JPH0328476B2 - - Google Patents

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Publication number
JPH0328476B2
JPH0328476B2 JP6701583A JP6701583A JPH0328476B2 JP H0328476 B2 JPH0328476 B2 JP H0328476B2 JP 6701583 A JP6701583 A JP 6701583A JP 6701583 A JP6701583 A JP 6701583A JP H0328476 B2 JPH0328476 B2 JP H0328476B2
Authority
JP
Japan
Prior art keywords
coal
water
particle size
water slurry
flotation
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
JP6701583A
Other languages
Japanese (ja)
Other versions
JPS59193992A (en
Inventor
Akira Oosawa
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.)
Mitsubishi Heavy Industries Ltd
Original Assignee
Mitsubishi Heavy Industries Ltd
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 Mitsubishi Heavy Industries Ltd filed Critical Mitsubishi Heavy Industries Ltd
Priority to JP6701583A priority Critical patent/JPS59193992A/en
Publication of JPS59193992A publication Critical patent/JPS59193992A/en
Publication of JPH0328476B2 publication Critical patent/JPH0328476B2/ja
Granted legal-status Critical Current

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Description

【発明の詳細な説明】 本発明は脱灰された高濃度石炭−水スラリの製
造方法に関するものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for producing a highly concentrated deashed coal-water slurry.

石炭高濃度水スラリとは、石炭60〜85%(重量
%)、界面活性剤0.01〜5.0重量%対石炭粉末、水
分:残りの重量%で構成されるスラリ燃料であ
る。石炭高濃度水スラリ中の石炭濃度、界面活性
剤添加率は石炭の種類によつて異なつてくる。石
炭には灰分が含まれているが、石炭高濃度水スラ
リをボイラで燃焼させる際、灰分があると、ボイ
ラ効率の低下が発生するため、できるだけ灰分を
燃焼前に除去しておくことが好ましい。又、石炭
中の残灰分を各炭種毎に値をそろえるということ
は、炭種による発熱量、燃焼効果のばらつきを最
小にできるという効果がある。このような背景の
もとに従来の脱灰プロセスが組み込まれた石炭高
濃度水スラリ製造プロセスを第1図にしたがつて
説明する。
The coal-rich water slurry is a slurry fuel composed of 60 to 85% (wt%) coal, 0.01 to 5.0 wt% surfactant to coal powder, and water: the remaining weight%. The coal concentration and surfactant addition rate in a highly concentrated coal water slurry vary depending on the type of coal. Coal contains ash, but when a high-concentration water slurry of coal is burned in a boiler, the presence of ash reduces boiler efficiency, so it is preferable to remove as much ash as possible before combustion. . Further, by making the residual ash content in coal the same for each type of coal, it is possible to minimize variations in calorific value and combustion effect depending on the type of coal. Based on this background, a process for producing a highly concentrated coal water slurry incorporating a conventional deashing process will be explained with reference to FIG.

原炭30を原炭受入槽31に入れ定量供給機3
2により石炭破砕機33に供給する。石炭破砕機
33では約30〜50mmの原炭30を約3mm以下の細
炭34に破砕する。この細炭34はスクリーン3
5により、3mm以上の石炭37と3mmより小さい
石炭36に分別される。3mmより小さい石炭36
は細炭受入槽38に貯蔵される。3mm以上の石炭
37は再び原炭受入槽31にもどされる。細炭受
入槽38に貯蔵された3mmより小さい石炭36は
定量供給機39により一定割合で微粉砕機(通常
湿式微粉砕機)40に供給され水43と混合され
ながら200メツシユパス70〜95%の如き微粉炭4
1に微粉砕される。微粉炭41は石炭−水スラリ
状(石炭濃度で約45〜55重量%)で微粉炭貯槽4
2に受け入れられる。そして微粉炭41は、後記
する浮選機1の後の脱水機2より分離された水1
4により約20〜30重量%に濃度調整され、条件槽
4に起泡剤24、捕収剤25とともに供給され、
浮選機1に導入され灰分の少い石炭(精炭)11
と、灰分の多い石炭(テール)12に別けられ
る。灰分の多い石炭(テール)12は排水処理設
備へ送られ廃棄される。
Put the raw coal 30 into the raw coal receiving tank 31 and quantitative feeder 3
2, the coal is supplied to a coal crusher 33. The coal crusher 33 crushes raw coal 30 of about 30 to 50 mm into fine coal 34 of about 3 mm or less. This fine coal 34 is screen 3
5, the coal is separated into coal 37 larger than 3 mm and coal 36 smaller than 3 mm. Coal smaller than 3mm36
is stored in the fine coal receiving tank 38. Coal 37 of 3 mm or more is returned to the raw coal receiving tank 31 again. Coal 36 smaller than 3 mm stored in the fine coal receiving tank 38 is fed at a constant rate by a metering feeder 39 to a pulverizer (usually a wet pulverizer) 40, where it is mixed with water 43 and is mixed with 200 mesh passes of 70 to 95%. Like pulverized coal 4
Finely ground to 1. Pulverized coal 41 is in the form of a coal-water slurry (approximately 45 to 55% by weight in terms of coal concentration) and is stored in pulverized coal storage tank 4.
2 is accepted. The pulverized coal 41 is water 1 separated from a dehydrator 2 after the flotation machine 1, which will be described later.
4, the concentration is adjusted to about 20 to 30% by weight, and the foaming agent 24 and the collecting agent 25 are supplied to the condition tank 4,
Coal with low ash content introduced into flotation machine 1 (clean coal) 11
It is divided into 12 types of coal (tail) with a high ash content. Coal (tail) 12 with a high ash content is sent to a wastewater treatment facility and disposed of.

灰分の少い石炭(精炭)(1)(1)は脱水機2により
約20重量%水分の石炭濃度迄脱水され、脱水機2
より分離された水14は、前記したように条件槽
4に供給される微粉炭10の濃度調整に再利用さ
れる。ケーキ状の水分約20%の精炭13は、スラ
リ調整槽3で界面活性剤の水溶液26で石炭高濃
度水スラリ15の最終石炭濃度に再調整される。
Coal with a low ash content (clean coal) (1)(1) is dehydrated by dehydrator 2 to a coal concentration of approximately 20% water by weight.
The separated water 14 is reused to adjust the concentration of the pulverized coal 10 supplied to the conditioning tank 4 as described above. The cake-like clean coal 13 having a moisture content of approximately 20% is readjusted to the final coal concentration of a high coal concentration water slurry 15 using a surfactant aqueous solution 26 in a slurry adjustment tank 3.

以上が従来の脱灰プロセスが組み込まれた石炭
高濃度水スラリ製造プロセスである。ここで従来
のプロセスは、かなり粒径巾の広い微粉炭41を
同時に条件槽4で処理し浮選機1に送つている。
しかし条件槽4と微粉炭41と起泡剤24、捕収
剤25を充分撹拌混合すると、微粉炭41の微粒
炭と粗粒炭で起泡剤24、捕収剤25との付着度
合に差が発生し、浮選機1での脱灰処理に微粒炭
と粗粒炭に大きな差が発生し、全微粉炭の脱灰処
理効率が低下することとなる。
The above is the coal high concentration water slurry production process incorporating the conventional deashing process. Here, in the conventional process, pulverized coal 41 having a considerably wide particle size range is simultaneously treated in the condition tank 4 and sent to the flotation machine 1.
However, when the conditioned tank 4, the pulverized coal 41, the foaming agent 24, and the collecting agent 25 are sufficiently stirred and mixed, there is a difference in the degree of adhesion of the foaming agent 24 and the collecting agent 25 between the pulverized coal 41 and the coarse granulated coal. This causes a large difference in the deashing process in the flotation machine 1 between fine coal and coarse coal, resulting in a decrease in the deashing efficiency of all pulverized coal.

すなわち微粒炭の表面積の方が粗粒炭に比らべ
て大きいので起泡剤24、捕収剤25の付着量が
多いが、粒径が小さいため浮選特性は悪く粗粒炭
への付着量は少いが、粒径が大きいため浮選特性
は良い等に原因して全体の灰分の少い石炭(精
炭)11の回収率が起泡剤24、捕収剤25の添
加率の割合に比して低いものとなつてしまう。逆
に起泡剤24、捕収剤25を増やすと灰分の少い
石炭(精炭)11の回収率は向上するが、精炭1
1中の残灰率も多くなる。すなわち精炭11の脱
灰処理効率が低下したこととなり不具合である。
In other words, since the surface area of fine coal is larger than that of coarse grain coal, the amount of foaming agent 24 and collecting agent 25 that adheres to it is large, but because the particle size is small, the flotation properties are poor and the adhesion to coarse grain coal is poor. Although the amount is small, the recovery rate of coal (clean coal) 11 with a low overall ash content is lower than the addition rate of foaming agent 24 and collecting agent 25 due to its large particle size and good flotation properties. This results in a relatively low percentage. Conversely, increasing the foaming agent 24 and collecting agent 25 improves the recovery rate of coal with a low ash content (clean coal) 11, but
The percentage of residual ash in 1 also increases. In other words, the deashing efficiency of the clean coal 11 has decreased, which is a problem.

そこで本発明者は、石炭粒度分布の変動があつ
ても、精炭回収率、脱灰処理効率が効率よく保た
れるプロセスを開発すべく鋭意研究の結果本発明
を完成するに至つた。
Therefore, the present inventor completed the present invention as a result of intensive research in order to develop a process in which the clean coal recovery rate and deashing treatment efficiency can be efficiently maintained even when there are fluctuations in the coal particle size distribution.

すなわち本発明は、石炭を高濃度石炭−水スラ
リに適する粒度に紛砕し、これをより大きい粒度
とより小さな粒度の石炭粒群に分級し、各分級石
炭粒群を別々に石炭−水スラリにし、該各スラリ
にその中の石炭粒の粒度表面積に対応した量の起
泡剤、捕集剤を添加・撹拌した後、両石炭−水ス
ラリを別々に浮選脱灰処理し、各脱灰処理して得
られた精炭を一つにして高濃度石炭−水スラリに
調製することを特徴とする脱灰高濃度石炭−水ス
ラリの製造方法に関するものである。
That is, the present invention grinds coal to a particle size suitable for a highly concentrated coal-water slurry, classifies it into coal grain groups of larger particle size and smaller particle size, and separately infuses each classified coal particle group into a coal-water slurry. After adding and stirring a foaming agent and a scavenger in an amount corresponding to the particle size and surface area of the coal grains in each slurry, both coal-water slurries were separately subjected to flotation deashing treatment. The present invention relates to a method for producing a deashed high-concentration coal-water slurry, which is characterized in that clean coal obtained by ash treatment is combined into a high-concentration coal-water slurry.

以下、本発明の一実施態様を第2図にしたがつ
て説明する。第2図においては、第1図の微粉炭
貯槽42までの工程は同一であるので省略してあ
る。
Hereinafter, one embodiment of the present invention will be described with reference to FIG. In FIG. 2, the steps up to the pulverized coal storage tank 42 in FIG. 1 are the same and are therefore omitted.

微粉炭貯槽からの200メツシユパス70〜95%の
微粉炭41のスラリを湿式サイクロンの如き分級
器100で、200メツシユより大きい粒子と200メ
ツシユ以下の小さい粒子に分級する。200メツシ
ユより大きい石炭粒子50は、第1図に関して説
明したと同様に浮選機1の灰分の少い石炭(精
炭)11を脱水機2により約20重量%水分迄脱水
処理した水により石炭濃度が約20〜30%に調整さ
れ、条件槽4に起泡剤24、捕収剤25とともに
供給され充分、200メツシユより大きい石炭粒子
50は撹拌され、石炭粒子50の表面積に対応す
る起泡剤24、捕収剤25と付着、衝突させる。
その後浮選機1に導入し、灰分の少い石炭(精
炭)11と、灰分の多い石炭(テール)12に別
けられる。灰分の多い石炭(テール)12は排水
処理設備115へ送られ廃棄される。灰分の少い
石炭(精炭)11は脱水機2により約20重量%水
分の石炭濃度迄脱水され、脱水機2より分離され
た水14は、条件槽4に供給される200メツシユ
より大きい石炭粒子50の濃度調整に再利用され
る。ケーキ状の水分約20%の精炭13はスラリ調
整槽3で界面活性剤の水溶液26で石炭高濃度水
スラリ15の一部を構成する。
A slurry of 70 to 95% pulverized coal 41 from a pulverized coal storage tank is classified into particles larger than 200 mesh and particles smaller than 200 mesh using a classifier 100 such as a wet cyclone. Coal particles 50 larger than 200 mesh are obtained by dehydrating coal (clean coal) 11 with a low ash content from the flotation machine 1 to about 20% water by weight using the dehydrator 2 in the same manner as explained in connection with FIG. The concentration is adjusted to about 20 to 30%, and the coal particles 50 larger than 200 mesh are sufficiently stirred by being supplied to the condition tank 4 together with the foaming agent 24 and the collecting agent 25, and foaming corresponding to the surface area of the coal particles 50 is carried out. It adheres to and collides with the agent 24 and the collecting agent 25.
Thereafter, it is introduced into a flotation machine 1, where it is separated into coal 11 with a low ash content (clean coal) and coal 12 with a high ash content (tail). Coal (tail) 12 with a high ash content is sent to wastewater treatment facility 115 and disposed of. Coal (clean coal) 11 with a low ash content is dehydrated by a dehydrator 2 to a coal concentration of about 20% water by weight, and the water 14 separated from the dehydrator 2 is used as coal larger than 200 mesh to be supplied to the conditioner 4. It is reused to adjust the concentration of particles 50. The cake-like clean coal 13 having a water content of about 20% forms part of a highly concentrated coal water slurry 15 in a slurry adjustment tank 3 with an aqueous surfactant solution 26 .

一方、200メツシユ以下の石炭粒子150も、
これまた浮選機101の灰分の少い石炭(精炭)
111を脱水機102により約20重量%水分迄脱
水処理した水14により、石炭濃度が約20〜30%
に調整され、条件槽104に起泡剤24、捕収剤
25とともに供給され、200メツシユ以下の石炭
粒子150は充分撹拌され、石炭粒子150の表
面積に対応する起泡剤24、捕集剤25と付着、
衝突させる。その後浮選機101に導入し、灰分
の少い石炭(精炭)111と、灰分の多い石炭
(テール)112に別けられる。石炭灰分の多い
(テール)112は排水処理設備115へ送られ
廃棄される。
On the other hand, 150 coal particles of less than 200 mesh are also
This is also coal with a low ash content (clean coal) from the flotation machine 101.
The water 14 obtained by dehydrating 111 to about 20% water content by the dehydrator 102 reduces the coal concentration to about 20 to 30%.
The coal particles 150 of 200 mesh or less are sufficiently stirred, and the foaming agent 24 and the collecting agent 25 corresponding to the surface area of the coal particles 150 are supplied to the condition tank 104 together with the foaming agent 24 and the collecting agent 25. and adhesion,
make it collide. Thereafter, it is introduced into a flotation machine 101 and separated into coal 111 with a low ash content (clean coal) and coal 112 with a high ash content (tail). Coal ash-rich (tail) 112 is sent to wastewater treatment facility 115 and disposed of.

灰分の少い石炭(精炭)11は、脱水機102
により約20重量%水分の石炭濃度迄脱水され、脱
水機102より分離された水114は条件槽10
4に供給される200メツシユ以下の石炭粒子15
0の濃度調整に再利用される。ケーキ状の水分約
20%の精炭113は、スラリ調整槽3で界面活性
剤の水溶液26で、脱灰石炭高濃度水スラリ15
を精炭13とともに構成する。
Coal with a low ash content (clean coal) 11 is sent to a dehydrator 102
The water 114 separated from the dehydrator 102 is dehydrated to a coal concentration of about 20% water by weight.
Coal particles of 200 mesh or less supplied to 4.15
Reused for adjusting the density of 0. Cake moisture approx.
20% clean coal 113 is mixed with a surfactant aqueous solution 26 in a slurry adjustment tank 3, and deashed coal high concentration water slurry 15
together with clean coal 13.

以上、本発明の一実施態様のフローについて説
明したが、各工程における一般的な条件について
述べると、各条件槽における石炭−水スラリの滞
留時間は5〜20分間であり、浮選条件としてはPH
6〜8、浮選石炭濃度5〜30重量%、浮選時間5
〜20分間が採用され、また条件槽にはα−テルピ
ネオール、メチルイソブチルカルビノールなどの
起泡剤とケロシンなどの捕集剤が前者1、後者4
の重量割合の混合物(浮選剤)が添加される。
The flow of one embodiment of the present invention has been explained above, but to describe the general conditions in each step, the residence time of the coal-water slurry in each condition tank is 5 to 20 minutes, and the flotation conditions are PH
6-8, flotation coal concentration 5-30% by weight, flotation time 5
~20 minutes was adopted, and in the condition bath, foaming agents such as α-terpineol and methyl isobutyl carbinol and scavenging agents such as kerosene were used.
A weight proportion of the mixture (flotation agent) is added.

例 粒度200メツシユパス70%の大同炭を、第1図
及び第2図に示したフローに従つて処理した。両
フローとも、条件槽の滞留時間は7分間、浮選条
件は、フアーレンワルド型浮選機において、PH6
〜8、浮選石炭濃度10重量%、浮選時間は7分間
とした。又、両フローとも条件槽に添加した浮選
剤は、α−テルピネオール(起泡剤)1:ケロシ
ン(捕集剤)4の割合のものである。
Example Daido coal with a grain size of 200 and a mesh pass of 70% was treated according to the flow shown in Figures 1 and 2. For both flows, the residence time in the conditioned tank was 7 minutes, and the flotation conditions were PH6 in a Fahrenwald type flotation machine.
~8. The flotation coal concentration was 10% by weight, and the flotation time was 7 minutes. In both flows, the flotation agent added to the conditioned tank was in a ratio of 1 part α-terpineol (foaming agent) to 4 parts kerosene (collecting agent).

但し、第1図のフローにおいては、条件槽4に
浮選剤を石炭当り800ppm添加し、第2図のフロ
ーにおいては条件槽4(粗粒子側)には浮選剤を
石炭当り500ppm、条件槽104(微粒子側)に
は浮選剤を石炭当り800ppm添加した。
However, in the flow shown in Figure 1, 800 ppm of flotation agent per coal is added to conditioned tank 4, and in the flow shown in Figure 2, 500 ppm of flotation agent per coal is added to conditioned tank 4 (coarse particle side). A flotation agent was added to tank 104 (fine particle side) at 800 ppm per coal.

その結果を第3図に示す。第3図において横軸
は脱灰率(%)、縦軸は純炭回収率(%)を示す。
又グラフAは第2図のフロー(本発明方法)、グ
ラフBは第1図のフロー(従来法)の結果を示
す。
The results are shown in FIG. In FIG. 3, the horizontal axis shows the deashing rate (%), and the vertical axis shows the pure coal recovery rate (%).
Graph A shows the results of the flow shown in FIG. 2 (method of the present invention), and graph B shows the results of the flow shown in FIG. 1 (conventional method).

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

第1図は従来の脱灰プロセスを組込んだ脱灰高
濃度石炭−水スラリの製造フロー、第2図は本発
明の同フローを示し、第3図は本発明の効果を示
すグラフである。
Figure 1 is a production flow of a deashed highly concentrated coal-water slurry incorporating a conventional deashing process, Figure 2 is a flowchart of the present invention, and Figure 3 is a graph showing the effects of the present invention. .

Claims (1)

【特許請求の範囲】[Claims] 1 石炭を高濃度石炭−水スラリに適する粒度に
粉砕し、これをより大きい粒度とより小さな粒度
の石炭粒群に分級し、各分級石炭粒群を別々に石
炭−水スラリにし、該各スラリにその中の石炭粒
の粒度表面積に対応した量の起泡剤、捕集剤を添
加・撹拌した後、両石炭−水スラリを別々に浮選
脱灰処理し、各脱灰処理して得られた精炭を一つ
にして高濃度石炭−水スラリに調製することを特
徴とする脱灰高濃度石炭−水スラリの製造方法。
1. Pulverize coal to a particle size suitable for highly concentrated coal-water slurry, classify it into coal grain groups of larger particle size and smaller particle size, make each classified coal particle group separately into coal-water slurry, and After adding and stirring a foaming agent and a scavenger in an amount corresponding to the particle size and surface area of the coal grains in the slurry, both coal-water slurries were subjected to flotation and deashing treatment separately, and the resulting product from each deashing treatment was 1. A method for producing a deashed high concentration coal-water slurry, which comprises combining the purified coal to form a high concentration coal-water slurry.
JP6701583A 1983-04-18 1983-04-18 Preparation of de-ashed highly concentrated coal-water slurry Granted JPS59193992A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP6701583A JPS59193992A (en) 1983-04-18 1983-04-18 Preparation of de-ashed highly concentrated coal-water slurry

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP6701583A JPS59193992A (en) 1983-04-18 1983-04-18 Preparation of de-ashed highly concentrated coal-water slurry

Publications (2)

Publication Number Publication Date
JPS59193992A JPS59193992A (en) 1984-11-02
JPH0328476B2 true JPH0328476B2 (en) 1991-04-19

Family

ID=13332658

Family Applications (1)

Application Number Title Priority Date Filing Date
JP6701583A Granted JPS59193992A (en) 1983-04-18 1983-04-18 Preparation of de-ashed highly concentrated coal-water slurry

Country Status (1)

Country Link
JP (1) JPS59193992A (en)

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS59215391A (en) * 1983-05-21 1984-12-05 Electric Power Dev Co Ltd Preparation of deashed concentrated slurry
JPS61123699A (en) * 1984-11-20 1986-06-11 Electric Power Dev Co Ltd Production of deashed slurry with high concentration
JPS61133294A (en) * 1984-11-30 1986-06-20 Electric Power Dev Co Ltd Production of high-concentration slurry
JPS61133293A (en) * 1984-11-30 1986-06-20 Electric Power Dev Co Ltd Production of high-concentration slurry

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JPS59193992A (en) 1984-11-02

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