particle size of coal is reduced to 50~ by using pulverized coal burners.
It was found that combustion could be completed even at 200μ.

更に該スラグの特殊性として固形分を多量に含有するた
め、微細化されても尚固形分は擬似粒子を形成し粗大粒
子と同等の作用をする。
Furthermore, as a special feature of the slag, since it contains a large amount of solid content, even if it is made fine, the solid content still forms pseudo particles and has the same effect as coarse particles.

そのため、タール分の粘性を下げて擬似粒子を破壊し、
固形分の粒度を微粉炭燃焼時の粒度より若干下げて、2
50μ以上の粒子を1%以下にする必要がある。
Therefore, the viscosity of the tar content is lowered and pseudo particles are destroyed.
The particle size of the solid content is slightly lower than the particle size of pulverized coal combustion, and 2
It is necessary to reduce the amount of particles larger than 50μ to 1% or less.

この燃焼状態について種々実験した結果、固形物の粒子
径は149μ以下を90%以上にすれば250μ以上を
1多以下にすることが出来、バーナーのフレーム内で固
形物の燃焼を好適に完了し得ることを見出した。
As a result of various experiments regarding this combustion condition, it was found that if the particle size of the solids is 149μ or less to 90% or more, the particle size of 250μ or more can be reduced to 1 or less, and the combustion of the solids can be suitably completed within the flame of the burner. I found out what I got.

以上の如きスラグの加温と粉砕によって、バーナー先端
での霧化即ち燃焼が通常の燃料と全く同等に可能となっ
た。
By heating and crushing the slag as described above, it has become possible to atomize it at the tip of the burner, that is, to burn it in exactly the same way as normal fuel.

しかも、この加温、粉砕によってポンプ1こよるスラグ
の移送が可能となり、燃焼装置やバーナーの磨耗あるい
は閉塞を大幅に改善できることとなる。
Moreover, this heating and pulverization makes it possible to transport the slag using the pump 1, and it is possible to significantly reduce wear and blockage of the combustion device and burner.

但し、スラグは微粉化されてもなお固形分を多量に含有
しているため、通常の燃料例えば重油や灯油等に比し装
置が磨耗、閉塞し易く、従って通常の燃焼装置例えばギ
ヤポンプ、オーバル流量計、内部混気式ノ→←等では長
時間の使用に適しない。
However, even if slag is pulverized, it still contains a large amount of solid content, so it is more likely to wear out and clog equipment than normal fuels such as heavy oil or kerosene. Meter, internal air mixture type, etc. are not suitable for long-term use.

このため本発明の実施にあたっては以下の装置を適用す
ることが望ましい。
Therefore, in carrying out the present invention, it is desirable to apply the following apparatus.

即ち、油ポンプは耐磨耗性のある構造を有しかつ定量給
油可能なダイヤプラム型ポンプを採用する0 特にタールスラグは固形分による閉塞のためいかなる流
量計も使用できず、従って流量制御できないが、この点
ダイヤフラム型ポンプは定量移送式であるから流量制御
が可能である。
In other words, the oil pump adopts a diaphragm type pump that has a wear-resistant structure and can supply a fixed amount of oil. In particular, tar slag cannot be used with any flow meter because it is clogged with solids, so the flow rate cannot be controlled. In this respect, since the diaphragm pump is a fixed quantity transfer type, it is possible to control the flow rate.

更に、スラグによるバーナーのオイルノズルの磨耗と閉
塞に対処するには、構造が簡単でオイルノズル径の大き
い外部混気式バーナーが好適である0か5る大口径バー
ナーであればスラグの吐出速度が遅くノズルの磨耗を防
止できる。
Furthermore, in order to deal with the abrasion and clogging of the burner oil nozzle caused by slag, an external mixture burner with a simple structure and a large oil nozzle diameter is suitable. is slow and prevents nozzle wear.

次に、本発明を実施する場合の処理工程を第5図の例に
従って説明する。
Next, processing steps for carrying out the present invention will be explained according to the example shown in FIG.

まずコークス工場で発生し常温では固化状態のタールス
ラグを第1の加熱器で加温し、粉砕機に装入可能な粘度
にする。
First, tar slag, which is generated in a coke factory and is solidified at room temperature, is heated in a first heater to a viscosity that can be charged into a crusher.

この粘度はポンプ移送可能な粘度にはゾ等しく、500
cst以下であればよい0 従って、スラグ温度は第2図に示すように50℃以上と
なるが、80℃以上では臭気の発生が著るしくなるため
、50〜80℃の範囲が粉砕に適した温度といえる。
This viscosity is equal to the pumpable viscosity of 500
Therefore, the slag temperature should be 50°C or higher as shown in Figure 2, but if it is 80°C or higher, odor will be generated significantly, so a range of 50 to 80°C is suitable for pulverization. It can be said that the temperature is

次に加温されたスラグを粉砕するが、スラグの飛散や臭
気発生等環境汚染のおそれのある解放式粉砕機よりも、
振動ミル又は回転砥石等の準密閉式粉砕機を使用するの
が望ましい。
The heated slag is then crushed, but compared to an open type crusher, which has the risk of environmental pollution such as slag scattering and odor generation.
It is preferable to use a semi-closed crusher such as a vibratory mill or a rotary grindstone.

粉砕粒度は装置の磨耗、閉塞及び固形物の燃焼状態によ
り制約されるが、装置の磨耗、閉塞はダイヤフラム型ポ
ンプと外部混気式バーナーの採用が適切であり、固形分
の燃焼状態については前記の如く固形物の粒度を149
μ以下90%以上とすることで解決し得る。
The pulverized particle size is limited by equipment wear and blockage, and the combustion state of solids, but it is appropriate to use a diaphragm pump and an external mixture burner to prevent equipment wear and blockage. If the particle size of the solid is 149,
This can be solved by setting μ to 90% or more.

このようにして粉砕されたスラグを一旦ストレージタン
クに送り保温、攪拌状態で貯蔵した後、ポンプで第2の
加熱器に送り80〜120℃に加温する。
The slag pulverized in this way is once sent to a storage tank and stored in a warm and stirred state, and then sent to a second heater using a pump and heated to 80 to 120°C.

なお、第2の加熱器でスラグを80〜120℃にする理
由は先に述べたが、特に最高温度(120℃)について
は前記理由以外に次の制約があるためである。
The reason why the slag is heated to 80 to 120° C. in the second heater is as described above, but especially regarding the maximum temperature (120° C.), there is the following restriction in addition to the above reason.

即ち、スラグ中には水分及び低沸騰点有機物が存在しi
oo℃前後で沸騰現象が始まるため、低油圧を特徴とす
る外部混合式バーナーでは脈動現象を引きおこして不完
全燃焼の一因となるからであり、実験による最高許容温
度は約120℃であったことによる。
That is, water and low boiling point organic matter are present in the slag.
This is because the boiling phenomenon begins at around 00°C, which causes pulsation in external mixing burners characterized by low oil pressure, which contributes to incomplete combustion, and the maximum allowable temperature according to experiments is about 120°C. It depends on what happened.

かくして80−120℃に加温されたタールスラグは、
空気を導入した外部混気式バーナーを完全燃焼するもの
であり、例えばロータリーキルンの如き工業窯炉の燃料
として何等問題なく使用できる。
The tar slag heated to 80-120°C in this way is
It completely burns an external air mixture type burner into which air is introduced, and can be used without any problems as a fuel for industrial furnaces such as rotary kilns.

実施例 1 タールスラグの温度が燃焼に及ぼす影響を調べるため、
原タールスラジを振動ミルで粒度149μ以下96.5
%に微粉砕したものを外部混気式バーナーで燃焼させた
結果を第2表に示すが、タールスラグ温度が80〜12
0℃であれば長期使用に耐えることが判明した。
Example 1 To investigate the effect of tar slag temperature on combustion,
Raw tar sludge is processed into a vibration mill to reduce the particle size to 149μ or less, 96.5
Table 2 shows the results of burning the finely pulverized material in an external air mixture burner.
It was found that it could withstand long-term use at 0°C.

実施例 2 タールスラジの粒度が燃焼に及ぼす影響を調べるため、
粒度149μ以下が86.5,91.2゜96.5%の
3種について温度lOO℃一定として外部混気式バーナ
ーで燃焼させた結果を第3表に示す。
Example 2 In order to investigate the influence of tar sludge particle size on combustion,
Table 3 shows the results of combustion in an external air mixture burner at a constant temperature of 100° C. for three types of particles having a particle size of 149 μm or less: 86.5, 91.2°, and 96.5%.

これによればタール滓粒度149μ以下が90%以上あ
れば炉体の損傷を伴わず工業的な長期使用に耐えること
が判る。
According to this, it can be seen that if the tar slag particle size is 149μ or less in 90% or more, it can withstand long-term industrial use without causing damage to the furnace body.

実施例 3 原タールスラジを振動ミルで粒度149μ以下96.5
%jこ微粉砕したものを供試材料として、従来の燃焼装
置と本発明で適用した燃焼装置における磨耗と閉塞の状
況を第4表に示す。
Example 3 Raw tar sludge was milled with a vibration mill to a particle size of 149μ or less, 96.5
Table 4 shows the state of wear and clogging in the conventional combustion device and the combustion device applied in the present invention using the pulverized material as a test material.

実験の結果、従来装置では磨耗と閉塞が激しくタールス
ラジを安定して燃焼させることができなかったのに対し
、本発明を適用した燃焼装置では200時間運転後もタ
ールスラジは完全に燃焼し装置の磨耗、閉塞は無かった
As a result of experiments, it was found that the conventional equipment was not able to stably burn tar sludge due to severe wear and blockage, whereas the combustion equipment to which the present invention was applied was able to completely burn tar sludge even after 200 hours of operation, and the equipment did not wear out. , there was no occlusion.

上記のとおり本発明によれば、従来原料炭に混入するか
タール中に分散させざるを得なかったタールスラジを、
そのまま単独で工業窯炉の燃料として活用でき、廃棄物
の有効活用と環境汚染の防止を同時に満足させることが
できる。
As described above, according to the present invention, tar sludge, which conventionally had to be mixed into coking coal or dispersed in tar, can be removed.
It can be used on its own as a fuel for industrial kilns, making effective use of waste and preventing environmental pollution at the same time.

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

第1図は各バーナー型式における油粘度と油噴霧粒径の
関係図、第2図はタールスラジ粘度の温度依存性を示す
図、第3図は石炭粒の燃焼所要時間を示す図、第4図は
窯炉温度と石炭粒の燃焼速度の関係図、第5図は本発明
の一実施例を示す処理工程図である。
Figure 1 is a diagram showing the relationship between oil viscosity and oil spray particle size for each burner type, Figure 2 is a diagram showing the temperature dependence of tar sludge viscosity, Figure 3 is a diagram showing the time required to burn coal particles, and Figure 4 is a diagram showing the temperature dependence of tar sludge viscosity. 5 is a diagram showing the relationship between the furnace temperature and the combustion rate of coal grains, and FIG. 5 is a processing process chart showing an embodiment of the present invention.

Claims (1)

【特許請求の範囲】[Claims] 1 タールスラグを微粉砕して内在する可燃性固形物の
粒度が149μ以下を90%以上とせしめた後、80〜
120℃に加熱してバーナーにより燃焼させることを特
徴とする、タールスラグの燃料化方法。
1 After finely pulverizing tar slag to make the particle size of the combustible solids contained within 149μ or less 90% or more,
A method for converting tar slag into fuel, the method comprising heating it to 120°C and burning it with a burner.
JP53139495A 1978-11-13 1978-11-13 How to turn tar sludge into fuel Expired JPS5844114B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP53139495A JPS5844114B2 (en) 1978-11-13 1978-11-13 How to turn tar sludge into fuel

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP53139495A JPS5844114B2 (en) 1978-11-13 1978-11-13 How to turn tar sludge into fuel

Publications (2)

Publication Number Publication Date
JPS5566992A JPS5566992A (en) 1980-05-20
JPS5844114B2 true JPS5844114B2 (en) 1983-09-30

Family

ID=15246591

Family Applications (1)

Application Number Title Priority Date Filing Date
JP53139495A Expired JPS5844114B2 (en) 1978-11-13 1978-11-13 How to turn tar sludge into fuel

Country Status (1)

Country Link
JP (1) JPS5844114B2 (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS60110787A (en) * 1983-11-18 1985-06-17 Fuji Sekiyu Kk Fine fuel powder
KR100395215B1 (en) * 2001-05-02 2003-08-21 재원산업 주식회사 manufacturing method of revival change fuel
JP5462503B2 (en) * 2009-03-09 2014-04-02 新日鐵住金株式会社 Recycling method of tar sludge discharged from coke oven

Also Published As

Publication number Publication date
JPS5566992A (en) 1980-05-20

Similar Documents

Publication Publication Date Title
JP2607424B2 (en) Use of low-grade coal and peat
CN107513450B (en) A kind of coke-removing agent, the system and preparation method for preparing coke-removing agent
CN110107890B (en) Method for preventing circulating fluidized bed boiler from coking
JP2009191085A (en) Method and system for manufacturing solid fuel, and solid fuel
JPS5844114B2 (en) How to turn tar sludge into fuel
JP5582685B2 (en) Solid fuel and method for producing solid fuel
JPS5916589B2 (en) How to treat oil sand bits
JP2002020771A (en) How to treat waste wood
JPH05208183A (en) Treatment for gasifying plastic waste
JPS5913823A (en) Incineration of waste ion exchange resin
RU2185421C2 (en) Powdered coal fuel and method for production thereof
JP3112854B2 (en) Activated carbon sludge incineration method
FR2691524A1 (en) Disposal of radioactive graphite without contaminating environment - by pulverising, mixing with water and burning, then purifying combustion gases and recycling unburnt solids
CN107488480A (en) Particulate sludge fuel and its production method
CN110358581A (en) A kind of aqueous dregs of fat are granulated again the device and method of pyrolytic gasification
JP6203698B2 (en) Production method of ashless coal
JP2009228945A (en) Processing method and device of petroleum refining residue
SU827533A1 (en) Method of producing smokeless solid fuel coal (preferably from brown coal)
KR101344724B1 (en) A gasification method
JPH10227426A (en) Method and apparatus for treating combustible component-containing waste
JPH09157666A (en) Fuel composition
JPS60110787A (en) Fine fuel powder
KR101299531B1 (en) A method for gasification
JPS5818013A (en) Combustion method of coal-water slurry fuel
JPH0742465B2 (en) Method for producing slurry containing waste plastic