JPH0362753B2 - - Google Patents
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- Publication number
- JPH0362753B2 JPH0362753B2 JP57194128A JP19412882A JPH0362753B2 JP H0362753 B2 JPH0362753 B2 JP H0362753B2 JP 57194128 A JP57194128 A JP 57194128A JP 19412882 A JP19412882 A JP 19412882A JP H0362753 B2 JPH0362753 B2 JP H0362753B2
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- Prior art keywords
- solvent
- deashing
- hydrogenation
- coal
- src
- 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 - Lifetime
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Description
本発明は、直接水添液化法、特に2段水添法に
よつて石炭を効率良く液化する方法に関し、詳細
には1次水添後における溶剤精製炭(SRC)の
脱灰効率を高めることによつて2次水添の効果を
有効に発揮せしめる様な脱灰技術を組込んだ石炭
液化法に関するものである。
この種の脱灰技術としては、(1)過法、遠心分
離法、重力沈降法、蒸留法等の機械的分離法と、
(2)特殊な溶剤を加えて沈降速度を促進する溶剤分
離法の2種類が知られている。しかし脱灰効率と
装置経済の両面を総合的に評価すると、溶剤分離
法の方が有利と判断され、現在では溶剤分離法が
脱灰技術開発の主流となりつつある。そして既に
開発されているものの代表例として、ルーマス
(Lummus)社のアンチ・ソルベント法
(Antisolvent法)とカーマギー(Kerr−McGee)
社のクリテイカル・ソルベント法(Critical
solvent法)がある。まずアンチ・ソルベント法
では、1次水添溶剤の高沸点側留分で溶解した
SRC溶液に、沸点170〜400℃の石油系脱灰溶剤
(アンチ・ソルベント)を混合し、十分溶解させ
たのち沈降槽に送り込んで沈降分離させ頂部より
精製SRC溶液を、又底部よりスラツジと灰分に
富んだ溶液を夫々分離し、これらを蒸留塔に送つ
て精留し、溶剤、精SRC及び脱灰スラツジに分
離している。しかしこのプロセスは、石油系の比
較的高沸点領域の脱灰溶剤を使用する点に特徴が
あり、且つ蒸留による溶剤分離法を採用している
ため、経済性において問題があり溶剤使用量にも
自ずと制限がある。その為沈降槽内での溶液の粘
度は後述のクリテイカル・ソルベント法に比較し
て大きく、従つてスラツジの沈降速度が小さくな
り、装置が大形化する欠点がある。又石油系の溶
剤を使用するものであるから商業プラントの建設
場所に制限を受けるという問題もある。
一方クリテイカル・ソルベント法ではピリジ
ン、ベンゼン、トルエン等の単環式芳香族化合物
を脱灰溶剤として使用し、灰分の沈降分離を溶剤
の臨界点に近い状態で行ない、次いで溶液の温度
及び圧力条件を臨界点に調節することにより、蒸
発潜熱を与えることなしに溶剤を分離回収してい
る。このプロセスは溶剤の回収に膨大なエネルギ
ーを必要としないという利点があるから、多量の
溶剤を使用することができる。しかも溶剤自体が
低分子量であり、且つ脱灰操作が臨界温度に近い
高温で行なわれるなどの理由により、沈降槽内で
のスラツジの沈降速度は極めて早く、従つて沈降
槽も非常に小形化することができるという利点は
ある。しかしプロセスの特性から脱灰SRC中の
アスフアルト分などの残留量が多くなるので2次
水添の効率が悪くなると共に、上記の如き臨界点
での温度や圧力の調整操作が困難であるところか
ら2段水添法の効果を有効に発揮せしめるには至
つていない。更に上記のいずれの方法において
も、分離されたスラツジに同伴してSRCの一部
がロスされるので、収率上も問題がある。
本発明はこうした事情に着目してなされたもの
でその目的とするところは、特別困難な操作をす
ることなく分離沈降速度を大きくとることがで
き、同時にアスフアルテン等の様に2次水添が困
難な大分子量物質(縮合多環式芳香族化合物等)
の分離を可能として2次水添を容易ならしめ、も
つて2段水添法の効果を有効に発揮せしめ得る脱
灰技術を組込んだ石炭液化方法を提供しようとす
るにある。
しかしてこの様な目的を達成し得た本発明の石
炭液化方法とは、原料石炭に溶剤を混合して得ら
れるスラリーを、高温高圧下及び触媒の存在下
で、1次水添に付し、ここに得られたSRCを、
該SRC中の灰分を溶媒中で沈降除去した後、更
に水素化分離能の高い金属触媒の存在下及び高温
高圧下で2次水添に付して軽質油を得る石炭の液
化方法において、前記SRC中の灰分除去工程に
添加すべき溶媒として、1次水添生成物を蒸留し
て得られる留分のうち、180℃以下の温度で留出
するナフサ分を循環使用する点に要旨が存在す
る。
以下実施例を示すフローに基づいて本発明の構
成及び作用効果を明らかにするが、これらの説明
によつて本発明の適用対象や実施態様が制限を受
けることはなく、前・後記の趣旨に反しない程度
の変更実施は全て本発明の技術的範囲に含まれ
る。
本1図は本発明の工程概要を示すブロツクフロ
ー図で、四角枠は処理内容、括弧書きは物質を表
わしている。即ち褐炭等の原料石炭に溶剤を混合
して得られるスラリーが、必要に応じて予熱を受
け、高温高圧下及び触媒の存在下で1次水添を受
ける。スラリー化溶剤の種類や添加量、予熱や1
次水添反応の条件、触媒の種類や量等は本発明の
制限的要件ではない。1次水添が行なわれた後、
必要により減圧下に気液分離を行ない、次いで蒸
留(1)を行なうが、ここでは平衡溶媒が回収され、
SRCが生成すると同時にナフサ(一般に180℃以
下の沸点を有する芳香族化合物、ナフテン類及び
パラフイン類等からなる混合油)が得られる。従
来はこのナフサを、製品として回収するだけであ
つたが、本発明ではその一部を脱灰溶媒として循
環使用する点にポイントがある。
即ち蒸留(1)によつて得られたSRC中には前述
の様に灰分が含まれて2次水添の効率に悪影響を
及ぼすので、前述の如き脱灰技術の研究が展開さ
れているが、本発明は溶剤中における灰分の沈降
分離法に準拠するものであつて、蒸留(1)で得られ
たナフサの一部を脱灰溶媒としてSRCに加える。
尚脱灰後に改めて蒸留(2)を行ない、脱灰時に加え
たナフサを回収する工程を付加する場合には、回
収されたナフサを脱灰溶媒として脱灰工程に供給
することもでき、茲に矢印Aで示す様なクローズ
ドシステムが形成される。従つて本プロセスの実
操業に当つては、最初の内は蒸留(1)で得たナフサ
だけで脱灰溶媒をまかなう必要があるが、一定の
ランニング状態に入れば、クローズドシステムA
によつて脱灰溶媒が循環供給されるので、蒸留(1)
からのナフサ供給は、単なる補給程度と考えても
良い。
蒸留(1)及び蒸留(2)の条件は本発明において制限
的に解釈される必要はなく、沸点180℃以下のナ
フサ分を効率的に回収できる方法でありさえすれ
ばどの様な方法でも良いが、第1図からも理解さ
れる様に、少なくともナフサ分(低温留分)、平
衡溶媒(中温留分)及びSRC(高温留分)に分留
できるものであることが望まれる。又脱灰条件に
ついても特段の制限を受けることは無いが、種々
研究したところでは、次に示す条件範囲を最適範
囲として推奨することができる。
温度:150〜400℃
更に好ましくは280〜350℃
圧力:20〜60Kg/cm2
脱灰溶媒量:SRC量に対して2〜20倍更に好ま
しくは2.5〜4倍(重量比)
上記の推奨範囲を外れても本発明の実施が不可
能になるという訳ではないが、温度及び圧力の相
関々係において、溶媒の臨界点に近い状態で脱灰
を行なわしめ、且つ蒸留(2)において溶液の温度及
び圧力を臨界点に調節して溶媒を回収するという
組合わせを採用するのが最適である。しかして
150℃未満、圧力60Kg/cm2超では、沈降槽内での
スラツジの沈降速度が遅くなり、400℃超、圧力
20Kg/cm2未満では溶媒の対流が生じてスラツジの
沈降を妨げるというきらいがある。又脱灰溶媒量
がSRC量に対して2倍未満のときはスラツジと
SRCの分離が不十分であり、逆に20倍を越えて
も両者の分離能力はそれ以上改善されず却つて蒸
留(2)におけるナフサの回収コストを高騰させるだ
けであつて好ましいことではない。
次に水添条件は本発明の制限要件ではなく、原
料炭の性状、平衡溶媒の種類や量、H2の消費量、
触媒の種類等を勘案して種々検討すれば良いが、
代表的な条件を例示すると次の通りである。
<1次水添>
温度:430〜480℃
圧力:150〜280Kg/cm2G
触媒:Fe2O3
水添度:3〜4%
<2次水添>
温度:400℃以下
圧力:150〜280Kg/cm2G
触媒:Co−Mo系、Ni−Mo系等の金属触媒
水添度:3〜4%
次に本発明の実施例を説明する。
1次水添によつて得られたSRC中に15重量%
相当の灰分が含まれている場合において、この
SRCを50mmφの沈降槽に導入し、蒸留(1)又は蒸
留(2)でにおいて180℃で蒸留カツトして得たナフ
サ(該ナフサの蒸留曲線は第2図に示す通りであ
り、このうち初留から180℃までに留出する留分)
をSRCの4倍(重量比)加え、温度:300℃、流
量70/hr、沈降速度:61cm/minで脱灰を行な
つた。尚比較の為に同条件下でナフサをトルエ
ン、ベンゼン、ケロシン(いずれも試薬)に置き
換えて脱灰を行なつた。脱灰後のSRC中に含ま
れる灰分量は、第1表に示す通りであつた。
The present invention relates to a method for efficiently liquefying coal by a direct hydrogenation liquefaction method, particularly a two-stage hydrogenation method, and more specifically, a method for efficiently liquefying coal by increasing the deashing efficiency of solvent refined coal (SRC) after primary hydrogenation. The present invention relates to a coal liquefaction method that incorporates deashing technology that effectively brings out the effects of secondary hydrogenation. This type of deashing technology includes (1) mechanical separation methods such as filtration, centrifugation, gravity sedimentation, and distillation;
(2) Two types of solvent separation methods are known in which a special solvent is added to accelerate the sedimentation rate. However, after comprehensively evaluating both deashing efficiency and equipment economy, it was determined that the solvent separation method is more advantageous, and the solvent separation method is now becoming the mainstream in the development of deashing technology. Representative examples of those that have already been developed include Lummus' anti-solvent method and Kerr-McGee's anti-solvent method.
Critical Solvent Method
solvent method). First, in the anti-solvent method, the high-boiling fraction of the primary hydrogenated solvent is used to dissolve
A petroleum-based deashing solvent (anti-solvent) with a boiling point of 170 to 400°C is mixed with the SRC solution, and after it is sufficiently dissolved, it is sent to a sedimentation tank where it settles and separates.The purified SRC solution is collected from the top, and the sludge and ash are collected from the bottom. The solutions rich in SRC are separated and sent to a distillation column for rectification and separated into solvent, purified SRC and demineralized sludge. However, this process is characterized by the use of a petroleum-based deashing solvent with a relatively high boiling point, and because it employs a solvent separation method by distillation, there are problems with economic efficiency and the amount of solvent used is limited. There are limits of course. Therefore, the viscosity of the solution in the sedimentation tank is higher than that in the critical solvent method described below, which results in a lower sedimentation rate of the sludge and a disadvantage that the apparatus becomes larger. Furthermore, since petroleum-based solvents are used, there is a problem in that there are restrictions on where commercial plants can be constructed. On the other hand, in the critical solvent method, a monocyclic aromatic compound such as pyridine, benzene, or toluene is used as a deashing solvent, and the ash is separated by precipitation near the critical point of the solvent, and then the temperature and pressure conditions of the solution are adjusted. By adjusting the temperature to the critical point, the solvent can be separated and recovered without imparting latent heat of vaporization. This process has the advantage that solvent recovery does not require large amounts of energy, so large amounts of solvent can be used. Moreover, because the solvent itself has a low molecular weight and the deashing operation is carried out at a high temperature close to the critical temperature, the settling speed of the sludge in the settling tank is extremely fast, and the settling tank is also extremely small. There are advantages to being able to do so. However, due to the characteristics of the process, the residual amount of asphalt in the deashing SRC increases, which reduces the efficiency of secondary hydrogenation, and makes it difficult to adjust the temperature and pressure at the critical point as described above. The effects of the two-stage hydrogenation method have not yet been effectively demonstrated. Furthermore, in any of the above methods, a portion of the SRC is lost along with the separated sludge, which poses a problem in terms of yield. The present invention was developed in view of these circumstances, and its purpose is to be able to increase the separation and sedimentation rate without any particularly difficult operations, and at the same time, it is difficult to perform secondary hydrogenation, such as with asphaltenes. large molecular weight substances (fused polycyclic aromatic compounds, etc.)
The purpose of the present invention is to provide a coal liquefaction method that incorporates deashing technology that enables the separation of coal, facilitates secondary hydrogenation, and effectively exhibits the effects of the two-stage hydrogenation method. However, the coal liquefaction method of the present invention that has achieved these objectives involves subjecting the slurry obtained by mixing raw coal with a solvent to primary hydrogenation at high temperature and pressure in the presence of a catalyst. , the SRC obtained here is
In the coal liquefaction method for obtaining light oil by removing the ash content in the SRC by sedimentation in a solvent, and then subjecting it to secondary hydrogenation in the presence of a metal catalyst with high hydrogenation separation ability and under high temperature and high pressure. The key point lies in the recycling and use of the naphtha fraction distilled at a temperature of 180°C or less among the fractions obtained by distilling the primary hydrogenated product as a solvent to be added to the ash removal process during SRC. do. The configuration and effects of the present invention will be clarified below based on the flowchart showing the examples, but the scope of application and embodiments of the present invention will not be limited by these explanations, and the purpose of the above and below will not be limited. All modifications that do not violate the scope of the present invention are included in the technical scope of the present invention. Figure 1 is a block flow diagram showing an outline of the process of the present invention, with square frames representing processing details and parentheses representing substances. That is, a slurry obtained by mixing raw coal such as lignite with a solvent is preheated as necessary and subjected to primary hydrogenation at high temperature and pressure in the presence of a catalyst. The type and amount of slurry-forming solvent, preheating and
The conditions for the subsequent hydrogenation reaction, the type and amount of the catalyst, etc. are not limiting requirements of the present invention. After primary hydrogenation is carried out,
If necessary, gas-liquid separation is performed under reduced pressure, followed by distillation (1), in which the equilibrium solvent is recovered,
At the same time as SRC is produced, naphtha (generally a mixed oil consisting of aromatic compounds, naphthenes, paraffins, etc. having a boiling point of 180°C or less) is obtained. Conventionally, this naphtha was simply recovered as a product, but the key point of the present invention is that a portion of it is recycled and used as a deashing solvent. That is, as mentioned above, the SRC obtained by distillation (1) contains ash, which has a negative effect on the efficiency of secondary hydrogenation, so research on deashing technology as mentioned above is being carried out. The present invention is based on a method of sedimentation separation of ash in a solvent, and a part of the naphtha obtained in distillation (1) is added to SRC as a deashing solvent.
In addition, when performing distillation (2) again after deashing and adding a step to recover the naphtha added during deashing, the recovered naphtha can be supplied to the deashing process as a deashing solvent, and the A closed system as shown by arrow A is formed. Therefore, in the actual operation of this process, it is necessary to initially supply the deashing solvent only with the naphtha obtained from distillation (1), but once a certain running state is reached, the closed system A
Distillation (1)
The supply of naphtha from can be considered as mere replenishment. The conditions for distillation (1) and distillation (2) do not need to be interpreted in a restrictive manner in the present invention, and any method may be used as long as it is a method that can efficiently recover naphtha components with a boiling point of 180°C or less. However, as can be understood from FIG. 1, it is desirable that the product can be fractionated into at least a naphtha fraction (low temperature fraction), an equilibrium solvent (medium temperature fraction), and SRC (high temperature fraction). Further, there are no particular restrictions on demineralization conditions, but after various studies, the following condition range can be recommended as the optimum range. Temperature: 150 to 400°C, more preferably 280 to 350°C Pressure: 20 to 60 Kg/cm 2 Amount of deashing solvent: 2 to 20 times the amount of SRC, more preferably 2.5 to 4 times (weight ratio) Above recommended range This does not mean that it is impossible to carry out the present invention even if the temperature and pressure are outside the range, but due to the relationship between temperature and pressure, deashing is carried out near the critical point of the solvent, and the solution is removed during distillation (2). It is best to employ a combination of adjusting the temperature and pressure to a critical point and recovering the solvent. However
At temperatures below 150℃ and pressures above 60Kg/ cm2 , the settling speed of the sludge in the settling tank becomes slow;
If it is less than 20 Kg/cm 2 , there is a tendency that convection of the solvent occurs and prevents the settling of the sludge. In addition, if the amount of deashing solvent is less than twice the amount of SRC, it will be treated as sludge.
Separation of SRC is insufficient, and conversely, even if the separation capacity exceeds 20 times, the separation ability between the two will not be improved any further, and the cost of recovering naphtha in distillation (2) will only increase, which is not desirable. Next, the hydrogenation conditions are not a limiting requirement of the present invention, but include the properties of the coking coal, the type and amount of the equilibrium solvent, the consumption of H2 ,
Various considerations should be made, taking into account the type of catalyst, etc.
Typical conditions are as follows. <Primary hydrogenation> Temperature: 430~480℃ Pressure: 150~280Kg/ cm2G Catalyst: Fe 2 O 3 Hydrogenation degree: 3~4% <Secondary hydrogenation> Temperature: 400℃ or less Pressure: 150~ 280 Kg/cm 2 G Catalyst: Metal catalyst such as Co-Mo type or Ni-Mo type Hydrogenation degree: 3 to 4% Next, examples of the present invention will be described. 15% by weight in SRC obtained by primary hydrogenation
In cases where a considerable amount of ash is contained, this
Naphtha was obtained by introducing SRC into a 50 mm diameter settling tank and distilling it at 180°C in distillation (1) or distillation (2) (the distillation curve of this naphtha is as shown in Figure 2; Distillate up to 180℃)
was added in an amount four times that of SRC (weight ratio), and deashing was carried out at a temperature of 300°C, a flow rate of 70/hr, and a sedimentation rate of 61 cm/min. For comparison, deashing was carried out under the same conditions by replacing naphtha with toluene, benzene, and kerosene (all reagents). The amount of ash contained in SRC after deashing was as shown in Table 1.
【表】
即ちナフサを用いたものでは、脱灰効率が十分
に改善されており、2次水添効率の向上に寄与す
るところが大きい。特にトルエンやベンゼン、あ
るいはケロシンに比べて灰分量を200ppmも減少
させているということは、ベンゼン不溶分やヘキ
サン不溶分(アスフアルテン等の縮合多環式芳香
族化合物類を含む)の分離にも有効であることを
意味し、この面からも2次水添率の向上に資する
ところが大きい。
本発明は上記の如く構成されているので、プロ
セス中の生成産物を脱灰溶媒として循環的に使用
でき、ランニングコストの低減を図ることができ
るだけでなく、SRC中の脱灰効率が向上し、且
つ2次水添効率の向上に寄与することができた。[Table] That is, in the case of using naphtha, the deashing efficiency has been sufficiently improved, and this greatly contributes to improving the secondary hydrogenation efficiency. In particular, the fact that the ash content is reduced by 200 ppm compared to toluene, benzene, or kerosene is effective for separating benzene-insoluble components and hexane-insoluble components (including fused polycyclic aromatic compounds such as asphaltene). This means that, from this point of view, it greatly contributes to improving the secondary hydrogenation rate. Since the present invention is configured as described above, the product produced during the process can be used cyclically as a deashing solvent, which not only reduces running costs but also improves the deashing efficiency during SRC. Moreover, it was possible to contribute to improving the secondary hydrogenation efficiency.
第1図は本発明のプロセスを示すブロツクフロ
ー図、第2図は本発明で用いたナフサの蒸留曲線
を示す図である。
FIG. 1 is a block flow diagram showing the process of the present invention, and FIG. 2 is a diagram showing the distillation curve of naphtha used in the present invention.
Claims (1)
を、高温高圧下及び触媒の存在下で1次水添に付
し、茲に得られた溶剤精製炭を、該溶剤精製炭中
の灰分を溶媒中で沈降除去した後、更に水素化分
解能の高い金属触媒の存在下及び高温高圧下で2
次水添に付して軽質油を得る石炭の液化方法にお
いて、前記溶剤精製炭中の灰分除去工程で添加さ
れる溶媒として、1次水添生成物を蒸留して得ら
れる留分のうち180℃以下の温度で留出するナフ
サ分を循環使用することを特徴とする石炭の液化
方法。1. A slurry obtained by mixing raw coal with a solvent is subjected to primary hydrogenation at high temperature and pressure in the presence of a catalyst, and the ash content in the solvent-refined coal is removed from the solvent. After sedimentation and removal in
In the method of liquefying coal to obtain light oil by subjecting it to secondary hydrogenation, 180% of the fraction obtained by distilling the primary hydrogenation product is used as the solvent added in the ash removal step from the solvent-refined coal. A coal liquefaction method characterized by recycling naphtha fraction distilled at temperatures below ℃.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP19412882A JPS5984977A (en) | 1982-11-04 | 1982-11-04 | Liquefaction of coal |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP19412882A JPS5984977A (en) | 1982-11-04 | 1982-11-04 | Liquefaction of coal |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS5984977A JPS5984977A (en) | 1984-05-16 |
| JPH0362753B2 true JPH0362753B2 (en) | 1991-09-26 |
Family
ID=16319368
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP19412882A Granted JPS5984977A (en) | 1982-11-04 | 1982-11-04 | Liquefaction of coal |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS5984977A (en) |
Families Citing this family (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS6051784A (en) * | 1983-08-30 | 1985-03-23 | Kobe Steel Ltd | Method of liquefying brown coal |
| JPS6051785A (en) * | 1983-08-31 | 1985-03-23 | Kobe Steel Ltd | Method for liquefying brown coal by two-stage hydrogenation |
| CN103436280B (en) * | 2013-09-11 | 2015-11-04 | 神华集团有限责任公司 | Coal directly-liquefied residue is utilized to prepare the method for coke |
Family Cites Families (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS5681390A (en) * | 1979-12-07 | 1981-07-03 | Chiyoda Chem Eng & Constr Co Ltd | Multistage hydrogenation treatment of coal |
| JPS5761084A (en) * | 1980-09-30 | 1982-04-13 | Kobe Steel Ltd | Liquefaction of coal |
-
1982
- 1982-11-04 JP JP19412882A patent/JPS5984977A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS5984977A (en) | 1984-05-16 |
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