JPH0139967B2 - - Google Patents

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Publication number
JPH0139967B2
JPH0139967B2 JP57195101A JP19510182A JPH0139967B2 JP H0139967 B2 JPH0139967 B2 JP H0139967B2 JP 57195101 A JP57195101 A JP 57195101A JP 19510182 A JP19510182 A JP 19510182A JP H0139967 B2 JPH0139967 B2 JP H0139967B2
Authority
JP
Japan
Prior art keywords
regeneration
activated carbon
dryer
waste activated
furnace
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
JP57195101A
Other languages
Japanese (ja)
Other versions
JPS5983921A (en
Inventor
Yukio Kawabata
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.)
Kuraray Chemical Co Ltd
Original Assignee
Kuraray Chemical 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 Kuraray Chemical Co Ltd filed Critical Kuraray Chemical Co Ltd
Priority to JP57195101A priority Critical patent/JPS5983921A/en
Publication of JPS5983921A publication Critical patent/JPS5983921A/en
Publication of JPH0139967B2 publication Critical patent/JPH0139967B2/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
    • Y02P20/129Energy recovery, e.g. by cogeneration, H2recovery or pressure recovery turbines

Description

【発明の詳細な説明】 本発明は水処理等に使用された含水率が高い廃
活性炭を再使用するための再生方法及びその装置
に関するものである。しかして、特に含水率が高
い廃活性炭を連続流動法により効率よく再賦活す
ると共に脱臭炉で発生した熱を乾燥機に再利用す
るようにして特に省エネルギー効果を高めた点に
特徴を有するものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a regeneration method and apparatus for reusing waste activated carbon with a high moisture content used for water treatment and the like. Therefore, it is characterized in that waste activated carbon, which has a particularly high moisture content, is efficiently reactivated using a continuous flow method, and the heat generated in the deodorizing furnace is reused in the dryer, which particularly enhances the energy saving effect. be.

現在活性炭は水処理等において吸着剤として広
く使用されているが、一定の吸着量に達した場合
廃活性炭を取出して再生し、循環使用することが
望ましい。廃活性炭の再生方式として、流動層に
よる方法も従来から多く提示されているが、何れ
も流動層高が高く、また縦型多段方式あるいは横
型多段方式いづれも溢流管もしくは隔壁で仕切ら
れた各槽は完全混合するような機構となつてい
る。従つて、滞留時間を相当長くする必要がある
が、これは多分に活性炭製造用賦活炉の設計思想
の影響をうけたためと考えられ、再生時活性炭の
滞留量が多く、また流動層高が高いため、磨耗損
失が多くなる欠陥が目立つた。
Currently, activated carbon is widely used as an adsorbent in water treatment and the like, but when a certain amount of adsorption is reached, it is desirable to take out the waste activated carbon, regenerate it, and recycle it. As a method for regenerating waste activated carbon, many methods using fluidized beds have been proposed in the past, but all of them have a high fluidized bed height, and both vertical and horizontal multi-stage systems have separate sections separated by overflow pipes or partition walls. The tank is designed to ensure complete mixing. Therefore, it is necessary to make the residence time considerably longer, but this is probably due to the influence of the design concept of the activation furnace for producing activated carbon.The amount of retained activated carbon during regeneration is large and the height of the fluidized bed is high. Therefore, defects that increase wear loss are noticeable.

かかる技術的課題を解決するための手段として
例えば2段式の連続流動式再生装置(特開昭53−
18494)が提示されている。これは縦型の反応炉
に上下2段の流動層を設け上段で予熱、乾燥、乾
留(焙焼)し、下段で再生する方式であるが、水
処理に使用された廃活性炭を含水率が高い状態で
直接流動層に仕込んだ場合、塊状となつて良好な
流動状態が得られず、従つて、乾燥、乾留が不充
分となり、次の再生室においても充分な効果が上
らない。
As a means to solve such technical problems, for example, a two-stage continuous flow regenerator (Japanese Patent Application Laid-open No.
18494) are presented. This is a method in which a vertical reactor has two fluidized beds, upper and lower, where the upper stage performs preheating, drying, and carbonization (roasting), and the lower stage regenerates the waste activated carbon used for water treatment. If it is directly charged into a fluidized bed at a high temperature, it will become lumpy and a good fluidization state will not be obtained, and therefore drying and carbonization will be insufficient, and sufficient effects will not be achieved in the next regeneration chamber.

本発明者等はかかる問題点を解決するために乾
燥、乾留工程と再生工程を分離すると共に、前者
にロータリイキルン方式或いは特殊な移動層方式
を採用することにより、含水率が非常に高く且つ
粘着し易い廃活性炭を使用しても充分な効果が得
られる機構及び容量を賦与し、ひいては後者の再
生用流動層の機能も一層高めうる方法を探求し
た。再生工程に使用された高温の廃ガスは乾燥・
乾留工程に使用されるが臭気が強くそのまま放出
できないため、燃料を加えて再燃焼し脱臭して放
出している。しかし再燃焼ガスを乾燥・乾留工程
の間接加熱に循環再使用することにより廃活性炭
の含水率が高い場合再燃焼ガスの熱量が大きいこ
とも相まつて著しい省エネルギー効果が得られる
ことを見出して本発明に到達した。
In order to solve this problem, the present inventors separated the drying and carbonization steps from the regeneration step, and adopted a rotary kiln method or a special moving bed method for the former, thereby producing a product with a very high moisture content. We sought a method that would provide a mechanism and capacity that would provide sufficient effects even when using waste activated carbon, which tends to stick, and that would further enhance the functionality of the latter fluidized bed for regeneration. The high temperature waste gas used in the regeneration process is dried and
It is used in the carbonization process, but it has a strong odor and cannot be released as it is, so it is re-burned with fuel and deodorized before being released. However, by circulating and reusing the afterburned gas for indirect heating in the drying/carbonization process, we have discovered that when the moisture content of waste activated carbon is high, a significant energy saving effect can be obtained due to the large calorific value of the afterburned gas, and we have developed the present invention. reached.

すなわち、乾燥機、燃焼室及び再生室よりなる
再生炉、脱臭炉からなる廃活性炭再生工程におい
て、再生炉として縦型同心円筒状の2ケの隔壁及
び底部が多孔板整流器により区かくされた環状再
生室を有し、環状整流器は1ケ所直径方向の堰で
仕切られている。高温の再生用ガスは下部燃焼室
より、多孔板を通して再生室に吹込み活性炭流動
層を形成せしめる如くし、また再生炭取出口の高
さは調節可能とし、流動層高さ及び滞留時間を調
節しうるごとくしている。また再生炉の出ガスは
乾燥機に導びき廃活性炭と向流乾燥せしめた後脱
臭炉で燃焼せしめ、高温再燃焼ガスは乾燥機のジ
ヤケツトに導びき廃活性の乾燥に利用しうるよう
にしたことを特徴とする廃活性炭再生装置であ
る。
That is, in the waste activated carbon regeneration process, which consists of a regeneration furnace consisting of a dryer, a combustion chamber, and a regeneration chamber, and a deodorizing furnace, the regeneration furnace is an annular regeneration furnace with two vertical concentric cylindrical partition walls and a bottom section separated by a perforated plate rectifier. It has a regeneration chamber, and the annular rectifier is partitioned at one point by a diametrical weir. High-temperature regeneration gas is blown into the regeneration chamber from the lower combustion chamber through a perforated plate to form an activated carbon fluidized bed, and the height of the regenerated coal outlet can be adjusted to adjust the fluidized bed height and residence time. It's very quiet. In addition, the gas emitted from the regeneration furnace was led to a dryer, where it was dried in countercurrent to the waste activated carbon, and then combusted in a deodorizing furnace.The high-temperature re-combustion gas was led to the jacket of the dryer so that it could be used for drying the waste activated carbon. This is a waste activated carbon regeneration device characterized by the following.

次に例示した図面によつて、本発明を更に詳し
く説明する。第1図は本発明の1例を示したもの
で、燃焼炉、再生炉、乾燥機及び脱臭炉よりなる
構成を示したものである。1は内外熱併用ロータ
リイキルン型乾燥機で廃活性炭を2より仕込み、
再生炉より発生したガス3により乾燥された後4
より再生炉5に仕込まれる。尚A―A部分の断面
図を第2図に示す。再生炉は耐火物より出来た円
筒状の外殻5と中心部に低い円柱状部分6及び多
孔板整流器7よりなり、その環状の部分が再生室
となつており、整流器の上に活性炭の流動層8が
形成される。再生室には堰9があり、4より仕込
まれた廃活性炭は再生室を落下して10の部分に
落ち流動層8を形成しながら、整流器を通して吹
込まれた燃焼ガスにより再生され再生済活性炭取
出口11より取出される。
The present invention will now be explained in more detail with reference to the illustrated drawings. FIG. 1 shows one example of the present invention, and shows a configuration consisting of a combustion furnace, a regeneration furnace, a dryer, and a deodorizing furnace. 1 is a rotary kiln type dryer with internal and external heating, and waste activated carbon is charged from 2.
After being dried by gas 3 generated from the regeneration furnace 4
It is then fed into the regeneration furnace 5. A cross-sectional view of the AA section is shown in FIG. 2. The regeneration furnace consists of a cylindrical outer shell 5 made of refractory material, a low cylindrical part 6 in the center, and a perforated plate rectifier 7.The annular part serves as a regeneration chamber, and activated carbon flows over the rectifier. Layer 8 is formed. There is a weir 9 in the regeneration chamber, and the waste activated carbon charged from 4 falls through the regeneration chamber and falls into the area 10, forming a fluidized bed 8 while being regenerated by the combustion gas blown through the rectifier and collecting the regenerated activated carbon. It is taken out from the outlet 11.

燃焼室12はバーナー13、燃料吹込口14、
空気吹込口15及び水蒸気吹込口16よりなり、
燃焼ガス及び水蒸気よりなるガスは整流器7を通
つて再生室の活性炭層8に吹込まれる。
The combustion chamber 12 includes a burner 13, a fuel inlet 14,
Consisting of an air inlet 15 and a steam inlet 16,
The gas consisting of combustion gas and steam is blown into the activated carbon bed 8 of the regeneration chamber through the rectifier 7.

再生に使用された燃焼ガスは3を通つてロータ
リイキルン型の乾燥機の内部17に吹込まれ、キ
ルンの回転に伴つて撹拌されながら移動する水分
を含んだ廃活性炭と向流しながら乾燥される。乾
燥機出口18を出たガスは活性炭より脱着された
成分を含むため通常強い悪臭を有し、そのまま放
出できないため脱臭炉19に導き、バーナー20
より発生した燃焼ガスと混合して、高温状態とし
て脱臭する。21は燃料吹込口、22は空気吹込
口である。高温脱臭ガスは乾燥機のジヤケツト部
23を通り、廃熱を廃活性炭の乾燥に利用した後
更に熱交換機24でバーナー吹込用空気を予熱し
た後放出される。また系内に入る空気はブロワー
25を通り、熱交換器24で予熱された後再生炉
及び脱臭炉のバーナー13及び20に吹込まれ
る。
The combustion gas used for regeneration is blown into the interior 17 of a rotary kiln type dryer through 3, and is dried in countercurrent to the waste activated carbon containing moisture, which moves while being stirred as the kiln rotates. . The gas that exits the dryer outlet 18 usually has a strong odor because it contains components desorbed from the activated carbon, and cannot be released as it is, so it is led to the deodorizing furnace 19 and sent to the burner 20.
It mixes with the combustion gas generated by the gas and deodorizes it in a high temperature state. 21 is a fuel inlet, and 22 is an air inlet. The high-temperature deodorizing gas passes through the jacket part 23 of the dryer, uses the waste heat to dry the waste activated carbon, and then preheats the air for blowing into the burner in the heat exchanger 24 before being released. Further, the air entering the system passes through the blower 25, is preheated by the heat exchanger 24, and is then blown into the burners 13 and 20 of the regeneration furnace and the deodorizing furnace.

第3図は乾燥機に移動層型乾燥機を使用した場
合の構成を示したものであるが、乾燥機及び脱臭
炉以外は第1図の構成と同様である。乾燥機26
は底部がコニツクとなつた円筒状で、内部にカサ
型分散板27を有する。水分を含んだ廃活性炭は
28より入り、分散板上に落下し、再生に使用さ
れた燃焼ガスにより分散板に沿つて落下する間に
乾燥される。乾燥された廃活性炭は29より再生
炉5に仕込まれる。乾燥機出口30を出たガスは
活性炭より脱着された成分を含むため、通常強い
臭気を有し、そのまま放出できないため、脱臭炉
31に導き、バーナー32で発生した燃焼ガスと
混合して高温状態として脱臭する。33は燃料吹
込口、34は空気吹込口である。高温脱臭ガスは
乾燥機のジヤケツト35を通り、廃熱を廃活性炭
の乾燥に再利用した後更に熱交換機24でバーナ
ー吹込用空気を予熱した後放出される。
FIG. 3 shows the configuration when a moving bed dryer is used as the dryer, and the configuration is the same as that in FIG. 1 except for the dryer and the deodorizing furnace. Dryer 26
It has a cylindrical shape with a rounded bottom and has an umbrella-type dispersion plate 27 inside. The waste activated carbon containing moisture enters from 28, falls onto the distribution plate, and is dried by the combustion gas used for regeneration while falling along the distribution plate. The dried waste activated carbon is fed into the regeneration furnace 5 through 29. The gas exiting the dryer outlet 30 contains components desorbed from the activated carbon, so it usually has a strong odor and cannot be released as it is, so it is led to the deodorizing furnace 31 and mixed with the combustion gas generated by the burner 32, where it is heated to a high temperature state. Deodorizes as. 33 is a fuel inlet, and 34 is an air inlet. The high-temperature deodorizing gas passes through the jacket 35 of the dryer, reuses the waste heat for drying the waste activated carbon, and then preheats the air for blowing into the burner in the heat exchanger 24 before being released.

次に主要な単位操作について述べる。再生炉に
おいて乾燥された廃活性炭は、環状の再生室の堰
の近くに仕込まれ、整流器を通して吹込まれた燃
焼ガスにより流動層を形成しながら、移動し、堰
の反対側に達し、取出される。これは多年の経験
より(1)粒状炭の流動層においてはガス整流器上の
層高数10ミリメートルで速かに伝熱および物質移
動が行われる。(2)流動層高が低いときは流動層の
平均粒子移動速度が小さい場合でも粒子の逆混合
は殆んど起らない。従つて隔壁がない流動層で処
理しても、略完全なピストン・フローに近い状態
となる。(3)ピストン・フローの流動層で再生する
のが最も均質且つ高能率である。本再生炉はこれ
らの知見に基づいて設計されたものである。
Next, we will discuss the main unit operations. The waste activated carbon dried in the regeneration furnace is placed near the weir in the annular regeneration chamber, moves while forming a fluidized bed with the combustion gas blown through the rectifier, reaches the opposite side of the weir, and is taken out. . This is based on many years of experience: (1) In a fluidized bed of granular coal, heat and mass transfer occur rapidly at a bed height of 10 mm above the gas rectifier. (2) When the height of the fluidized bed is low, back mixing of particles hardly occurs even if the average particle movement speed of the fluidized bed is small. Therefore, even if the treatment is performed using a fluidized bed without partition walls, a state close to a complete piston flow will be achieved. (3) Regeneration using a piston flow fluidized bed is the most homogeneous and highly efficient. This regeneration reactor was designed based on these findings.

再生炭排出口は高低の調節が可能で、これによ
つて流動層高の調節が可能となり、滞留時間及び
性能回復率を制御しうる。
The reclaimed coal outlet can be adjusted in height, which allows the fluidized bed height to be adjusted and the residence time and performance recovery rate to be controlled.

廃活性炭は使用された態様により様々の状態と
なるが、最も大量に使用され且つ再生が必要とさ
れる水処理用のものは通常再生が容易で再生時間
も比較的短かくてよい。スチーム、炭酸ガスを含
む高温ガスを吹込んで流動層を形成せしめた場合
層高数10ミリメートルで有効な再生が行わわれ、
それより上の部分は再生速度が低下する。またそ
の程度の層高であれば、流動状態もマイルドで、
粒子の磨耗も少く、また略完全なピストン・フロ
ーに近い状態となるため、再生収率及び均質性も
高い。従つて、本発明の再生炉は流動層の層高を
低くして再生することにより、水処理に使用され
た活性炭の再生に極めてすぐれた効果が得られる
ものである。
Waste activated carbon is in various states depending on the manner in which it is used, but those for water treatment, which are used in the largest quantities and require regeneration, are usually easy to regenerate and require a relatively short regeneration time. When a fluidized bed is formed by blowing high-temperature gas containing steam or carbon dioxide, effective regeneration can be achieved with a bed height of several 10 mm.
The playback speed of the portion above this level decreases. Also, if the bed height is that high, the flow state will be mild,
Particle wear is low, and the state is close to perfect piston flow, resulting in high regeneration yield and high homogeneity. Therefore, in the regeneration furnace of the present invention, extremely excellent effects can be obtained in the regeneration of activated carbon used in water treatment by lowering the bed height of the fluidized bed for regeneration.

廃活性炭を再生炉に仕込むためにはあらかじ
め、乾燥処理が必要である。しかし、水処理に使
用された廃活性炭の含水率は通常極めて高く且つ
若干粘着性を有する場合も少くない。活性炭を効
率よく乾燥させるため屡々流動層方式が使用され
るが、かかる性状の活性炭は塊状となり易く均一
な乾燥が固難である。かかる観点から本願では第
1図においてはロータリイキルン型乾燥機を使用
した。これは含水率が極めて高い廃活性炭を使用
してもキルンの自転による撹拌で塊状となること
が妨げられ、乾燥用ガスと活性炭の接触が良好で
均一な乾燥ができジヤケツト部からの高温脱臭ガ
スによる加熱と相まつて、一層乾燥が促進され
る。特に含水率が高いゾーンでは間接加熱も相当
大きな効果が得られる。
In order to feed waste activated carbon into a regeneration furnace, it must be dried beforehand. However, waste activated carbon used for water treatment usually has an extremely high moisture content and is often slightly sticky. A fluidized bed method is often used to efficiently dry activated carbon, but activated carbon with such properties tends to form lumps and is difficult to dry uniformly. From this point of view, in the present application, a rotary kiln type dryer is used in FIG. 1. This means that even when waste activated carbon with an extremely high moisture content is used, it is prevented from forming into lumps due to agitation caused by the rotation of the kiln, and good contact between the drying gas and the activated carbon allows for uniform drying. Combined with the heating, drying is further promoted. Particularly in zones with high moisture content, indirect heating can also have a considerable effect.

第3図は移動層方式による乾燥機であるが、カ
サ型の分散板付近の移動層の直接加熱に加え、更
にジヤケツト部からの高温脱臭ガスによる間接加
熱によつて乾燥が一層促進される。しかし、この
型の乾燥機ではカサ型分散板付近の直接加熱によ
る乾燥効果が最も大きいので、ロータリイキルン
型にくらべて廃活性炭の含水率が若干低い場合に
適している。
FIG. 3 shows a dryer using a moving bed method, and in addition to direct heating of the moving bed near the umbrella-type dispersion plate, drying is further promoted by indirect heating by high-temperature deodorizing gas from the jacket. However, this type of dryer has the greatest drying effect due to direct heating near the umbrella-type dispersion plate, so it is suitable when the moisture content of the waste activated carbon is slightly lower than that of the rotary kiln type.

更に本願構成において高い省エネルギー効果を
有することは最も重要な構成要件の1つである。
すなわち燃焼室で発生した約1000℃の再生に使用
されるガスは再生炉出口において約700℃程度の
温度を保持しており乾燥機に導かれる。廃活性炭
の向流乾燥に使用された乾燥機出口ガスの温度は
廃活性炭の含水率により左右されるが1例として
約400℃となつたガスは脱臭炉で再び750℃以上に
加熱された後、乾燥機ジヤケツトに導入されて乾
燥に再使用され、約500℃となり更に熱交換器で
バーナー吹込用空気の予熱に使用され420℃〜450
℃で放出される。廃活性炭の乾燥機より発生する
ガスは通常強い悪臭を有するため、再燃焼による
脱臭は不可避である。本願構成においては、該高
温脱臭ガスを乾燥及びバーナー吹込用空気の予熱
に利用すると共に、再生炉ガスも乾燥に使用する
ことにより約20%の燃料節約効果が得られた。
Furthermore, having a high energy saving effect is one of the most important structural requirements in the structure of the present invention.
That is, the gas used for regeneration at approximately 1000°C generated in the combustion chamber maintains a temperature of approximately 700°C at the outlet of the regeneration furnace and is led to the dryer. The temperature of the dryer outlet gas used for countercurrent drying of waste activated carbon depends on the moisture content of the waste activated carbon, but as an example, the gas that has reached about 400℃ is heated again to 750℃ or higher in a deodorizing furnace. It is introduced into the dryer jacket and reused for drying, reaching a temperature of approximately 500°C, and is further used in a heat exchanger to preheat the air for blowing into the burner, reaching a temperature of 420°C to 450°C.
Released at °C. Since the gas generated from waste activated carbon dryers usually has a strong odor, deodorization by re-combustion is inevitable. In the configuration of the present invention, a fuel saving effect of about 20% was obtained by using the high temperature deodorizing gas for drying and preheating the air for blowing into the burner, and also using the regeneration furnace gas for drying.

上記詳述したように廃活性炭の再生において、
摩耗が少なく、性能回復率が高く且つ均質な再生
炭が得られること及び、廃ガスの循環利用により
高い省エネルギー効果が併せて得られることが本
願発明の効果である。
As detailed above, in the regeneration of waste activated carbon,
The effects of the present invention are that a homogeneous recycled coal with little wear and a high performance recovery rate can be obtained, and that a high energy saving effect can be obtained by recycling waste gas.

以下実施例を挙げて本願発明を説明するが、こ
れらの実施例は本発明を何等限定するものではな
い。
The present invention will be described below with reference to Examples, but these Examples do not limit the present invention in any way.

実施例 食品工業で発生した排水処理に使用した廃活性
炭、再生炭の物性及び燃料使用量は次の如くであ
る。
Example The physical properties and amount of fuel used for waste activated carbon and recycled carbon used in the treatment of wastewater generated in the food industry are as follows.

●廃活性炭処理量 55Kg/hr(乾量換算) 〃 含水率 96.9%(乾量基準) 〃 吸着能力(ヨード)
555mg/g 〃 〃 (メチレンブルー)
80c.c./g ●乾燥機出口水分 33.3%(乾量基準) ●再生炭生成量 45.7Kg/hr 〃 吸着能力(ヨード)
1034mg/g 〃 〃 (メチレンブルー)
180c.c./g ●灯油使用量 0.44/Kg再生炭 比較例 前記実施例で使用した廃活性炭を直接再生炉に
仕込み、また脱臭炉ガスは熱交換機を通さず、直
接放出した。
●Waste activated carbon processing amount 55Kg/hr (dry weight conversion) 〃 Moisture content 96.9% (dry weight basis) 〃 Adsorption capacity (iodine)
555mg/g 〃 〃 (methylene blue)
80c.c./g ●Dryer outlet moisture 33.3% (dry basis) ●Regenerated coal production amount 45.7Kg/hr 〃 Adsorption capacity (iodine)
1034mg/g 〃 〃 (methylene blue)
180 c.c./g ●Amount of kerosene used: 0.44/Kg Regenerated coal Comparative example The waste activated carbon used in the above example was directly charged into a regeneration furnace, and the deodorizing furnace gas was directly discharged without passing through a heat exchanger.

●廃活性炭処理量 55Kg/hr(乾量換算) ●再生炭生成量 46.0Kg/hr 〃 吸着能力(ヨード)
1025mg/g 〃 〃 (メチレンブルー)
180c.c./g ●灯油使用量 0.55/Kg再生炭 実施例は比較例とくらべて約20%の省エネルギ
ー効果が得られる他、吸着能力も若干向上してい
る。
●Amount of waste activated carbon processed 55Kg/hr (dry weight conversion) ●Amount of recycled carbon produced 46.0Kg/hr 〃 Adsorption capacity (iodine)
1025mg/g 〃 〃 (methylene blue)
180c.c./g ●Amount of kerosene used: 0.55/Kg Regenerated coal In the example, an energy saving effect of about 20% is obtained compared to the comparative example, and the adsorption capacity is also slightly improved.

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

第1図は本発明において、乾燥機としてロータ
リイキルン型乾燥機を使用した場合の構成を縦断
面図にて示したものであり、第2図は第1図の再
生炉のA―A部の断面図を示す。第3図は乾燥機
としてカサ型分散板を有する移動層型乾燥機を使
用した場合の構成を縦断面図で示したものであ
る。
FIG. 1 is a longitudinal cross-sectional view showing the configuration of a rotary kiln type dryer used as the dryer in the present invention, and FIG. 2 is a section A-A of the regeneration furnace shown in FIG. A cross-sectional view is shown. FIG. 3 is a vertical sectional view showing the structure of a moving bed dryer having an umbrella-type dispersion plate as the dryer.

Claims (1)

【特許請求の範囲】 1 乾燥機、燃焼室及び再生室よりなる再生炉、
脱臭炉からなる廃活性炭再生工程において。 再生炉として縦型同心円筒状の2ケの隔壁及び
底部が多孔板整流器により区かくされた環状再生
室を有し、環状の整流器は1ケ所直径方向の堰で
仕切られ、高温の再生用ガスは下部燃焼室より多
孔板整流器を通して再生室に吹込み活性炭流動層
を形成せしめる如くし、また再生炭取出口の高さ
は調節可能として、流動層高さ及び滞留時間を調
節しうるごとくし、再生炉を出たガスは乾燥機に
導びき廃活性炭と向流乾燥せしめた後脱臭炉で燃
焼せしめ、高温再燃焼ガスは乾燥機のジヤケツト
に導びき廃活性炭の乾燥に利用しうるごとく構成
してなる廃活性炭再生装置。 2 乾燥機が内外熱併用ロータリイキルン型乾燥
機からなる特許請求の範囲第1項記載の廃活性炭
再生装置。 3 乾燥機が縦型で内部にカサ型の分散板を有
し、且つ外部にジヤケツトを有する移動層型乾燥
機よりなる特許請求の範囲第1項記載の廃活性炭
再生装置。
[Claims] 1. A regeneration furnace comprising a dryer, a combustion chamber, and a regeneration chamber;
In the waste activated carbon regeneration process consisting of a deodorizing furnace. The regeneration furnace has an annular regeneration chamber separated by two vertical concentric cylindrical partition walls and a perforated plate rectifier at the bottom. is injected into the regeneration chamber from the lower combustion chamber through a perforated plate straightener to form an activated carbon fluidized bed, and the height of the regenerated coal outlet is adjustable so that the height and residence time of the fluidized bed can be adjusted. The gas exiting the regeneration furnace is led to a dryer, where it is dried in countercurrent to the waste activated carbon, and then combusted in a deodorizing furnace.The high-temperature re-burned gas is led to the jacket of the dryer and is configured so that it can be used for drying the waste activated carbon. Waste activated carbon regeneration equipment. 2. The waste activated carbon regeneration apparatus according to claim 1, wherein the dryer is a rotary kiln type dryer using both internal and external heating. 3. The waste activated carbon regeneration apparatus according to claim 1, wherein the dryer is a vertical moving bed type dryer having an umbrella-shaped dispersion plate inside and a jacket outside.
JP57195101A 1982-11-05 1982-11-05 Apparatus for regeneration of waste activated carbon Granted JPS5983921A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP57195101A JPS5983921A (en) 1982-11-05 1982-11-05 Apparatus for regeneration of waste activated carbon

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP57195101A JPS5983921A (en) 1982-11-05 1982-11-05 Apparatus for regeneration of waste activated carbon

Publications (2)

Publication Number Publication Date
JPS5983921A JPS5983921A (en) 1984-05-15
JPH0139967B2 true JPH0139967B2 (en) 1989-08-24

Family

ID=16335532

Family Applications (1)

Application Number Title Priority Date Filing Date
JP57195101A Granted JPS5983921A (en) 1982-11-05 1982-11-05 Apparatus for regeneration of waste activated carbon

Country Status (1)

Country Link
JP (1) JPS5983921A (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002308613A (en) * 2001-04-10 2002-10-23 健郎 ▲とう▼ Method for producing activated carbon
JP6864930B1 (en) * 2020-02-17 2021-04-28 株式会社シバタ Porous material regeneration device
CN116812929B (en) * 2023-06-25 2023-11-28 中科合肥煤气化技术有限公司 System and method for preparing activated carbon by biomass fluidized bed carbonization coupling segmented activation

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5324188A (en) * 1976-08-17 1978-03-06 Ntn Toyo Bearing Co Ltd Device for controlling work engaged at predetermined suitable interval and for forming work
JPS56169107A (en) * 1980-06-02 1981-12-25 Ishikawajima Harima Heavy Ind Co Ltd Sulfur recovering apparatus

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5324188A (en) * 1976-08-17 1978-03-06 Ntn Toyo Bearing Co Ltd Device for controlling work engaged at predetermined suitable interval and for forming work
JPS56169107A (en) * 1980-06-02 1981-12-25 Ishikawajima Harima Heavy Ind Co Ltd Sulfur recovering apparatus

Also Published As

Publication number Publication date
JPS5983921A (en) 1984-05-15

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