JPH0328475B2 - - Google Patents

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Publication number
JPH0328475B2
JPH0328475B2 JP6701483A JP6701483A JPH0328475B2 JP H0328475 B2 JPH0328475 B2 JP H0328475B2 JP 6701483 A JP6701483 A JP 6701483A JP 6701483 A JP6701483 A JP 6701483A JP H0328475 B2 JPH0328475 B2 JP H0328475B2
Authority
JP
Japan
Prior art keywords
coal
particle size
flotation
water
slurry
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
JP6701483A
Other languages
Japanese (ja)
Other versions
JPS59193991A (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 JP6701483A priority Critical patent/JPS59193991A/en
Publication of JPS59193991A publication Critical patent/JPS59193991A/en
Publication of JPH0328475B2 publication Critical patent/JPH0328475B2/ja
Granted legal-status Critical Current

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  • Liquid Carbonaceous Fuels (AREA)
  • Solid Fuels And Fuel-Associated Substances (AREA)

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 deashed highly concentrated 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、燃焼効率のばらつきを最
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。
Highly concentrated coal water slurry consists of 60-85% coal (weight%), surfactant 0.01-5.0% by weight (based on coal powder),
Moisture: Slurry fuel made up of the remaining weight percent. 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 efficiency 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
41に微粉砕される。微粉炭411は石炭−水ス
ラリ状(石炭濃度で約45〜55重量%)で微粉炭貯
槽42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14により約20〜30重量%に濃峠調整され、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 to a pulverizer (usually a wet pulverizer) 40 by a quantitative feeder 39, and while being mixed with water 43, 200 mesh passes 70 to 95%. The coal is pulverized into pulverized coal 41 as shown in FIG. The pulverized coal 411 is received in the pulverized coal storage tank 42 in the form of a coal-water slurry (coal concentration of about 45 to 55% by weight). And pulverized coal 41 is
The water 14 separated from the dehydrator 2 after the flotation machine 1 (to be described later) is concentrated to about 20 to 30% by weight, and is supplied to the condition tank 4 together with the foaming agent 24 and the collecting agent 25, where it is flotated. Coal is introduced into coal 1 and 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 a wastewater treatment facility and disposed of.

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、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。
The coal (clean coal) 11 with a low ash content is dehydrated by the 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で微粉炭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
微粒度と粗粒度で起泡剤24、捕集剤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
粉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, in condition tank 4, pulverized coal 41 and foaming agent 24,
When the collecting agent 25 is sufficiently stirred and mixed, there will be a difference in the degree of adhesion of the foaming agent 24 and the collecting agent 25 depending on the fine and coarse particle size of the pulverized coal 41, and the fine powder will be used for the deashing process in the flotation machine 1. A large difference occurs between coal and coarse coal, and the deashing efficiency of all pulverized coal decreases.

すなわち微粉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を増やすと灰分の小い
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 pulverized coal is larger than that of coarse granulated 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 granulated coal is poor. Although the amount is small, the recovery rate of coal (clean coal) 11 with 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 small 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、捕収剤を添加・撹拌した後、両石炭−水ス
ラリを一つにして浮選脱灰処理することを特徴と
する脱灰高濃度石炭−水スラリの製造法に関する
ものである。
That is, the present invention grinds coal to a particle size suitable for highly concentrated coal-water slurry, classifies it into coal grain groups of larger particle size and smaller particle size, and separately converts each classified coal particle group into coal-water slurry. After adding and stirring a foaming agent and a collecting agent in an amount corresponding to the particle size and surface area of the coal grains in each slurry, the two coal-water slurries are combined and subjected to flotation deashing treatment. The present invention relates to a method for producing a characteristic deashed highly concentrated 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のスラリは、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の灰分の小い石炭(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。
A slurry of 70 to 95% pulverized coal 41 from a 200 mesh pass 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, which are larger than 200 mesh, are sufficiently stirred and supplied to the conditioned tank 4 together with the foaming agent 24 and the collecting agent 25. It adheres to and collides with the foaming agent 24 and the collecting agent 25.

一方、200メツシユ以下の石炭粒子150も、
これまた浮選機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15
0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、捕収剤25と付着、衝突させ
る。その後前述の200メツシユより大きい石炭粒
子50とともに浮選機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。
On the other hand, 150 coal particles of less than 200 mesh are also
This is also low ash coal (clean coal) 11 from flotation machine 1.
The coal concentration is adjusted to about 20 to 30% using water 14 which has been dehydrated to about 20% water content by the dehydrator 2, and is supplied to the conditioning tank 104 together with the foaming agent 24 and the collecting agent 25 to reduce the coal concentration to 200 mesh or less. coal particles 15
The coal particles 150 are sufficiently stirred to adhere and collide with the foaming agent 24 and the collecting agent 25 corresponding to the surface area of the coal particles 150. Thereafter, the above-mentioned coal particles 50 larger than 200 mesh are introduced into the flotation machine 1, and coal with a low ash content (clean coal) 11 and coal with a high ash content (tail) 12 are introduced into the flotation machine 1.
It is divided into Coal (tail) 12 with a high ash content is sent to wastewater treatment facility 115 and disposed of.

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及び104
に供給される石炭粒子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、脱灰石炭
高濃度水スラリ15となる。
Coal (clean coal) 11 with a low ash content is dehydrated by a dehydrator 2 to a coal concentration of approximately 20% water by weight, and water 14 separated from the dehydrator 2 is passed through the condition tanks 4 and 104.
It is reused to adjust the concentration of coal particles supplied to the The cake-like clean coal 13 having a water content of about 20% is turned into a deashed coal high concentration water slurry 15 with a surfactant aqueous solution 26 in the slurry adjustment tank 3.

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(浮選別)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) 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(捕収剤)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−水スラリを一つにして
浮選脱灰処理することを特徴とする脱灰高濃度石
炭−水スラリの製造法。
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 Deashing is characterized by 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, and then combining the two coal-water slurries and subjecting them to flotation deashing. Method for producing ash-high concentration coal-water slurry.
JP6701483A 1983-04-18 1983-04-18 Preparation of de-ashed highly concentrated coal-water slurry Granted JPS59193991A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP6701483A JPS59193991A (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
JP6701483A JPS59193991A (en) 1983-04-18 1983-04-18 Preparation of de-ashed highly concentrated coal-water slurry

Publications (2)

Publication Number Publication Date
JPS59193991A JPS59193991A (en) 1984-11-02
JPH0328475B2 true JPH0328475B2 (en) 1991-04-19

Family

ID=13332630

Family Applications (1)

Application Number Title Priority Date Filing Date
JP6701483A Granted JPS59193991A (en) 1983-04-18 1983-04-18 Preparation of de-ashed highly concentrated coal-water slurry

Country Status (1)

Country Link
JP (1) JPS59193991A (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
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

Also Published As

Publication number Publication date
JPS59193991A (en) 1984-11-02

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