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JPS626853B2 - - Google Patents
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JPS626853B2 - - Google Patents

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Publication number
JPS626853B2
JPS626853B2 JP55031247A JP3124780A JPS626853B2 JP S626853 B2 JPS626853 B2 JP S626853B2 JP 55031247 A JP55031247 A JP 55031247A JP 3124780 A JP3124780 A JP 3124780A JP S626853 B2 JPS626853 B2 JP S626853B2
Authority
JP
Japan
Prior art keywords
activated carbon
powdered activated
tube
reactivated
combustion
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
JP55031247A
Other languages
Japanese (ja)
Other versions
JPS56129605A (en
Inventor
Okitsugu Shinobu
Yoshiki Uchama
Sho Hashimoto
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.)
JGC Corp
Original Assignee
JGC Corp
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 JGC Corp filed Critical JGC Corp
Priority to JP3124780A priority Critical patent/JPS56129605A/en
Publication of JPS56129605A publication Critical patent/JPS56129605A/en
Publication of JPS626853B2 publication Critical patent/JPS626853B2/ja
Granted legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/10Process efficiency

Landscapes

  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)
  • Carbon And Carbon Compounds (AREA)

Description

【発明の詳細な説明】[Detailed description of the invention]

本発明は、使用ずみの粉末活性炭を再活性化す
る方法の改良に関する。本発明はまた、この方法
の実施に使用するに適した再活性化装置にも関す
る。 粉末状の活性炭は、粒状その他の成型活性炭に
くらべて安価であり、吸着速度もはるかな速いな
どの利点があるので、たとえば排水の高次処理に
おいて微量の有機物を吸着除去するといつた用途
がある。しかし、使用ずみの粉末活性炭を再度活
性化してくり返し使用できるようにする好適な方
法が確立されているとはいえず、これが粉末活性
炭の工業的利用に制約を与えていた。 従来実施され、または提案された粉末状活性炭
の再活性化技術は、多くは内熱式とよばれるもの
であつて、調節された微量の酸素を含有する高温
燃焼排ガスおよびスチームと活性炭とを直接接触
させることにより、被吸着物の酸化や熱分解をひ
きおこして、再活性化を行なうという方式であ
る。この方式は、活性炭の燃焼ロスを避けられな
いため回収率が低いという欠点があり、また実施
に当つては、酸素濃度を厳しくコントロールする
必要がある。 そのような問題を避けて粉末活性炭の再活性化
をする技術として、外熱式とよばれる、外部から
の間接加熱により600〜1000℃の高温を与え、ス
チームで再活性化することが考えられた。たとえ
ば、特公昭52−19200号には、粉末活性炭のスラ
リーを水蒸気で噴霧し、外部からの加熱により噴
霧されたスラリー滴中の水を気化させ、それによ
り生成した水蒸気と噴霧用の水蒸気とを利用して
再活性化を行なうことが開示されている。 本発明者らは、外熱式の利点を生かし、水蒸気
による粉末活性炭スラリーの噴霧のための特殊な
ノズルを必要とせず、噴霧用の水蒸気を別に用意
しないですむ再活性化の技術を確立すべく研究を
重ねた。その過程で、加熱されている管の一端に
水性スラリーを送り込むと、そこで水が気化して
水蒸気となり、含まれていた粉末がその中に懸濁
した固−気混合物が形成され、水の気化と高い温
度により生じた急激な体積膨脹のため、この固−
気混合物は高速で管の他端に向つて移動しそこか
ら噴出すること、そして、少なくとも粉末活性炭
のスラリーに関する限り、管の閉塞を招くことな
く上記の変化を連続的に実現できることを知つ
た。この研究は、スラリーまたは粉末の取扱いに
伴いがちな装置の閉塞のトラブルが皆無であるこ
とをめざすばかりでなく、熱効率の改善をも目標
とした。活性炭の熱的再活性化を工業的に実施す
る際に、熱効率の高低はそのコストを左右する重
要な因子である。 こうした狙いは、本発明により達成された。 本発明の粉末活性炭を再活性化する方法は、再
活性化すべき粉末活性炭の水性スラリーを、外部
から加熱されている筒内を撹拌下に流下させ、水
分の蒸発により乾燥した粉末活性炭が水蒸気中に
浮遊する固−気混合物を形成し、この混合物を外
部から燃焼ガスにより加熱されている活性化管内
を移動させつつ昇温して、被吸着物質を脱着ある
いは熱分解させるとともに、前記の水蒸気により
粉末活性炭を再活性化し、ついで再活性化された
粉末活性炭を水蒸気から分離回収することからな
る。 本発明の粉末活性炭を再活性化する装置は、再
活性化すべき粉末活性炭の水性スラリーを送給す
る手段、内部にスラリーの撹拌機を、そして外部
に加熱用ジヤケツトをそなえ、乾燥した粉末活性
炭が水蒸気中に浮遊する固−気混合物を形成する
ための乾燥筒、この固−気混合物を受入れ外部か
らの加熱により前記水蒸気で粉末活性炭を活性化
する活性化管、再活性化された粉末活性炭を回収
する分離槽、ならびに燃焼ガスにより前記活性化
管を加熱する炉からなる。 以下、図面を参照して本発明の代表的な態様を
説明する。 第1図において、使用ずみ粉末活性炭は、スラ
リー調整タンク2において、適宜の濃度のスラリ
ー1Aにされ、スラリーポンプ3により、スラリ
ー乾燥筒4の上端4Aに送り込まれる。処理すべ
き粉末活性炭の粒径は通常は約60メツシユ以下で
あり、スラリーの濃度は5〜50重量%の範囲内と
する。50%を超えるものは取扱いが困難である
し、5%よりうすいものは再活性化に消費する熱
エネルギーが過大となつて、本発明の目的に合致
しない。10〜35%の範囲内のものが適当である。 スラリー乾燥筒は、外側にジヤケツト5が設け
てあり、その中を粉末活性炭の活性化に利用した
後の燃焼排ガスを通して、スラリーを加熱する。
筒の内部には回転軸に多数のロツドを植えた撹拌
機があり、可変速度モーター(図示してない)に
よつて駆動され、スラリーを筒の壁に押しつけた
りかき取つたりしてスラリーの固着を回避すると
共にその乾燥を促す。撹拌下にスラリーは乾燥筒
4内を少しずつ流下し、下端4Bに至るころには
ほとんどの水分が気化して、粉末活性炭が水蒸気
中に浮遊する固−気混合物が形成される。この固
−気混合物は、400℃以上、好ましくは600℃以上
の温度で活性化管7に入る。 活性化管7は加熱炉8内におかれ、バーナー9
A,9B,9Cおよび9Dにより加熱される。図
示した例ではこの管は二重管構造であつて、外管
7Aと内管7Bとの間を上記の混合物が高速で流
下し、燃焼ガスは外管7Aを外側から加熱したの
ち、通路7Cを通つて内管7Bの内側を上昇して
さらに加熱を続け、前記した乾燥筒のジヤケツト
5に至る。二重管構造の詳細、とくに下部の燃焼
ガス通路7C付近は、第2図に示すとおりであ
る。 水蒸気中に浮遊している粉末活性炭は、活性化
管7内を高速で流下する間に、被吸着物の脱着や
熱分解、酸化が起り、ついで水蒸気の作用により
再活性化が行なわれる。この部分で必要な温度お
よび滞留時間は、浮遊粉末濃度(換言すればスラ
リー濃度)、被吸着物質の種類および吸着量など
によつても異なるが、700℃以上の温度と長くと
も30秒間、好ましくは1〜10秒間の滞留とが適当
である。活性化は高温の方が速やかであるが、
1000℃以上では粉末活性炭の酸化によるロスが多
くなるし、装置の耐久性の点からも実用的とはい
えない。通常は700〜900℃、とくに800℃程度が
望ましい。活性化管内の操作圧力は特に限定され
るものではないが常圧から数Kg/cm2G程度までの
加圧下に操業することができ、これは装置のコン
パクト化に役立ち、または十分な滞留時間を得る
にも有用である。 再活性化された粉末活性炭は、水蒸気および再
活性化に伴つて発生し、脱着した吸着物質とその
分解生成物からなるガスとともに活性化管7を
出、好ましくは図示したように燃焼用の空気に熱
交換器10で熱を与えたのち、分離槽11に入
る。 ここで、上部に設けたスプレーノズル12から
の冷水により粉末活性炭は分離され、同時に水蒸
気の一部も凝縮し、再びスラリーを形成して回収
される。 再活性化により発生したガスは、図示したよう
に、ブロア13で吸引して再度形成された粉末活
性炭のスラリーに移行することを防ぎ、加熱炉内
に送つて燃焼処理する。 本発明は、上記した例のほかに多くの変更態様
があり得る。たとえば、スラリー乾燥筒の撹拌機
6として、第3図に示すような、多数のロツド6
2を植えた軸61を2本組み合わせたものを用い
ることが推奨される。2本の軸のロツドを互いち
がいに植え、両者を接触はしないように近接して
同方向に回転させれば、ロツドに付着したスラリ
ーまたは粉末を常にかき落とすことができる。ま
た、乾燥筒の方向も、図示したより傾斜の急なも
の、極端には垂直のものであつても、乾燥した粉
末活性炭が水蒸気中に浮遊する固−気混合物が形
成される限り差支えない。これは、乾燥筒の長さ
を十分にとることや、撹拌機の回転を比較的速く
してスラリーが遠心力で筒の壁に打ちつけられ、
加熱が効率的に行なわれるようにすることによつ
て実現する。 活性化管も、小容量の装置においては単管、と
くに第4図に示すようなコイル状に形成したもの
でもよく、また熱交換器のような多管式の構造を
とることもできる。これらの態様を含めて、加熱
炉のバーナーは、局部的な過熱を避けるよう、切
線方向に配置するなどの配慮が望ましい。 乾燥筒のジヤケツトも、実質上その周囲から燃
焼排ガスによる加熱が行なわれさえすればよいか
ら、第1図や第3図に示した構造に限らず、第4
図に示すように、乾燥筒の全部または一部を再活
性化管を加熱する炉の内部におさめた構造にし
て、同じ効果を得ることができる。本発明でジヤ
ケツトとは、そのようなものも包含する。 さらに、再活性化された粉末活性炭の回収も、
必らずしもスラリーを形成する必要はなく、冷空
気である程度まで冷却してからバツグフイルター
やサイクロンなどを用いて乾燥状態で回収するこ
ともできるし、粉末活性炭を冷却した水がすべて
蒸発し去る程度にスプレーの水量を調節して、上
記の乾式回収手段を利用することもできる。 本発明によるときは、外熱式の再活性化の利益
をすべて享受した上、再生のために別に水蒸気を
発生させる必要はなく、そして特殊な噴霧装置を
使わないのでスラリー濃度の変動や流量変動に対
しても安定で、しかも装置の閉塞のおそれからも
解放される、という効果が得られる。しかも粉末
活性炭は再活性の管内を乱流状態で移動して加熱
されるので、熱伝導が良好で、全体がむらなく再
活性化され、高い再活性化率が容易に得られる。
高い熱効率を実現できるから、再活性化のコスト
を低減でき、粉末活性炭の工業的使用の可能性を
ひろげる。再活性化された粉末活性炭は、所望に
より、スラリー状態でも、また乾燥状態でも回収
できる。再活性化により到達する活性は、次に示
す実例にみるとおり高い。 実施例 1 第4図に示した構成の、スラリー乾燥筒が垂直
であつてその大部分が加熱炉内に入つており、か
つ活性化管がコイル状の単管である実験室規模の
装置を用いて、60〜400メツシユの粉末活性炭に
パラニトロフエノール(試薬特級)を190mg/g
吸着させたものを模擬使用ずみ活性炭とし、その
再活性化を種々の温度で試みた。装置に送給した
スラリー濃度は20重量%、活性化管内滞留時間は
約1秒間である。 再活性化した粉末活性炭について、ヨウ素吸着
量およびM.B.(メチレンブルー)脱色力を測定
した。前者はJIS K1474「粒状活性炭試験方法」
に準じた方法により、また後者はJIS K1470「粉
末活性炭試験方法」に定める方法に従つた。その
結果は次のとおりである。
The present invention relates to an improved method for reactivating used powdered activated carbon. The invention also relates to a reactivation device suitable for use in carrying out this method. Powdered activated carbon has the advantage of being cheaper and having a much faster adsorption speed than granular or other shaped activated carbon, so it has applications such as adsorption and removal of trace amounts of organic matter in higher-level treatment of wastewater. . However, no suitable method has been established for reactivating used powdered activated carbon so that it can be used repeatedly, and this has placed restrictions on the industrial use of powdered activated carbon. Most of the reactivation technologies for powdered activated carbon that have been implemented or proposed in the past are of the so-called internal heating type, in which activated carbon is directly heated with controlled high-temperature combustion exhaust gas and steam containing a trace amount of oxygen. This is a method in which the adsorbed material is brought into contact with the adsorbent to cause oxidation and thermal decomposition, thereby reactivating it. This method has the disadvantage that the recovery rate is low because combustion loss of activated carbon cannot be avoided, and when implementing it, it is necessary to strictly control the oxygen concentration. As a technique for reactivating powdered activated carbon to avoid such problems, it is thought to use a so-called external heating method, which applies indirect heating from the outside to a high temperature of 600 to 1000℃ and reactivates it with steam. Ta. For example, in Japanese Patent Publication No. 52-19200, a slurry of powdered activated carbon is atomized with water vapor, the water in the sprayed slurry droplets is vaporized by external heating, and the resulting water vapor is combined with the water vapor for spraying. It is disclosed that reactivation can be carried out using the same method. The present inventors took advantage of the external heating method to establish a reactivation technology that does not require a special nozzle for spraying powdered activated carbon slurry with water vapor, and does not require separate preparation of water vapor for spraying. I did a lot of research. In the process, an aqueous slurry is pumped into one end of the heated tube, where the water evaporates to steam, forming a solid-gas mixture with the contained powder suspended in it, and the water evaporates. Due to the rapid volume expansion caused by high temperatures, this solid
It has been found that the gas mixture moves at high speed towards the other end of the tube and is ejected therefrom, and that, at least as far as the slurry of powdered activated carbon is concerned, the above changes can be achieved continuously without causing blockage of the tube. This research aimed not only to eliminate the problems of equipment clogging that often accompany slurry or powder handling, but also to improve thermal efficiency. When carrying out thermal reactivation of activated carbon industrially, the level of thermal efficiency is an important factor that influences the cost. These aims have been achieved by the present invention. The method of reactivating powdered activated carbon of the present invention is to flow an aqueous slurry of powdered activated carbon to be reactivated through an externally heated cylinder while stirring, and dry powdered activated carbon by evaporation of water into steam. This mixture is moved through an activation tube that is heated by combustion gas from the outside, and the temperature is raised to desorb or thermally decompose the adsorbed substance, and the water vapor It consists of reactivating powdered activated carbon and then separating and recovering the reactivated powdered activated carbon from water vapor. The apparatus for reactivating powdered activated carbon of the present invention comprises a means for feeding an aqueous slurry of powdered activated carbon to be reactivated, an internal slurry stirrer, and an external heating jacket. a drying tube for forming a solid-gas mixture suspended in water vapor; an activation tube for receiving this solid-gas mixture and activating powdered activated carbon with the water vapor by heating from the outside; It consists of a separation tank for recovery and a furnace for heating the activation tube with combustion gas. Hereinafter, typical aspects of the present invention will be described with reference to the drawings. In FIG. 1, used powdered activated carbon is made into a slurry 1A of an appropriate concentration in a slurry adjustment tank 2, and is sent to an upper end 4A of a slurry drying cylinder 4 by a slurry pump 3. The particle size of the powdered activated carbon to be treated is typically less than about 60 mesh, and the slurry concentration is within the range of 5 to 50% by weight. If it exceeds 50%, it will be difficult to handle, and if it is thinner than 5%, the thermal energy consumed for reactivation will be excessive, and this will not meet the purpose of the present invention. A range of 10 to 35% is suitable. The slurry drying cylinder is provided with a jacket 5 on the outside, and the slurry is heated by passing the combustion exhaust gas used for activating the powdered activated carbon through the jacket 5.
Inside the cylinder is an agitator with a number of rods mounted on a rotating shaft, which is driven by a variable speed motor (not shown) to push and scrape the slurry against the walls of the cylinder. Avoids sticking and promotes drying. The slurry flows down the drying cylinder 4 little by little while being stirred, and by the time it reaches the lower end 4B, most of the water has evaporated, forming a solid-gas mixture in which powdered activated carbon is suspended in water vapor. This solid-gas mixture enters the activation tube 7 at a temperature above 400°C, preferably above 600°C. The activation tube 7 is placed in a heating furnace 8 and a burner 9
Heated by A, 9B, 9C and 9D. In the illustrated example, this pipe has a double pipe structure, and the above mixture flows down at high speed between the outer pipe 7A and the inner pipe 7B, and the combustion gas heats the outer pipe 7A from the outside, and then passes through the passage 7C. It passes through and rises inside the inner tube 7B and continues to be heated, reaching the jacket 5 of the drying tube described above. The details of the double pipe structure, especially the vicinity of the lower combustion gas passage 7C, are as shown in FIG. While the powdered activated carbon suspended in the steam flows down the activation pipe 7 at high speed, adsorbed substances are desorbed, thermally decomposed, and oxidized, and then reactivated by the action of the steam. The temperature and residence time required in this part vary depending on the suspended powder concentration (in other words, the slurry concentration), the type of substance to be adsorbed, the amount of adsorption, etc., but preferably a temperature of 700°C or higher and 30 seconds at the longest. A residence time of 1 to 10 seconds is appropriate. Activation is faster at high temperatures, but
If the temperature exceeds 1000°C, there will be a lot of loss due to oxidation of the powdered activated carbon, and it is not practical in terms of the durability of the device. Normally, the temperature is preferably 700 to 900°C, especially about 800°C. The operating pressure inside the activation tube is not particularly limited, but it can be operated from normal pressure to several kg/cm 2 G, which helps to make the device more compact, or if the residence time is sufficient. It is also useful to obtain The reactivated powdered activated carbon exits the activation tube 7 together with water vapor and the gas generated during the reactivation, consisting of the desorbed adsorbent and its decomposition products, and is preferably supplied with combustion air as shown. After being given heat by a heat exchanger 10, it enters a separation tank 11. Here, the powdered activated carbon is separated by cold water from the spray nozzle 12 provided at the top, and at the same time, a portion of the water vapor is also condensed, forming a slurry again and recovering it. As shown in the figure, the gas generated by the reactivation is sucked in by a blower 13 to prevent it from transferring to the re-formed slurry of powdered activated carbon, and is sent into a heating furnace for combustion treatment. The present invention may have many modifications in addition to the examples described above. For example, a large number of rods 6 as shown in FIG.
It is recommended to use a combination of two shafts 61 planted with 2. If the rods on the two shafts are placed at different angles and rotated in the same direction in close proximity without touching each other, slurry or powder adhering to the rods can be constantly scraped off. Furthermore, the direction of the drying cylinder may be steeper than that shown in the drawings, or even vertical in the extreme, as long as a solid-vapor mixture in which dried powdered activated carbon is suspended in water vapor is formed. This is achieved by making the drying cylinder long enough and rotating the stirrer relatively fast so that the slurry is hit against the wall of the cylinder by centrifugal force.
This is achieved by ensuring efficient heating. The activation tube may also be a single tube in a small-capacity device, especially one formed in a coil shape as shown in FIG. 4, or a multi-tube structure such as a heat exchanger. Including these aspects, it is desirable that the burners of the heating furnace be arranged in the tangential direction to avoid local overheating. Since the jacket of the drying tube only needs to be heated by the combustion exhaust gas from the surrounding area, it is not limited to the structure shown in Figs. 1 and 3.
As shown in the figure, the same effect can be obtained by placing all or part of the drying tube inside the furnace that heats the reactivation tube. In the present invention, the jacket includes such a jacket. Furthermore, the recovery of reactivated powdered activated carbon is also possible.
It is not always necessary to form a slurry; it is possible to cool it to a certain level with cold air and then collect it in a dry state using a bag filter or cyclone, or if all the water used to cool the powdered activated carbon evaporates. It is also possible to use the above-mentioned dry recovery means by adjusting the amount of water sprayed to the extent that the amount of water is removed. According to the present invention, in addition to enjoying all the benefits of external heating type reactivation, there is no need to separately generate steam for regeneration, and no special spraying equipment is used, so slurry concentration fluctuations and flow rate fluctuations The effect is that the device is stable and free from the possibility of clogging the device. Moreover, since the powdered activated carbon moves in a turbulent state within the reactivation tube and is heated, it has good heat conduction, and the entire activated carbon is evenly reactivated, making it easy to obtain a high reactivation rate.
Since high thermal efficiency can be achieved, the cost of reactivation can be reduced and the possibility of industrial use of powdered activated carbon is expanded. The reactivated powdered activated carbon can be recovered in slurry or dry form, if desired. The activity achieved by reactivation is high as shown in the following example. Example 1 A laboratory-scale device was constructed as shown in FIG. 4, in which the slurry drying tube was vertical and most of it was inside the heating furnace, and the activation tube was a coiled single tube. 190 mg/g of paranitrophenol (reagent special grade) was added to 60 to 400 mesh powdered activated carbon.
The adsorbed material was used as a simulated activated carbon, and its reactivation was attempted at various temperatures. The slurry concentration fed to the device was 20% by weight, and the residence time in the activation tube was about 1 second. The iodine adsorption amount and MB (methylene blue) decolorizing power of the reactivated powder activated carbon were measured. The former is JIS K1474 "Test method for granular activated carbon"
The latter was conducted in accordance with the method specified in JIS K1470 "Powdered Activated Carbon Test Method". The results are as follows.

【表】 実施例 2 コークス炉排水を処理し、CODMo200mg/gま
で吸着させた粉末活性炭(60メツシユ以下)を、
同じ装置を用い、種々のスラリー濃度で送給して
再活性化した。活性化温度は800℃、管内滞留時
間は約1秒間である。その結果を次に示す。
[Table] Example 2 Powdered activated carbon (60 mesh or less) treated with coke oven wastewater and adsorbed up to 200 mg/g of COD Mo ,
The same equipment was used to deliver and reactivate various slurry concentrations. The activation temperature is 800°C, and the residence time in the tube is about 1 second. The results are shown below.

【表】 実施例 3 例2と同じ粉末活性炭で石油化学工場の総合排
水処理し、CODMo200mg/gを吸着させたもの
を、同じ装置で、異なる活性化温度で再活性化し
た。スラリー濃度は20重量%、活性化管滞留時間
はやはり約1秒間である。その結果は下記のとお
り。
[Table] Example 3 Comprehensive wastewater treatment from a petrochemical factory was performed using the same powdered activated carbon as in Example 2, and 200 mg/g of COD Mo was adsorbed, and the waste was reactivated using the same equipment at different activation temperatures. The slurry concentration is 20% by weight and the activation tube residence time is also about 1 second. The results are as follows.

【表】 実施例 4 ドデシルベンゼンスルホン酸ナトリウムを100
mg/g吸着させた粉末活性炭(60〜400メツシ
ユ)を、スラリー濃度20重量%、活性化温度800
℃、滞留時間約1秒間の条件で再活性化した。下
記のとおり、新炭をこえる高い再生率が得られ
た。
[Table] Example 4 Sodium dodecylbenzenesulfonate 100%
Powdered activated carbon (60 to 400 mesh) adsorbed mg/g was prepared at a slurry concentration of 20% by weight and an activation temperature of 800%.
Reactivation was carried out under conditions of temperature and residence time of about 1 second. As shown below, a higher regeneration rate than fresh coal was obtained.

【表】 実施例 5 例1と同じ粉末活性炭に、やはりパラニトロフ
エノールを190mg/g吸着させたものを、濃度20
重量%のスラリーにして同じ装置に送給し、800
℃の活性化温度、ただし滞留時間を変化させて再
活性化した。その結果、次の成績が得られた。
[Table] Example 5 The same powdered activated carbon as in Example 1, which also had 190 mg/g of paranitrophenol adsorbed, was used at a concentration of 20
800% by weight slurry and fed into the same equipment.
Reactivation was performed at an activation temperature of °C, but with varying residence times. As a result, the following results were obtained.

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

第1図は、本発明の粉末活性炭を再活性化する
装置の代表的な例を示す系統図である。第2図
A,BおよびCは、第1図の活性化管の主要部の
構造を示す図であつて、Aは縦断面図、BはAの
−位置、Cは−位置における横断面図で
ある。第3図AおよびBは、スラリー乾燥筒の別
の態様を示す図であつて、Aは縦断面図、Bは横
断面図である。第4図は、本発明の装置の別の例
であつて実施例に用いたものを示す断面図であ
る。 1A……使用ずみ粉末活性炭のスラリー、1B
……再活性化された粉末活性炭のスラリー、4…
…スラリー乾燥筒、7……活性化管、8……加熱
炉、11……分離槽。
FIG. 1 is a system diagram showing a typical example of an apparatus for reactivating powdered activated carbon of the present invention. 2A, B, and C are views showing the structure of the main part of the activation tube in FIG. 1, in which A is a longitudinal cross-sectional view, B is a -position of A, and C is a cross-sectional view at a -position. It is. FIGS. 3A and 3B are views showing another embodiment of the slurry drying cylinder, in which A is a longitudinal cross-sectional view and B is a cross-sectional view. FIG. 4 is a cross-sectional view showing another example of the device of the present invention, which was used in an example. 1A...Slurry of used powdered activated carbon, 1B
...Reactivated powdered activated carbon slurry, 4...
... Slurry drying cylinder, 7 ... Activation tube, 8 ... Heating furnace, 11 ... Separation tank.

Claims (1)

【特許請求の範囲】 1 再活性化すべき粉末活性炭の水性スラリー
を、外部から加熱されている筒内を撹拌下に流下
させ、水分の蒸発により乾燥した粉末活性炭が水
蒸気中に浮遊する固−気混合物を形成し、この混
合物を外部から燃焼ガスにより加熱されている活
性化管内を移動させつつ昇温して、被吸着物質を
脱着あるいは熱分解させるとともに、前記の水蒸
気により粉末活性炭を再活性化し、ついで再活性
化された粉末活性炭を水蒸気から分離回収するこ
とからなる粉末活性炭を再活性化する方法。 2 乾燥筒の加熱を活性化管を加熱した燃焼廃ガ
スにより行なう特許請求の範囲第1項の方法。 3 粉末活性炭の水性スラリーを濃度10〜35重量
%で乾燥筒内に送給し、活性化管における混合物
の加熱温度を700〜900℃、その滞留時間を1〜10
秒間とする特許請求の範囲第1項の方法。 4 再活性化された粉末活性炭に対して水をスプ
レーして急冷するとともに水蒸気を凝縮させる特
許請求の範囲第1項の方法。 5 水スプレーにより急冷された再活性化粉末活
性炭および凝縮した水と分離した脱着物もしくは
その分解生成物を含むガスを活性化管の加熱のた
めの燃焼により処理する特許請求の範囲第4項の
方法。 6 再活性化すべき粉末活性炭の水性スラリーを
送給する手段、内部にスラリーの撹拌機を、そし
て外部に加熱用ジヤケツトをそなえ、乾燥した粉
末活性炭が水蒸気中に浮遊する固−気混合物を形
成するための乾燥筒、この固−気混合物を受入れ
外部からの加熱により前記水蒸気で粉末活性炭を
活性化する活性化管、再活性化された粉末活性炭
を回収する分離槽、ならびに燃焼ガスにより前記
活性化管を加熱する炉からなる粉末活性炭を再活
性化する装置。 7 炉の廃ガスをジヤケツトの熱媒として利用す
る特許請求の範囲第6項の装置。 8 スラリーの撹拌機が回転軸に多数のパドルま
たはロツドを植えたものである特許請求の範囲第
6項の装置。 9 スラリーの撹拌機が近接して同方向に回転す
る二本の軸に多数のロツドを植えたものである特
許請求の範囲第6項の装置。 10 活性化管が二重管構造であつて、その外管
の外側および内管の内側を燃焼ガスが流れて加熱
するように構成した特許請求の範囲第6項の装
置。 11 粉末活性炭の活性化を終えた固−気混合物
を燃焼用の空気と熱交換する装置を備えた特許請
求の範囲第6項の装置。 12 分離槽で粉末活性炭と分離したガスを燃焼
装置に送つて燃焼処理をするように構成した特許
請求の範囲第6項の装置。
[Claims] 1. An aqueous slurry of powdered activated carbon to be reactivated is allowed to flow down an externally heated cylinder with stirring, and the dried powdered activated carbon is formed into solid air suspended in water vapor by evaporation of moisture. A mixture is formed, and this mixture is moved through an activation tube heated by combustion gas from the outside and heated to desorb or thermally decompose the adsorbed substance, and the powdered activated carbon is reactivated by the water vapor. , and then separating and recovering the reactivated powdered activated carbon from water vapor. 2. The method according to claim 1, wherein the drying tube is heated by the combustion waste gas that heated the activation tube. 3. Feed an aqueous slurry of powdered activated carbon into the drying tube at a concentration of 10 to 35% by weight, heat the mixture in the activation tube at a temperature of 700 to 900°C, and set the residence time to 1 to 10%.
The method according to claim 1, wherein the time period is within seconds. 4. The method according to claim 1, in which the reactivated powdered activated carbon is sprayed with water to rapidly cool it and condense water vapor. 5. The reactivated powdered activated carbon rapidly cooled by water spray and the gas containing the desorbed product or its decomposition product separated from the condensed water are treated by combustion for heating the activation tube. Method. 6. Means for delivering an aqueous slurry of powdered activated carbon to be reactivated, with an internal slurry agitator and an external heating jacket to form a solid-gas mixture in which dried powdered activated carbon is suspended in water vapor. a drying tube for receiving this solid-gas mixture and activating the powdered activated carbon with the steam by heating from the outside, a separation tank for recovering the reactivated powdered activated carbon, and a drying tube for receiving the solid-gas mixture and activating the powdered activated carbon with the steam using combustion gas. A device for reactivating powdered activated carbon, consisting of a furnace that heats a tube. 7. The device according to claim 6, which utilizes waste gas from the furnace as a heat medium for the jacket. 8. The device according to claim 6, wherein the slurry agitator has a number of paddles or rods installed on a rotating shaft. 9. The device according to claim 6, wherein the slurry agitator has a large number of rods installed on two shafts that rotate in the same direction in close proximity. 10. The device according to claim 6, wherein the activation tube has a double tube structure, and the combustion gas is heated by flowing outside the outer tube and inside the inner tube. 11. The device according to claim 6, comprising a device for exchanging heat between the solid-gas mixture after the activation of the powdered activated carbon and combustion air. 12. The device according to claim 6, which is configured to send the gas separated from the powdered activated carbon in the separation tank to a combustion device for combustion treatment.
JP3124780A 1980-03-12 1980-03-12 Method and apparatus for reactivating powdered activated carbon Granted JPS56129605A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP3124780A JPS56129605A (en) 1980-03-12 1980-03-12 Method and apparatus for reactivating powdered activated carbon

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP3124780A JPS56129605A (en) 1980-03-12 1980-03-12 Method and apparatus for reactivating powdered activated carbon

Publications (2)

Publication Number Publication Date
JPS56129605A JPS56129605A (en) 1981-10-09
JPS626853B2 true JPS626853B2 (en) 1987-02-13

Family

ID=12326036

Family Applications (1)

Application Number Title Priority Date Filing Date
JP3124780A Granted JPS56129605A (en) 1980-03-12 1980-03-12 Method and apparatus for reactivating powdered activated carbon

Country Status (1)

Country Link
JP (1) JPS56129605A (en)

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5162275A (en) * 1982-05-24 1992-11-10 Custom Equipment Corporation Low temperature kiln carbon reactivation
ZA872043B (en) * 1986-03-27 1987-11-25 Seaford Nominees Pty Ltd Heat exchanger
US4957721A (en) * 1988-06-28 1990-09-18 Lonsinger Jack J Process for regeneration of activated carbon
US5073454A (en) * 1989-09-05 1991-12-17 Westates Carbon Oxidation resistant activated carbon and method of preparation
JP2016022399A (en) * 2014-07-16 2016-02-08 フタムラ化学株式会社 Water purification filter body
JP6418584B1 (en) * 2017-10-25 2018-11-07 エネサイクル株式会社 Activation furnace and activated carbon production equipment

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Publication number Priority date Publication date Assignee Title
JPS5138275A (en) * 1974-09-30 1976-03-30 Hitachi Ltd FUNMATSUKATSUSEITANNOSAISEIHOHO OYOBI SOCHI

Also Published As

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