JPH0819418B2 - Liquefaction method of coal - Google Patents
Liquefaction method of coalInfo
- Publication number
- JPH0819418B2 JPH0819418B2 JP2288124A JP28812490A JPH0819418B2 JP H0819418 B2 JPH0819418 B2 JP H0819418B2 JP 2288124 A JP2288124 A JP 2288124A JP 28812490 A JP28812490 A JP 28812490A JP H0819418 B2 JPH0819418 B2 JP H0819418B2
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- Prior art keywords
- ash
- solution
- settling tank
- concentration
- concentrated slurry
- Prior art date
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Description
【発明の詳細な説明】 (産業上の利用分野) 本発明は、石炭の液化方法に関し、詳細には褐炭等の
石炭の水添工程、水添生成物の蒸留工程、蒸留残渣の脱
灰処理工程を含む石炭の液化方法に関する。Description: TECHNICAL FIELD The present invention relates to a method for liquefying coal, and more particularly to a process for hydrogenating coal such as brown coal, a process for distilling a hydrogenated product, and a process for deashing a distillation residue. The present invention relates to a coal liquefaction method including a process.
(従来の技術) 石炭の液化方法は水添法が代表的である。この方法に
は、原料石炭をスラリー化溶剤及び触媒と共に粉砕混
合してスラリー化した後、1次水添塔に供給して水添
し、その水添生成物を蒸留塔で蒸留して軽質油、中質
油、蒸留残渣(灰分及び油成分の重質油を含有してい
る)に分離する1次水添法と、更に該蒸留残渣を脱灰
処理して灰分含有量を低減させた後、2次水添し、蒸留
する2次水添法と、更に該蒸留の残渣を水添し、蒸留
する多段水添法とがある。1次水添の触媒には通常鉄系
触媒、2次水添以降の水添用触媒にはNi−Mo系又はCo−
Mo系触媒が使用される。(Prior Art) A typical hydrogenation method is a liquefaction method of coal. In this method, raw coal is pulverized and mixed with a slurrying solvent and a catalyst to form a slurry, which is then supplied to a primary hydrogenation tower for hydrogenation, and the hydrogenated product is distilled in a distillation tower to produce light oil. First, a primary hydrogenation method of separating into a medium oil and a distillation residue (containing ash and heavy oil as an oil component), and further deashing the distillation residue to reduce the ash content. There are a secondary hydrogenation method of secondary hydrogenation and distillation, and a multistage hydrogenation method of further hydrogenating and distilling the residue of the distillation. The primary hydrogenation catalyst is usually an iron-based catalyst, and the hydrogenation catalysts after the secondary hydrogenation are Ni-Mo-based or Co-
Mo-based catalyst is used.
上記脱灰処理は溶剤脱灰処理方法により行われる場合
が多く、この脱灰処理方法は、第2図に示す如く、溶解
槽(1)で蒸留残渣を脱灰溶剤と混合し、高温高圧下で
蒸留残渣中の重質物を溶解して灰分及び不溶重質物が共
存する溶液と成し、連続的又は断続的に、該溶液を沈降
槽(2)に供給し、沈降槽(2)内で該溶液中の灰分及
び不溶重質物を沈降させ、沈降槽(2)下部に高灰分濃
度のスラリー状溶液(灰分濃縮スラリー)を形成させる
と共にその上部に低灰分濃度の溶液(灰分希釈液)を形
成させ、沈降槽(2)上部より灰分希釈液を抜き出し、
沈降槽(2)下部より灰分濃縮スラリーを抜き出す方法
によって行われる。The above-mentioned deashing treatment is often carried out by a solvent deashing treatment method. As shown in FIG. 2, this deashing treatment method involves mixing the distillation residue with a deashing solvent in a dissolution tank (1), In, the heavy substances in the distillation residue are dissolved to form a solution in which ash and insoluble heavy substances coexist, and the solution is continuously or intermittently supplied to the settling tank (2), and in the settling tank (2) The ash and insoluble heavy substances in the solution are allowed to settle, a slurry-like solution having a high ash concentration (ash concentrated slurry) is formed in the lower part of the settling tank (2), and a solution having a low ash concentration (ash diluted solution) is formed in the upper part thereof. Form, draw out the ash dilution liquid from the upper part of the sedimentation tank (2),
The ash concentrated slurry is extracted from the lower part of the settling tank (2).
上記灰分濃縮スラリーは、沈降槽(2)下部の抜き出
し口に管接続されたスラリー流通管を介して油分蒸発分
離装置に送給され、油分の重質及び溶剤を蒸発させ、灰
分及び不溶重質物と分離して回収される。The ash-concentrated slurry is fed to an oil evaporation separator through a slurry flow pipe connected to an outlet at the bottom of the settling tank (2) to evaporate the heavy oil and the solvent, and to remove the ash and insoluble heavy substances. It is separated and collected.
かかる脱灰処理方法において、沈降槽(2)下部の灰
分濃縮スラリーの灰分濃度が高く、略30%以上になる
と、該スラリー中の灰分が粘着性の重質物により接着さ
れて凝集塊化し、沈降槽(2)下部の抜き出し口や、ス
ラリー流通管内に付着し、更には詰まってスラリー流通
管等の閉塞が生じるようになる。又、上記灰分濃度が低
い場合は、沈降槽(2)内での灰分の沈降が充分でな
く、良好な灰分希釈液が得られていないことを暗示して
いる。そのため、沈降槽(2)下部の灰分濃縮スラリー
の灰分濃度目標値(所定値)は通常10%以上に設定され
る。In such a deashing method, when the ash concentration of the ash-concentrated slurry in the lower part of the settling tank (2) is high and is about 30% or more, the ash in the slurry is adhered by a sticky heavy substance to form an agglomerate and settle. It adheres to the outlet of the lower part of the tank (2) and the inside of the slurry flow pipe, and is further clogged to cause clogging of the slurry flow pipe and the like. Further, when the ash concentration is low, it implies that the ash is not sufficiently settled in the settling tank (2), and a good ash diluted solution is not obtained. Therefore, the ash concentration target value (predetermined value) of the ash concentrated slurry in the lower part of the settling tank (2) is usually set to 10% or more.
上記閉塞等の問題点の発生を防止するには、灰分濃縮
スラリーの灰分濃度を随時測定し、その濃度に応じて灰
分濃縮スラリーの抜き出し量や、沈降槽の温度等の脱灰
処理条件を調整する必要がある。従って、上記灰分濃縮
スラリーの灰分濃度の測定は極めて重要なことである。In order to prevent the occurrence of problems such as the above clogging, measure the ash concentration of the ash-concentrated slurry at any time, and adjust the deashing conditions such as the amount of ash-concentrated slurry withdrawn and the temperature of the sedimentation tank according to the concentration. There is a need to. Therefore, it is extremely important to measure the ash concentration of the ash-concentrated slurry.
上記沈降槽(2)下部の灰分濃縮スラリーの灰分濃度
の測定は、沈降槽(2)下部の灰分濃縮スラリーの一部
を採取し、JIS M−8812の灰分分析法により行われる。
即ち、採取スラリーをルツボ内に入れ加熱して蒸発乾固
し、その残渣(残留する灰分)を重量測定し、採取スラ
リーに占める割合を求める方法により行われている。The ash concentration of the ash concentrated slurry in the lower part of the settling tank (2) is measured by a part of the ash concentrated slurry in the lower part of the settling tank (2) and by the ash analysis method of JIS M-8812.
That is, the method is carried out by placing the sampled slurry in a crucible, heating it to evaporate it to dryness, weighing the residue (residual ash), and determining the proportion of the sampled slurry.
(発明が解決しようとする課題) ところが、前記従来の石炭の液化方法においては、沈
降槽下部の灰分濃縮スラリーの灰分濃度の測定に際し、
採取スラリーの蒸発乾固に長時間(略4時間)を要する
ので、灰分濃縮スラリーの灰分濃度の測定に長時間(4
時間以上)を要する。そのため、実際に沈降槽(2)下
部の灰分濃縮スラリーの灰分濃度がその所定値より低く
なり、脱灰処理に異常を来し始めている時点において、
該異常をその時点では全く把握し得ず、長時間経過後に
過去のこととして認識し得るだけである。(Problems to be solved by the invention) However, in the conventional coal liquefaction method, in measuring the ash concentration of the ash concentrated slurry in the lower part of the settling tank,
Since it takes a long time (approximately 4 hours) to evaporate and dry the collected slurry, it takes a long time (4 hours) to measure the ash concentration of the ash-concentrated slurry.
It takes more than time). Therefore, at the time when the ash concentration of the ash-concentrated slurry in the lower part of the settling tank (2) actually becomes lower than the predetermined value and the deashing process starts to become abnormal,
The abnormality cannot be grasped at that time at all, and can be recognized as a past thing after a long time has passed.
従って、灰分濃縮スラリーの灰分濃度をその所定値に
回復するための脱灰処理条件の調整が間に合わず、脱灰
処理異常に対する対策措置がとれない。そのためスラリ
ー中灰分の塊化、スラリー流通管等の閉塞の発生を防止
し得ない。又、所定の高灰分濃度の灰分濃縮スラリーが
得られているのかどうかも明確にし得ない。このよう
に、灰分濃縮スラリー抜き出し量等の脱灰処理条件を調
整するためのフイードバツク情報として有用な灰分濃度
を測定し得ないという問題点がある。Therefore, adjustment of the deashing treatment conditions for recovering the ash concentration of the ash-concentrated slurry to the predetermined value cannot be made in time, and countermeasures against abnormal deashing treatment cannot be taken. Therefore, it is not possible to prevent the ash content in the slurry from being agglomerated and the slurry flow pipe from being clogged. In addition, it cannot be clarified whether or not an ash-concentrated slurry having a predetermined high ash concentration is obtained. As described above, there is a problem that the ash concentration useful as feed back information for adjusting deashing conditions such as the amount of ash concentrated slurry withdrawn cannot be measured.
本発明はこの様な事情に着目してなされたものであっ
て、その目的は従来のものがもつ以上のような問題点を
解消し、脱灰処理の際の沈降槽下部の灰分濃縮スラリー
の灰分濃度を短時間に測定し得、灰分濃縮スラリー抜き
出し量等の脱灰処理条件を調整するためのフイードバツ
ク情報として有用な沈降槽下部灰分濃縮スラリーの灰分
濃度を早期に把握し得る石炭の液化方法を提供しようと
するものである。The present invention has been made by paying attention to such a situation, and its object is to solve the above-mentioned problems of the conventional one, and to provide an ash-concentrated slurry at the bottom of the sedimentation tank during deashing treatment. A coal liquefaction method that can measure the ash concentration in a short time and is useful as information on the feed back for adjusting deashing conditions such as the amount of ash concentrated slurry extracted Is to provide.
(課題を解決するための手段) 上記の目的を達成するために、本発明は次のような構
成の石炭の液化方法としている。(Means for Solving the Problems) In order to achieve the above object, the present invention provides a coal liquefaction method having the following configuration.
即ち、本発明に係る石炭の液化方法は、石炭を触媒及
び溶剤の共存下で水添する水添工程、その水添生成物を
蒸留して軽質油と、中質油と、重質物及び灰分を含む蒸
留残渣とに分離する蒸留工程、その蒸留残渣を脱灰溶剤
と混合し重質物を溶解して灰分及び不溶重質物が共存す
る溶液と成し、該溶液を沈降槽に供給し、沈降槽内で該
溶液中の灰分及び不溶重質物を沈降させ、沈降槽上部よ
り低灰分濃度の溶液を抜き出し、沈降槽上部より高灰分
濃度のスラリー状溶液を抜き出す脱灰処理工程を含む石
炭の液化方法において、前記脱灰処理の際に、前記沈降
槽下部の外側より内側の溶液に向けてγ線を照射し、沈
降槽下部内の溶液を透過し外側へ出てくるγ線量を測定
して該溶液の密度を求め、該密度より該溶液の灰分濃度
を求めることを特徴とする石炭の液化方法である。That is, the coal liquefaction method according to the present invention is a hydrogenation step of hydrogenating coal in the presence of a catalyst and a solvent, a light oil by distilling the hydrogenated product, a medium oil, a heavy oil, and an ash content. A distillation step of separating into a distillation residue containing, and the distillation residue is mixed with a deashing solvent to dissolve a heavy substance to form a solution in which ash and an insoluble heavy substance coexist, and the solution is supplied to a sedimentation tank and settled. Liquefaction of coal including a deashing treatment step in which ash and insoluble heavy substances in the solution are settled in the tank, a solution with a low ash content is extracted from the upper part of the settling tank, and a slurry-like solution with a high ash content is extracted from the upper part of the settling tank. In the method, at the time of the decalcification treatment, γ-rays are irradiated toward the solution inside from the outside of the lower part of the settling tank, and the γ-ray dose that passes through the solution in the lower part of the settling tank and goes out to the outside is measured. Characterized in that the density of the solution is obtained, and the ash concentration of the solution is obtained from the density. This is a coal liquefaction method.
(作 用) 本発明に係る石炭の液化方法は、前記の如く、脱灰処
理の際に、沈降槽下部の外側より内側の溶液に向けてγ
線を照射し、沈降槽下部内の溶液を透過し外側へ出てく
るγ線量を測定して該溶液の密度を求め、該密度より該
溶液の灰分濃度を求めるようにしている。(Operation) As described above, the coal liquefaction method according to the present invention, when performing the deashing process, the γ from the outside of the lower part of the sedimentation tank toward the inside
The density of the solution is determined by irradiating a ray, and the γ-ray amount that passes through the solution in the lower part of the settling tank and goes out to the outside is determined, and the ash concentration of the solution is determined from the density.
上記溶液、即ち沈降槽下部の灰分濃縮スラリーを透過
し外側へ出てくるγ線量(透過γ線量)は、灰分濃縮ス
ラリーの密度と負の相関関係にあるので、透過γ線量の
測定により灰分濃縮スラリーの密度を求めることができ
る。The γ-dose (permeation γ-dose) that permeates the above solution, that is, the ash-concentrated slurry in the lower part of the settling tank and goes out, has a negative correlation with the density of the ash-concentrated slurry. The density of the slurry can be determined.
このようにして求められる灰分濃縮スラリーの密度
は、該スラリー中の灰分の占める割合、即ち灰分濃度に
対応するので、灰分濃縮スラリーの密度の測定により灰
分濃縮スラリーの灰分濃度を求めることができる。The density of the ash-concentrated slurry thus obtained corresponds to the proportion of ash in the slurry, that is, the ash concentration. Therefore, the ash concentration of the ash-concentrated slurry can be calculated by measuring the density of the ash-concentrated slurry.
上記の如くγ線を照射し、透過γ線量を測定して密度
を求める計器としては、所謂γ線密度計と言われるもの
があり、かかる密度計によればγ線を照射すると略同時
に密度となって出力される。As an instrument for irradiating γ-rays as described above and measuring the transmitted γ-ray dose to obtain the density, there is a so-called γ-ray density meter. Will be output.
このように上記密度測定は瞬時にできる。又、灰分濃
縮スラリーの灰分濃度と密度との関係を予め求めておけ
ば、上記密度測定値から灰分濃縮スラリーの灰分濃度を
素早く求め得る。故に、灰分濃縮スラリーの灰分濃度を
極めて短時間に測定し得る。Thus, the density measurement can be done instantly. Further, if the relationship between the ash concentration and the density of the ash concentrated slurry is obtained in advance, the ash concentration of the ash concentrated slurry can be quickly obtained from the density measurement value. Therefore, the ash concentration of the ash concentrated slurry can be measured in a very short time.
又、上記灰分濃縮スラリーの灰分濃度は、灰分濃度が
5%以上であれば精度良く測定し得、一方灰分濃縮スラ
リーの灰分濃度の所定値は通常10%以上であるので、測
定精度上の問題はない。即ち、所定の灰分濃度になって
いるか否か、灰分濃度が所定値より低くなり、脱灰処理
に異常を来しているか否かの確認が可能であり、上記灰
分濃縮スラリー中灰分濃度の測定精度は充分である。Further, the ash concentration of the ash-concentrated slurry can be accurately measured if the ash concentration is 5% or more, while the predetermined value of the ash concentration of the ash-concentrated slurry is usually 10% or more. There is no. That is, it is possible to confirm whether or not the ash concentration is a predetermined ash concentration, the ash concentration is lower than a predetermined value, and there is an abnormality in the deashing treatment. The accuracy is sufficient.
故に、脱灰処理の際の沈降槽下部の灰分濃縮スラリー
の灰分濃度を極めて短時間にリアルタイムで測定し得、
従って、灰分濃縮スラリー抜き出し量等の脱灰条件を調
整するためのフイードバツク情報として有用な沈降槽下
部灰分濃縮スラリーの灰分濃度を早期に把握し得る。Therefore, it is possible to measure the ash concentration of the ash-concentrated slurry at the bottom of the settling tank during deashing in a very short time in real time.
Therefore, the ash concentration of the lower ash-concentrated slurry in the sedimentation tank, which is useful as feedback information for adjusting deashing conditions such as the amount of ash-concentrated slurry withdrawn, can be grasped at an early stage.
そのため、所定高灰分濃度の灰分濃縮スラリーが得ら
れているか否かを随時素早く確認し得るようになる。
又、沈降槽下部灰分濃縮スラリーの灰分濃度が低く、脱
灰処理に異常を来している時には、その異常をその時点
又はその直後に察知し得、従って、脱灰処理異常に対す
る対策措置を早期にとり得るようになる。例えば、灰分
濃縮スラリー抜き出し量を減少させたり、重質物の溶解
条件や沈降槽の温度を変化させる等の対策を早期に講じ
得るようになる。Therefore, whether or not the ash-concentrated slurry having a predetermined high ash concentration has been obtained can be quickly confirmed at any time.
In addition, when the ash concentration of the ash concentrated slurry in the lower part of the sedimentation tank is low and there is an abnormality in the deashing process, the abnormality can be detected at that time or immediately thereafter. Can be taken into account. For example, it becomes possible to take measures at an early stage such as reducing the amount of ash-concentrated slurry withdrawn, changing the conditions for dissolving heavy substances, and changing the temperature of the sedimentation tank.
従って、沈降槽下部の灰分濃縮スラリーの灰分濃度を
所定値に維持し易くなり、その結果灰分の凝集塊化、管
内への付着及び管内閉塞等のトラブルの発生を防止し得
るようになる。Therefore, the ash concentration of the ash-concentrated slurry in the lower part of the settling tank can be easily maintained at a predetermined value, and as a result, troubles such as ash agglomeration, sticking in the pipe, and clogging in the pipe can be prevented.
尚、前記灰分濃度測定は、連続してし得ると共に、分
析試料溶液を採取する必要がなく簡単にし得る。更には
自動測定も可能である。The ash concentration measurement can be performed continuously and can be simplified without the need to collect an analytical sample solution. Furthermore, automatic measurement is possible.
(実施例) 粉砕及び脱水された褐炭をスラリー化溶剤、鉄系触媒
及び溶融硫黄触媒と共に粉砕混合してスラリー化した
後、水添塔に供給して1次水添し、その水添生成物を蒸
留し軽質油、中質油、蒸留残渣に分離して得た。(Example) The pulverized and dehydrated brown coal is pulverized and mixed with a slurrying solvent, an iron-based catalyst and a molten sulfur catalyst to form a slurry, which is then supplied to a hydrogenation tower for primary hydrogenation, and its hydrogenated product. Was distilled to obtain light oil, medium oil, and distillation residue.
上記蒸留残渣の脱灰処理を下記の如く連続的に行っ
た。即ち、上記蒸溜残渣を粉砕後、第1図に示す如く、
溶解槽(1)に移し、蒸留残渣中重質物を溶解すべく脱
灰溶剤を添加し250℃で撹拌混合して灰分共存溶液と成
し、該溶液を連続的に、沈降槽(2)に供給し、沈降槽
(2)内で灰分及び不溶重質物を沈降させ、沈降槽
(2)下部に灰分濃縮スラリーを形成させると共にその
上部に灰分希釈液を形成させ、沈降槽(2)上部より灰
分希釈液を抜き出し、沈降槽(2)下部より灰分濃縮ス
ラリーを抜き出した。The above-mentioned distillation residue was continuously deashed as follows. That is, after pulverizing the distillation residue, as shown in FIG.
Transfer to a dissolution tank (1), add a deashing solvent to dissolve heavy substances in the distillation residue, stir and mix at 250 ° C to form an ash coexisting solution, and continuously add the solution to the sedimentation tank (2). Ash and insoluble heavy substances are settled in the settling tank (2), an ash concentrated slurry is formed in the lower part of the settling tank (2), and an ash diluting liquid is formed in the upper part of the settling tank (2). The ash diluted liquid was extracted, and the ash concentrated slurry was extracted from the lower part of the sedimentation tank (2).
上記脱灰処理の際に、γ線密度計により沈降槽(2)
下部の灰分濃縮スラリー灰分濃度を連続して求めた。即
ち、沈降槽(2)下部の外側からγ線照射手段(3)に
よりγ線を沈降槽(2)下部の灰分濃縮スラリーに向け
て照射し、透過γ線量をカウントし密度に変換して密度
表示する手段(4)により灰分濃縮スラリーの密度を測
定し、密度を灰分濃度に変換表示する手段(5)により
灰分濃縮スラリーの灰分農度を求めた。尚、予め、上記
手段(4)については透過γ線量と灰分濃縮スラリー密
度とを対応させるためのキャリブレーションを行い、
又、手段(5)については予め求めた灰分濃縮スラリー
の密度と灰分濃度との関係を入力しキャリブレーション
した。During the above deashing treatment, a settling tank (2) was used with a γ-ray density meter.
The lower ash concentrated slurry ash concentration was continuously determined. That is, from the outside of the lower part of the settling tank (2), γ-rays are irradiated to the ash-concentrated slurry in the lower part of the settling tank (2) by the γ-ray irradiation means (3), the transmitted γ-dose is counted, and the density is converted into the density. The density of the ash-concentrated slurry was measured by the displaying means (4), and the ash concentration of the ash-concentrating slurry was determined by the displaying means (5) by converting the density into the ash concentration. In addition, with respect to the above-mentioned means (4), calibration for making the transmitted γ dose correspond to the ash-concentrated slurry density is performed in advance,
For the means (5), the relationship between the density and the ash concentration of the ash-concentrated slurry obtained in advance was input and calibrated.
かかる測定によれば、γ線照射時から灰分濃度表示ま
での所要時間は1秒以内であり、連続して灰分濃度をリ
アルタイムで測定し得た。その結果沈降槽(2)下部の
灰分濃縮スラリーの灰分濃度は時々刻々と変動すること
が確認された。According to such measurement, the time required from γ-ray irradiation to ash concentration display is within 1 second, and the ash concentration can be continuously measured in real time. As a result, it was confirmed that the ash concentration of the ash concentrated slurry in the lower part of the settling tank (2) fluctuates from moment to moment.
上記灰分濃度の測定値によっては脱灰処理条件をその
都度調整した。即ち、灰分濃度の測定値が10%以上の場
合は脱灰処理条件を調整することなく一定に保持した
が、10%未満の場合にはその直後に沈降槽(2)への溶
液の供給量、沈降槽(2)上部からの灰分希釈液の抜き
出し量、及び、沈降槽(2)下部からの灰分濃縮スラリ
ーの抜き出し量を減少させ、次いで蒸留残渣と脱灰溶剤
との混合割合、混合温度や、沈降槽(2)の温度等の脱
灰処理条件を調整し、沈降槽(2)下部の灰分濃縮スラ
リーの灰分濃度を10%以上に回復させた。Depending on the measured value of the ash concentration, the deashing treatment conditions were adjusted each time. That is, when the measured ash concentration was 10% or more, the deashing conditions were kept constant without adjustment, but when it was less than 10%, the amount of solution supplied to the settling tank (2) immediately after that. The amount of the ash diluted liquid withdrawn from the upper part of the settling tank (2) and the amount of the ash concentrated slurry withdrawn from the lower part of the settling tank (2), and then the mixing ratio of the distillation residue and the deashing solvent and the mixing temperature. Alternatively, the deashing conditions such as the temperature of the sedimentation tank (2) were adjusted to recover the ash concentration of the ash-concentrated slurry in the lower part of the sedimentation tank (2) to 10% or more.
このように、沈降槽(2)下部の灰分濃縮スラリーの
灰分濃度が所定値(10%以上)になっているか否かをリ
アルタイムで素早く確認し得、又、灰分濃度が低く脱灰
処理異常である時にはその時に該異常を察知し、その対
策を早期に講じることができた。その結果、殆どの時期
において灰分濃縮スラリーの灰分濃度を所定値に維持し
得た。そのため、灰分の凝集塊化、管内への付着及び管
内閉塞等のトラブルの発生は全く認められなかった。一
方、沈降槽(2)上部より得られた灰分希釈液は灰分濃
度が低く(200ppm)、良好であった。In this way, it is possible to quickly confirm in real time whether the ash concentration of the ash-concentrated slurry in the lower part of the settling tank (2) has reached a predetermined value (10% or more). At some point, I was able to detect the anomaly at that time and take countermeasures early. As a result, the ash concentration of the ash-concentrated slurry could be maintained at a predetermined value at almost all times. Therefore, no trouble such as agglomeration of ash, adhesion to the inside of the pipe, and blockage in the pipe was observed. On the other hand, the ash diluted solution obtained from the upper part of the settling tank (2) had a low ash concentration (200 ppm) and was good.
(発明の効果) 本発明に係る石炭の液化方法によれば、脱灰処理の際
の沈降槽下部の灰分濃縮スラリーの灰分濃度を極めて短
時間に測定し得、灰分濃縮スラリー抜き出し量等の脱灰
処理条件を調整するためのフイードバツク情報として有
用な沈降槽下部灰分濃縮スラリーの灰分濃度を早期にリ
アルタイムで把握し得るようになる。又、上記灰分濃度
測定は連続してできると共に、分析試料溶液を採取する
必要がなく簡単にし得る。更には自動測定も可能であ
る。(Effects of the Invention) According to the coal liquefaction method of the present invention, the ash concentration of the ash concentrated slurry at the bottom of the sedimentation tank during deashing can be measured in an extremely short time, and the ash concentration slurry withdrawal amount and the like can be removed. The ash concentration of the lower ash concentrated slurry in the settling tank, which is useful as feed back information for adjusting ash treatment conditions, can be grasped in real time at an early stage. Further, the above ash concentration measurement can be continuously performed, and it is not necessary to collect an analytical sample solution, which can be simplified. Furthermore, automatic measurement is possible.
そのため、所定高灰分濃度の灰分濃縮スラリーが得ら
れているか否かを常に容易に素早く確認し得るようにな
る。又、沈降槽下部灰分濃縮スラリーの灰分濃度が低く
脱灰処理異常を来している時には、その異常をその時点
に察知し得、故に脱灰処理異常に対する対策措置を早期
に講じ得るようになる。従って、沈降槽下部の灰分濃縮
スラリーの灰分濃度を所定値に維持し易くなり、その結
果灰分の凝集塊化、管内への付着及び管内閉塞等のトラ
ブルの発生を防止し得るようになる。Therefore, it becomes possible to always easily and quickly confirm whether or not the ash concentrated slurry having a predetermined high ash concentration is obtained. Also, when the ash concentration in the lower ash concentration slurry of the settling tank is low and abnormalities in deashing process are occurring, the abnormalities can be detected at that time, and therefore countermeasures against abnormalities in deashing process can be taken early. . Therefore, the ash concentration of the ash-concentrated slurry in the lower part of the settling tank can be easily maintained at a predetermined value, and as a result, troubles such as ash agglomeration, sticking in the pipe, and clogging in the pipe can be prevented.
第1図は、本発明の実施例に係る石炭液化方法の脱灰処
理を説明するためのフローチャートの概要図、第2図
は、水添液化法による石炭の液化プロセスにおける蒸留
残渣の溶剤脱灰処理方法を説明するためのフローチャー
トの概要図である。 (1)……溶解槽、(2)……沈降槽、(3)……γ線
照射手段 (4)……透過γ線量を測定し密度変換表示する手段 (5)……密度を灰分濃度に変換表示する手段FIG. 1 is a schematic diagram of a flow chart for explaining the deashing process of the coal liquefaction method according to the embodiment of the present invention, and FIG. 2 is the solvent deashing of distillation residue in the coal liquefaction process by the hydrogenation liquefaction method. It is a schematic diagram of a flow chart for explaining a processing method. (1) …… Dissolution tank, (2) …… Settling tank, (3) …… γ-ray irradiation means (4) …… Means for measuring the transmitted γ-dose and displaying the density conversion (5) …… Density for ash concentration Means to convert and display
Claims (1)
添工程、その水添生成物を蒸留して軽質油と、中質油
と、重質物及び灰分を含む蒸留残渣とに分離する蒸留工
程、その蒸留残渣を脱灰溶剤と混合し重質物を溶解して
灰分が共存する溶液と成し、該溶液を沈降槽に供給し、
沈降槽内で該溶液中の灰分を沈降させ、沈降槽上部より
低灰分濃度の溶液を抜き出し、沈降槽下部より高灰分濃
度のスラリー状溶液を抜き出す脱灰処理工程を含む石炭
の液化方法において、前記脱灰処理の際に、前記沈降槽
下部の外側より内側の溶液に向けてγ線を照射し、沈降
槽下部内の溶液を透過し外側へ出てくるγ線量を測定し
て該溶液の密度を求め、該密度より該溶液の灰分濃度を
求めることを特徴とする石炭の液化方法。1. A hydrogenation step of hydrogenating coal in the coexistence of a catalyst and a solvent, and distilling the hydrogenated product to separate light oil, medium oil, and distillation residue containing heavy substances and ash. Distillation step to, the distillation residue is mixed with a deashing solvent to dissolve heavy substances to form a solution in which ash coexists, and the solution is supplied to a sedimentation tank,
In a liquefaction method of coal including a deashing treatment step of precipitating ash content in the solution in the settling tank, extracting a solution having a low ash content from the upper part of the settling tank, and extracting a slurry-like solution having a high ash content from the lower part of the settling tank, At the time of the decalcification treatment, γ-rays are radiated toward the solution inside the lower part of the settling tank from the outside, and the γ-ray dose that passes through the solution in the lower part of the settling tank and goes out to the outside is measured. A method for liquefying coal, characterized in that the density is obtained and the ash concentration of the solution is obtained from the density.
Priority Applications (2)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2288124A JPH0819418B2 (en) | 1990-10-24 | 1990-10-24 | Liquefaction method of coal |
| AU86045/91A AU627669B2 (en) | 1990-10-24 | 1991-10-22 | Method for liquifying coal |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2288124A JPH0819418B2 (en) | 1990-10-24 | 1990-10-24 | Liquefaction method of coal |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH04161490A JPH04161490A (en) | 1992-06-04 |
| JPH0819418B2 true JPH0819418B2 (en) | 1996-02-28 |
Family
ID=17726121
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP2288124A Expired - Lifetime JPH0819418B2 (en) | 1990-10-24 | 1990-10-24 | Liquefaction method of coal |
Country Status (2)
| Country | Link |
|---|---|
| JP (1) | JPH0819418B2 (en) |
| AU (1) | AU627669B2 (en) |
Family Cites Families (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US3856675A (en) * | 1972-11-07 | 1974-12-24 | Lummus Co | Coal liquefaction |
| US3852183A (en) * | 1972-12-29 | 1974-12-03 | Lummus Co | Coal liquefaction |
| US3947346A (en) * | 1974-09-20 | 1976-03-30 | The Lummus Company | Coal liquefaction |
| JPS5574442A (en) * | 1978-11-29 | 1980-06-05 | Toshiba Corp | Measuring method for mixture ratio of gas or oil |
| JPS63193019A (en) * | 1987-02-05 | 1988-08-10 | Damu Gijutsu Center | Apparatus for measuring liquid fluid |
-
1990
- 1990-10-24 JP JP2288124A patent/JPH0819418B2/en not_active Expired - Lifetime
-
1991
- 1991-10-22 AU AU86045/91A patent/AU627669B2/en not_active Expired
Also Published As
| Publication number | Publication date |
|---|---|
| JPH04161490A (en) | 1992-06-04 |
| AU8604591A (en) | 1992-04-30 |
| AU627669B2 (en) | 1992-08-27 |
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