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
JPS6259759B2 - - Google Patents
[go: Go Back, main page]

JPS6259759B2 - - Google Patents

Info

Publication number
JPS6259759B2
JPS6259759B2 JP56057427A JP5742781A JPS6259759B2 JP S6259759 B2 JPS6259759 B2 JP S6259759B2 JP 56057427 A JP56057427 A JP 56057427A JP 5742781 A JP5742781 A JP 5742781A JP S6259759 B2 JPS6259759 B2 JP S6259759B2
Authority
JP
Japan
Prior art keywords
coal
chemical solution
fluoride
deashing
chemical
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
JP56057427A
Other languages
Japanese (ja)
Other versions
JPS57171000A (en
Inventor
Shigenori Onizuka
Takanobu Watanabe
Katsumasa Yano
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.)
Kanadevia Corp
Original Assignee
Hitachi Shipbuilding and Engineering Co 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 Hitachi Shipbuilding and Engineering Co Ltd filed Critical Hitachi Shipbuilding and Engineering Co Ltd
Priority to JP5742781A priority Critical patent/JPS57171000A/en
Priority to US06/356,337 priority patent/US4424062A/en
Priority to NZ199964A priority patent/NZ199964A/en
Priority to GB8206972A priority patent/GB2094830B/en
Priority to DE3208704A priority patent/DE3208704C2/en
Priority to CA000398285A priority patent/CA1169800A/en
Priority to AU81348/82A priority patent/AU532092B2/en
Priority to BR8201410A priority patent/BR8201410A/en
Publication of JPS57171000A publication Critical patent/JPS57171000A/en
Publication of JPS6259759B2 publication Critical patent/JPS6259759B2/ja
Granted legal-status Critical Current

Links

Landscapes

  • Extraction Or Liquid Replacement (AREA)
  • Solid Fuels And Fuel-Associated Substances (AREA)

Description

【発明の詳細な説明】 この発明は、石炭の輸送あるいは燃焼などを円
滑に行ない得る脱灰炭を製造するのに適用される
石炭の化学的脱灰処理装置に関するものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a chemical deashing treatment apparatus for coal that is applied to produce deashed coal that can be transported or burned smoothly.

周知のとおり、近年石油供給の見通しの不安、
ならびにその価格高騰のため、エネルギーの多様
化の必要性が説かれ、その代替品の第一候補とし
て石炭が取り上げられ、その有効な利用法の促進
が計られている。石炭は古来主要なエネルギー源
として利用されてきたが、石油の出現によつて取
つて替られた。その主もな理由は、石油が低廉か
つ多量に入手できるようになつたことにも起因す
るが、石炭が固体であることと、ほとんど利用価
値のない灰分を含んでいることにも由来する。す
なわち、固体であることから輸送が非常に困難で
あり、輸送コストがかさむ。石炭中の灰分の存在
は石炭のエネルギー密度を低下させ、そのことか
らだけでも灰分のない石油に比較して効率の悪い
エネルギー源といえる。また灰分は石炭燃焼時に
はそのまま排出されるので、最近のように大型化
が進んだ火力発電所等では、その処理に多大の費
用を要している。また厳密には無機物質だけに限
定されないが、硫黄分の問題もある。すなわち、
これらの硫黄分は燃焼によつて硫黄酸化物を生成
し、環境汚染の観点から重大な関心が寄せられて
いる。現在わが国は石炭需要の相当量を海外炭に
依存しているが、石炭中の灰分は数パーセントか
ら数十パーセントまで存在し、通常は10〜20%で
あり、これらの灰分は有効に利用されず廃棄さ
れ、結局輸送コストの10〜20%が無駄に費やされ
ていることになる。このように石炭の灰分の問題
は石炭の有効利用上極めて重大なものであり、石
炭の灰分の除去が有効になされればその経済的効
果は計り知れないものがある。
As is well known, in recent years there has been concern about the outlook for oil supply,
Due to the soaring prices of coal, the necessity of diversifying energy sources has been advocated, and coal has been chosen as the first candidate for its replacement, and efforts are being made to promote its effective use. Coal has been used as a major energy source since ancient times, but was replaced by the advent of oil. The main reason for this is that petroleum has become cheap and available in large quantities, but it also stems from the fact that coal is solid and contains ash, which has little utility value. That is, since it is a solid, it is very difficult to transport, and transportation costs are high. The presence of ash in coal reduces its energy density, which alone makes it a less efficient energy source than oil without ash. Furthermore, since ash is directly emitted when coal is burned, it costs a lot of money to dispose of it at thermal power plants, which have recently become larger. Although it is not strictly limited to inorganic substances, there is also the problem of sulfur content. That is,
These sulfur components generate sulfur oxides upon combustion, and are of great concern from the viewpoint of environmental pollution. Currently, Japan relies on foreign coal for a considerable amount of its coal demand, but the ash content in coal ranges from a few percent to several tens of percent, usually 10 to 20 percent, and this ash content is not being used effectively. In the end, 10 to 20% of transportation costs are wasted. As described above, the problem of the ash content of coal is extremely important for the effective use of coal, and if the ash content of coal can be effectively removed, the economic effects will be immeasurable.

また石炭は上記のように固体であるため、その
輸送に多大のコストがかかるが、そのコスト低減
のために石炭を微粉砕してニユーマチツク輸送す
る方法や水スラリーあるいはオイルスラリーなど
にして疑似的な流体として輸送する方法が検討さ
れている。また、石炭の燃焼ボイラでは大型にな
るとほとんど例外なく微粉炭燃焼ボイラが用いら
れており、このようなボイラでは一般には200メ
ツシユ以下80%程度に粉砕された石炭が使用され
ている。
In addition, as coal is solid as mentioned above, it costs a lot of money to transport it, but in order to reduce costs, there are ways to reduce the cost by pulverizing coal and transporting it pneumatically, or by making it into water slurry or oil slurry. A method of transporting it as a fluid is being considered. Furthermore, when it comes to large-scale coal combustion boilers, pulverized coal combustion boilers are almost always used, and such boilers generally use coal that has been pulverized to about 80% less than 200 mesh.

ここで、従来の石炭からの灰分の除去法すなわ
ち脱灰法について述べると、これは検討されてい
るが現在のところ真に有効な方法はないと言わざ
るを得ない。脱灰法の究極の技術となると石炭の
液化技術となろうが、これはまだ未来技術の内に
数えられているものである。比較的有効な方法と
しては、粉砕した石炭を水と油の混合したものに
懸濁撹拌し、石炭粒子のみを油層で凝集させ、灰
分を水層へ分離するオイルアグロメレーシヨンな
る方法がある。また古くは石炭を高温、高圧下で
アルカリにて処理する方法もある。また極く最近
では弗化水素ガスで処理する方法が提案(特開昭
55−133487号)されているが、いずれも完全に実
用的なものとは言い難い。すなわち有効な脱灰法
はまだ世の中にはでていないのである。
Now, regarding the conventional method of removing ash from coal, that is, the deashing method, it must be said that although this is being considered, there is currently no truly effective method. The ultimate technology for deashing would be coal liquefaction technology, but this is still considered a technology of the future. A relatively effective method is oil agglomeration, in which pulverized coal is suspended and stirred in a mixture of water and oil, only the coal particles are agglomerated in an oil layer, and the ash is separated into a water layer. There is also an old method of treating coal with alkali at high temperature and pressure. Also, very recently, a method of treatment with hydrogen fluoride gas has been proposed (Unexamined Japanese Patent Publication No.
55-133487), but none of them can be said to be completely practical. In other words, an effective deashing method has not yet appeared in the world.

本発明者らは、本特許出願に先だち、脱灰法と
して塩酸もしくはクエン酸水溶液に弗化物を添加
した溶液にて石炭を処理する化学的な方法を提案
した(特開昭57−151698号公報および特開昭57−
162791号公報参照)。ここで弗化物としては、酸
性弗化アンモン、弗化アンモン、酸性弗化ナトリ
ウム、弗化ナトリウム、酸性弗化カリウム、弗化
カリウムが有効であり、特に酸性弗化アンモンが
有効である。弗化物として酸性弗化アンモンを使
用する場合には、先提案の出願明細書に記載され
たように、塩酸1〜10重量%および酸性弗化アン
モン(NH4HF2)1.25〜10重量%、あるいはクエ
ン酸1〜10重量%および酸性弗化アンモン1〜10
重量%を含む水溶液を使用する。この先提案によ
る方法は水溶液反応をベースにしたいわゆる湿式
法であり、有害な弗化水素ガスの発生がなく、常
温にても脱灰効果を有するものである。
Prior to filing this patent application, the present inventors proposed a chemical method for treating coal with a solution of fluoride added to hydrochloric acid or citric acid aqueous solution as a deashing method (Japanese Unexamined Patent Publication No. 151698/1983). and JP-A-57-
(See Publication No. 162791). As the fluoride, acidic ammonium fluoride, ammonium fluoride, acidic sodium fluoride, sodium fluoride, acidic potassium fluoride, and potassium fluoride are effective, and acidic ammonium fluoride is particularly effective. When using acidic ammonium fluoride as the fluoride, 1 to 10% by weight of hydrochloric acid and 1.25 to 10% by weight of acidic ammonium fluoride (NH 4 HF 2 ), as described in the previously proposed application specification; or 1-10% by weight of citric acid and 1-10% by weight of acidic ammonium fluoride
Using an aqueous solution containing % by weight. The previously proposed method is a so-called wet method based on an aqueous solution reaction, does not generate harmful hydrogen fluoride gas, and has a deashing effect even at room temperature.

またここで、粉砕法について述べると、これは
周知の通り数限りなく存在する。すなわち、粗砕
機であるクラツシヤー類から微粉砕機の各種ミル
まで存在し、現状では用途に応じてこれらの粉砕
機が使用されている。上記のようなニユーマテイ
ツク輸送、水スラリーあるいはオイルスラリーな
どの疑似的な流体としての輸送の場合には、種々
のケースがあるが、石炭粒子は100メツシユ以下
程度であり、燃焼の場合にはいられており、この
ようなボイラでは一般には200メツシユ以下80%
程度に粉砕された石炭が使用されている。
Here, we will discuss the pulverization method.As is well known, there are an infinite number of pulverization methods. That is, there are various types of mills, from crushers that are coarse crushers to various types of mills that are fine crushers, and these crushers are currently used depending on the purpose. There are various cases in the case of pneumatic transportation as described above, transportation as a pseudo fluid such as water slurry or oil slurry, but the coal particles are about 100 mesh or less, and in the case of combustion, they cannot be contained. In general, the boiler is 80% less than 200 mesh.
Fairly pulverized coal is used.

ここで、従来の石炭からの灰分の除去法すなわ
ち脱灰法について述べると、これは検討されてい
るが現在のところ真に有効な方法はないと言わざ
るを得ない。脱灰法の究極の技術となると石炭の
液化技術となろうが、これはまだ未来技術の内に
数えられているものである。比較的有効な方法と
しては、粉砕した石炭を水と油の混合したものに
懸濁撹拌し、石炭粒子のみを油層で凝集させ、灰
分を水層へ分離するオイルアグロメレーシヨンな
る方法がある。また古くは石炭を高温、高圧下で
アルカリにて処理する方法もある。また極く最近
では弗化水素ガスで処理する方法が提案(特開昭
55−133487号)されているが、いずれも完全に実
用的なものとは言い難い。すなわち有効な脱灰法
はまだ世の中にはでていないのである。
Now, regarding the conventional method of removing ash from coal, that is, the deashing method, it must be said that although this is being considered, there is currently no truly effective method. The ultimate technology for deashing would be coal liquefaction technology, but this is still considered a technology of the future. A relatively effective method is oil agglomeration, in which pulverized coal is suspended and stirred in a mixture of water and oil, only the coal particles are agglomerated in an oil layer, and the ash is separated into a water layer. There is also an old method of treating coal with alkali at high temperature and pressure. Also, very recently, a method of treatment with hydrogen fluoride gas has been proposed (Unexamined Japanese Patent Publication No.
55-133487), but none of them can be said to be completely practical. In other words, an effective deashing method has not yet appeared in the world.

本発明者らは、本特許出願に先だち、脱灰法と
して塩酸もしくはクエン酸水溶液に弗化物を添加
した溶液にて石炭を処理する化学的な方法を提案
した(特開昭57−151698号公報および特開昭57−
162791号公報参照)。ここで弗化物としては、酸
性弗化アンモン、弗化アンモン、酸性弗化ナトリ
ウム、弗化ナトリウム、酸性弗化カリウム、弗化
カリウムが有効であり、特に酸性弗化アンモンが
有効である。弗化物として酸性弗化アンモンを使
用する場合には、先提案の出願明細書に記載され
たように、塩酸1〜10重量%および酸性弗化アン
モン(NH4HF2)1.25〜10重量%、あるいはクエ
ン酸1〜10重量%および酸性弗化アンモン1〜10
重量%を含む水溶液を使用する。この先提案によ
る方法は水溶液反応をベースにしたいわゆる湿式
法であり、有害な弗化水素ガスの発生がなく、常
温にても脱灰効果を有するものである。
Prior to filing this patent application, the present inventors proposed a chemical method for treating coal with a solution of fluoride added to hydrochloric acid or citric acid aqueous solution as a deashing method (Japanese Unexamined Patent Publication No. 151698/1983). and JP-A-57-
(See Publication No. 162791). As the fluoride, acidic ammonium fluoride, ammonium fluoride, acidic sodium fluoride, sodium fluoride, acidic potassium fluoride, and potassium fluoride are effective, and acidic ammonium fluoride is particularly effective. When using acidic ammonium fluoride as the fluoride, 1 to 10% by weight of hydrochloric acid and 1.25 to 10% by weight of acidic ammonium fluoride (NH 4 HF 2 ), as described in the previously proposed application specification; or 1-10% by weight of citric acid and 1-10% by weight of acidic ammonium fluoride
Using an aqueous solution containing % by weight. The previously proposed method is a so-called wet method based on an aqueous solution reaction, does not generate harmful hydrogen fluoride gas, and has a deashing effect even at room temperature.

またここで、粉砕法について述べると、これは
周知の通り数限りなく存在する。すなわち、粗砕
機であるクラツシヤー類から微粉砕機の各種ミル
まで存在し、現状では用途に応じてこれらの粉砕
機が使用されている。上記のようなニユーマテイ
ツク輸送、水スラリーあるいはオイルスラリーな
どの疑似的な流体としての輸送の場合には、種々
のケースがあるが、石炭粒子は100メツシユ以下
程度であり、燃焼の場合にはそれ以下であること
が多い。この種の微粉砕機としてはミル類が多く
使用されている。ミル類は大きく分けると乾式の
ものと湿式のものとがあるが、純粋に効率的な面
から見ると湿式のものが良いとされている。すな
わち、乾式の場合には粉砕機の壁面やボールなど
に微粒子が付着し、その緩衝作用のために能率が
低くなる。これに対し湿式の場合には微粉が流出
するため、このような現象がなく能率が高い。
Here, we will discuss the pulverization method. As is well known, there are an infinite number of pulverization methods. That is, there are various types of mills, from crushers that are coarse crushers to various types of mills that are fine crushers, and these crushers are currently used depending on the purpose. There are various cases in the case of pneumatic transportation as described above, transportation as a pseudo fluid such as water slurry or oil slurry, but the coal particles are about 100 mesh or less, and in the case of combustion, it is smaller than that. Often. Mills are often used as this type of pulverizer. Mills can be roughly divided into dry and wet types, but from a pure efficiency standpoint, wet types are considered better. That is, in the case of a dry type, fine particles adhere to the walls, balls, etc. of the pulverizer, and the efficiency decreases due to the buffering effect of the particles. On the other hand, in the case of a wet method, fine powder flows out, so this phenomenon does not occur and efficiency is high.

本発明者らは、上記の点に鑑み、湿式粉砕機の
効率の良さとその機能、および前述の化学的湿式
脱灰法の特性に着目し、石炭を粉砕すると同時に
脱灰することができる装置を見い出し、この発明
を完成したものである。この発明にかゝる脱灰処
理装置によれば、ニユーマテイツク輸送、水スラ
リー、オイルスラリーなどへ供給する最適の脱灰
炭を得ることができるものである。
In view of the above points, the present inventors focused on the efficiency and function of a wet pulverizer, as well as the characteristics of the chemical wet deashing method described above, and developed an apparatus that can simultaneously pulverize and deash coal. He discovered this and completed this invention. According to the deashing treatment apparatus according to the present invention, it is possible to obtain the optimum deashing coal to be supplied to pneumatic transportation, water slurry, oil slurry, etc.

この発明を、以下図面に示す実施例に基づいて
説明する。
This invention will be explained below based on embodiments shown in the drawings.

なお、実施例はこの発明の具体的な1例を示す
ものであり、この発明はこのような実施例に限定
されるものではない。
It should be noted that the Examples show one specific example of the present invention, and the present invention is not limited to such Examples.

図面において、粉砕されるべき原料石炭は混合
槽1に投入され、ここで原料石炭と脱灰剤水溶液
とが所定の割合に混合される。原料石炭と脱灰剤
水溶液の混合物はつぎの湿式粉砕機2に導入され
る。ここで、粉砕機2としては、格別制限はな
く、ボールミル、チユーブミル、ロツドミル、ア
トリツシヨンミルなど湿式の粉砕機が使用され
る。この粉砕機2において原料石炭の粉砕と同時
に、粉砕炭と脱灰剤水溶液との接触が行なわれ
る。この場合、加熱装置はとくに必要ではなく、
かつ常圧下において粉砕と脱灰反応が行なわれ
る。
In the drawing, raw coal to be pulverized is put into a mixing tank 1, where the raw coal and a deashing agent aqueous solution are mixed at a predetermined ratio. The mixture of raw coal and deashing agent aqueous solution is introduced into the next wet crusher 2. Here, the crusher 2 is not particularly limited, and wet-type crushers such as a ball mill, tube mill, rod mill, and attrition mill are used. In this pulverizer 2, the raw coal is pulverized and at the same time, the pulverized coal and the deashing agent aqueous solution are brought into contact. In this case, a heating device is not particularly necessary;
The pulverization and deashing reactions are carried out under normal pressure.

ここで脱灰剤水溶液は、腐食抑制剤を含んだ塩
酸もしくはクエン酸水溶液に弗化物を添加したも
のである。腐食抑制剤は装置および配管等を塩酸
もしくはクエン酸水溶液の腐食性から防御するた
めのものであり、市販のものが使用できる。すな
わちこの種の腐食抑制剤は、ボイラチユーブやプ
ラント配管類の酸洗時に使用されるものを用いる
ことができる。そして塩酸およびクエン酸は、石
炭中の灰分、特に鉄系の化合物の溶解に効果を有
し、また弗化物は、シリカ系の化合物の溶解に効
果を発揮する。しかしながら、これらの酸類と弗
化物の両者には相乗効果があり、両者が同一溶液
に存在する時に最も大きな脱灰作用を得ることが
できる。ここで弗化物としては、酸性弗化アンモ
ン、弗化アンモン、酸性弗化ナトリウム、弗化ナ
トリウム、酸性弗化カリウム、弗化カリウムより
なる群の中から選ばれたものを使用する。これら
の弗化物の中では酸性弗化アンモンが脱灰のため
に最も効果的である。これは単に脱灰作用が強い
だけでなく、後の排水処理に際しても、ナトリウ
ム塩やカリウム塩の場合とは異なり、分解可能で
あるためスラツジ量を増さない効果を有する。
Here, the deashing agent aqueous solution is a hydrochloric acid or citric acid aqueous solution containing a corrosion inhibitor to which fluoride is added. The corrosion inhibitor is used to protect equipment, piping, etc. from the corrosive properties of hydrochloric acid or citric acid aqueous solutions, and commercially available ones can be used. That is, as this type of corrosion inhibitor, those used when pickling boiler tubes and plant piping can be used. Hydrochloric acid and citric acid are effective in dissolving ash in coal, especially iron-based compounds, and fluoride is effective in dissolving silica-based compounds. However, both these acids and fluorides have a synergistic effect, and the greatest demineralization effect can be obtained when both are present in the same solution. The fluoride used herein is selected from the group consisting of acidic ammonium fluoride, ammonium fluoride, acidic sodium fluoride, sodium fluoride, acidic potassium fluoride, and potassium fluoride. Among these fluorides, acidic ammonium fluoride is the most effective for demineralization. This not only has a strong deashing effect, but also has the effect of not increasing the amount of sludge during subsequent wastewater treatment because it can be decomposed, unlike the case of sodium salts and potassium salts.

なお石炭中の灰分は、石炭中に夾雑物として存
在するものと、組織内に存在するものとがある。
前者は石炭の生成過程で外から混入したものであ
り、これは泥または石などである。この灰分は湿
式粉砕機2による破砕によつて石炭粒子の表面に
現われる。このため灰分は薬液と極めて効率よく
接触することになり、灰分の溶解がすみやかに行
なわれる。石炭の組織内に存在する灰分は、石炭
の原植物の生成期に導入されたものであり、これ
を取り除くことは非常に困難である。
Incidentally, the ash content in coal is divided into two types: one that exists as an impurity in the coal, and the other that exists within the coal's structure.
The former is what is mixed in from outside during the coal production process, such as mud or stones. This ash appears on the surface of the coal particles by crushing by the wet crusher 2. Therefore, the ash comes into contact with the chemical solution very efficiently, and the ash is quickly dissolved. The ash present in the coal tissue was introduced during the genesis of the coal's original plant, and it is extremely difficult to remove it.

また弗化物を含む塩酸またはクエン酸水溶液よ
りなる薬液は侵透力が強く、灰分中に侵入してい
くため、石炭と灰分との結合力を緩める役割を果
し、石炭自身を割れ易くするため総合的には粉砕
効率を上昇させる好結果を生む。灰分の溶解は灰
分と薬液との接触効率に影響されるが、このよう
な湿式粉砕機2内の状況は、この接触効率という
観点からはまさに理想的な条件を備えているとい
える。
In addition, chemical solutions consisting of hydrochloric acid or citric acid aqueous solutions containing fluorides have strong penetrating power and penetrate into the ash, so they play the role of loosening the binding force between coal and ash, making the coal itself more likely to crack. Overall, it produces good results that increase the crushing efficiency. The dissolution of ash is affected by the contact efficiency between the ash and the chemical solution, and it can be said that the situation inside the wet crusher 2 has ideal conditions from the viewpoint of this contact efficiency.

この湿式粉砕機2を出たスラリーは、つぎに分
級機3に導入される。この分級機3としては、格
別の制限はないが、たとえばレーキ分級機等が使
用可能である。分級機3において分離された粗粒
炭は混合槽1に再び供給される。所定の大きさに
なつた微粒炭と薬液とは脱水機4に導入され、そ
こで石炭と薬液に分離される。ここで脱水機4と
しては遠心分離機あるいは過機などが使用可能
である。そして薬液の大部分は再び薬液調製槽8
に戻されるが、その一部は抜き出され、排水処理
装置7で薬液中に溶解したSi、Al、Fe等の金属
イオン類をスラツジとして除去し、処理された溶
液は薬液調製槽8に戻され、循環使用される。
The slurry exiting the wet crusher 2 is then introduced into a classifier 3. Although there are no particular restrictions on the classifier 3, for example, a rake classifier or the like can be used. The coarse coal separated in the classifier 3 is supplied to the mixing tank 1 again. The granulated coal and the chemical liquid that have reached a predetermined size are introduced into a dehydrator 4, where they are separated into coal and the chemical liquid. Here, as the dehydrator 4, a centrifugal separator, a filtration machine, or the like can be used. Most of the chemical solution is then transferred to the chemical solution preparation tank 8 again.
A part of it is extracted, and the metal ions such as Si, Al, Fe, etc. dissolved in the chemical solution are removed as sludge in the wastewater treatment equipment 7, and the treated solution is returned to the chemical solution preparation tank 8. and used in circulation.

一方、脱水機4で脱水された石炭には、塩酸も
しくはクエン酸、さらには弗化物が付着している
ため、この石炭を洗浄槽5に導入する。そして洗
浄水を循環使用しながら、洗浄槽5内で石炭に付
着した薬液を洗浄する。なお洗浄槽5は必要に応
じて複数基設置する。十分に洗浄された石炭は洗
浄槽5から抜き出され、脱水機6に導かれる。な
お洗浄槽5に補給する水の量は、スラツジおよび
製品石炭に同伴して持ち出される水の量に対応す
るものである。またこのような水洗には従来の技
術が使用される。
On the other hand, since hydrochloric acid or citric acid and fluoride are attached to the coal dehydrated by the dehydrator 4, this coal is introduced into the cleaning tank 5. Then, the chemical solution adhering to the coal is cleaned in the cleaning tank 5 while circulating the cleaning water. Note that a plurality of cleaning tanks 5 may be installed as necessary. The thoroughly washed coal is extracted from the washing tank 5 and guided to a dehydrator 6. Note that the amount of water replenished into the cleaning tank 5 corresponds to the amount of water taken out together with the sludge and product coal. Also, conventional techniques are used for such washing.

つぎに脱水機6で脱水された石炭は必要に応じ
乾燥工程を経た後製品石炭となる。脱水機6で分
離された水は再び薬液調製槽8に戻される。薬液
調製槽8はデカンターの機能を併有している。こ
の調製槽8において薬液が所定の濃度となるよう
に薬剤を補給する。調製後の脱灰剤溶液は混合槽
1に再び供給される。
Next, the dehydrated coal in the dehydrator 6 undergoes a drying process if necessary, and then becomes product coal. The water separated by the dehydrator 6 is returned to the chemical solution preparation tank 8 again. The chemical liquid preparation tank 8 also has the function of a decanter. In this preparation tank 8, the drug is replenished so that the drug solution has a predetermined concentration. The prepared deashing agent solution is supplied to the mixing tank 1 again.

この発明は、上述の次第で、湿式粉砕機2にお
いて原料石炭を粉砕するのと同時に、塩酸もしく
はクエン酸に特定の弗化物が添加されてなる薬液
による脱灰が行なわれれるものであるから、石炭
の粉砕効率が向上するとともに、粉砕石炭と薬液
とが充分に撹拌されて、両者の接触が充分に行な
われ、したがつて脱灰率が高い。またこのように
石炭の粉砕操作と脱灰操作とが同時にしかも加熱
装置を必要とすることなく、常圧下で行なわれる
ため、脱灰操作に必要な各種の機器、並びに脱灰
反応槽の撹拌動力等も不要となり、経済性が非常
に高いという効果を奏する。
In this invention, as described above, raw coal is pulverized in the wet pulverizer 2, and at the same time, deashing is performed using a chemical solution made by adding a specific fluoride to hydrochloric acid or citric acid. The efficiency of coal pulverization is improved, and the pulverized coal and the chemical solution are sufficiently stirred to ensure sufficient contact between the two, resulting in a high deashing rate. In addition, since the coal pulverization and deashing operations are performed simultaneously and under normal pressure without the need for heating equipment, the various equipment necessary for the deashing operation as well as the stirring power for the deashing reaction tank are required. etc. are no longer necessary, resulting in a very economical effect.

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

図面はこの発明の実施例を示すフローシートで
ある。 1……混合槽、2……湿式粉砕機、3……分級
機、4……脱水機、5……洗浄槽、6……脱水
機、7……排水処理装置、8……薬液調製槽。
The drawing is a flow sheet showing an embodiment of the invention. 1... Mixing tank, 2... Wet crusher, 3... Classifier, 4... Dehydrator, 5... Washing tank, 6... Dehydrator, 7... Wastewater treatment equipment, 8... Chemical solution preparation tank .

Claims (1)

【特許請求の範囲】[Claims] 1 塩酸もしくはクエン酸水溶液に、酸性弗化ア
ンモン、弗化アンモン、酸性弗化ナトリウム、弗
化ナトリウム、酸性弗化カリウム、弗化カリウム
よりなる群の中から選ばれた弗化物が添加せられ
てなる脱灰用薬液と石炭とを混合する混合槽1
と、薬液中において石炭を粉砕する湿式粉砕器2
と、薬液中において粉砕された石炭のうち粗粒炭
を分離する分級機3と、脱灰された微粒炭と薬液
を含む混合溶液より微粒炭と薬液とを分離する脱
水機4と、脱灰処理後の薬液の一部を処理する排
水処理装置7と、薬液調製槽8とを備えており、
上記混合槽1において原料石炭と薬液とが混合せ
られ、これらの混合物が湿式粉砕機2に導入され
て、薬液中において石炭が粉砕せられると同時
に、薬液によつて石炭中の灰分が除去せられ、粉
砕された石炭と薬液との混合物が分級機3に導か
れて、粗粒炭が分離され、これが上記混合槽1に
返送せしめられ、この分級機3により取り出され
た脱灰微粒炭と薬液とを含む混合溶液が脱水機4
に導入されて、そこで脱灰微粒炭と薬液とに分離
され、脱灰処理後の薬液の大部分が薬液調製槽8
に送られ、かつ一部が排水処理装置7においてス
ラツジ除去せられたのち同調製槽8に送られ、こ
の調製槽8より薬液が混合槽1へ循環供給せられ
るようになされたことを特徴とする石炭の化学的
脱灰処理装置。
1. A fluoride selected from the group consisting of acidic ammonium fluoride, ammonium fluoride, acidic sodium fluoride, sodium fluoride, acidic potassium fluoride, and potassium fluoride is added to an aqueous solution of hydrochloric acid or citric acid. Mixing tank 1 for mixing the deashing chemical and coal
and a wet crusher 2 that crushes coal in a chemical solution.
, a classifier 3 that separates coarse coal from the pulverized coal in a chemical solution, a dehydrator 4 that separates the fine coal from the chemical solution from a mixed solution containing the deashed granule coal and the chemical solution, and a deashing machine. It is equipped with a wastewater treatment device 7 that processes a part of the chemical solution after treatment, and a chemical solution preparation tank 8.
Raw coal and a chemical solution are mixed in the mixing tank 1, and this mixture is introduced into a wet pulverizer 2, where the coal is pulverized in the chemical solution and, at the same time, the ash content in the coal is removed by the chemical solution. The mixture of the pulverized coal and the chemical solution is led to the classifier 3, where coarse coal is separated, and this is returned to the mixing tank 1, where it is separated from the deashed fine coal taken out by the classifier 3. The mixed solution containing the chemical solution is sent to the dehydrator 4.
is introduced into the chemical solution preparation tank 8, where it is separated into deashed pulverized coal and the chemical solution, and most of the chemical solution after the deashing process is transferred to the chemical solution preparation tank 8.
A part of the chemical solution is sent to the wastewater treatment equipment 7 for sludge removal and then sent to the preparation tank 8, from which the chemical solution is circulated and supplied to the mixing tank 1. Coal chemical deashing treatment equipment.
JP5742781A 1981-03-13 1981-04-15 Device for chemical removal of ash from coal Granted JPS57171000A (en)

Priority Applications (8)

Application Number Priority Date Filing Date Title
JP5742781A JPS57171000A (en) 1981-04-15 1981-04-15 Device for chemical removal of ash from coal
US06/356,337 US4424062A (en) 1981-03-13 1982-03-09 Process and apparatus for chemically removing ash from coal
NZ199964A NZ199964A (en) 1981-03-13 1982-03-09 A process for chemically removing ash from coal
GB8206972A GB2094830B (en) 1981-03-13 1982-03-10 Process and apparatus for chemically removing ash from coal with acid and nh4f
DE3208704A DE3208704C2 (en) 1981-03-13 1982-03-11 Process for the chemical removal of ash from coal and devices for carrying out this process
CA000398285A CA1169800A (en) 1981-03-13 1982-03-12 Process and apparatus for chemically removing ash from coal
AU81348/82A AU532092B2 (en) 1981-03-13 1982-03-12 Deashing coal with acid ammonium chloride
BR8201410A BR8201410A (en) 1981-03-13 1982-03-15 PROCESS AND APPARATUS TO REMOVE CHARCOAL ASH FROM CHEMICAL

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP5742781A JPS57171000A (en) 1981-04-15 1981-04-15 Device for chemical removal of ash from coal

Publications (2)

Publication Number Publication Date
JPS57171000A JPS57171000A (en) 1982-10-21
JPS6259759B2 true JPS6259759B2 (en) 1987-12-12

Family

ID=13055350

Family Applications (1)

Application Number Title Priority Date Filing Date
JP5742781A Granted JPS57171000A (en) 1981-03-13 1981-04-15 Device for chemical removal of ash from coal

Country Status (1)

Country Link
JP (1) JPS57171000A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0587262U (en) * 1991-04-15 1993-11-26 川崎重工業株式会社 Fuel supply system for small planing boats

Family Cites Families (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS50151201A (en) * 1974-05-23 1975-12-04
DE2611620C2 (en) * 1976-03-19 1982-11-11 Carl Still Gmbh & Co Kg, 4350 Recklinghausen Process for the removal of ash components from ash-rich coals

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0587262U (en) * 1991-04-15 1993-11-26 川崎重工業株式会社 Fuel supply system for small planing boats

Also Published As

Publication number Publication date
JPS57171000A (en) 1982-10-21

Similar Documents

Publication Publication Date Title
US4424062A (en) Process and apparatus for chemically removing ash from coal
JP4414394B2 (en) Method for desalting coal
WO2008052465A1 (en) A sintered flue gas wet desulfurizing and dedusting process
CN110314923A (en) A kind of method of reinforced aluminum ash desalination denitrogenation
CN109135838B (en) Coal water slurry circulating gasification system and method
AU602009B2 (en) Chemical benefication of coal
JPS5953215B2 (en) Method for producing alkali metal silicates
JP6637657B2 (en) Fly ash processing apparatus and processing method
JPS6259759B2 (en)
JP3284861B2 (en) Waste treatment method for cement raw materials
JP4194001B2 (en) Acid gas treatment agent and waste gas treatment method using the same
JPS62276095A (en) Recovery of caustic soda from alkali pulp waste liquid
US5312462A (en) Moist caustic leaching of coal
JPS6259758B2 (en)
CA1130231A (en) Coal recovery process
JP4071887B2 (en) Waste melting slag treatment method and apparatus
EP0060354B1 (en) Method of treating coal to remove sulphur and ash
JP2002029738A (en) Calcium hydroxide and acidic gas treating agent by using the same
JP4480317B2 (en) Aluminosilicate soda treatment method
JP2004507351A (en) Treatment of bottom ash from waste incineration plant
JPS6259757B2 (en)
JPH10277384A (en) Preparation of high efficiency acidic gas-treating agent
JPS58141295A (en) Coal slurry deashing transportation method
JPS631999B2 (en)
CN117923500A (en) A method for comprehensive utilization of wastewater from ultrapure quartz sand production