JP3693687B2 - Vacuum concentration drying tank for distilled liquor waste liquor and vacuum concentration drying method - Google Patents

Vacuum concentration drying tank for distilled liquor waste liquor and vacuum concentration drying method Download PDF

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JP3693687B2
JP3693687B2 JP35010093A JP35010093A JP3693687B2 JP 3693687 B2 JP3693687 B2 JP 3693687B2 JP 35010093 A JP35010093 A JP 35010093A JP 35010093 A JP35010093 A JP 35010093A JP 3693687 B2 JP3693687 B2 JP 3693687B2
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tank
drying
waste liquid
concentration
vacuum
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JPH07184629A (en
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俊郎 飯田
隆史 花本
博 武田
馨 二村
雅美 栗山
潤 高橋
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Ulvac Inc
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Ulvac Inc
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  • Distillation Of Fermentation Liquor, Processing Of Alcohols, Vinegar And Beer (AREA)
  • Heat Treatment Of Water, Waste Water Or Sewage (AREA)

Description

【0001】
【産業上の利用分野】
本発明は焼酎、その他蒸溜酒の製造プロセスにおいて蒸溜釜残として発生する蒸溜酒廃液の真空濃縮乾燥槽および真空濃縮乾燥方法に関するものである。
【0002】
【従来の技術及びその問題点】
例えば焼酎の製造工程においては、蒸溜後に釜残として残る廃液は5〜7%の有機固形分を含んでおり、有機汚泥として分類されるものなので、そのまま一般河川へ放流することはできない。従って、これ迄は海洋投棄することが行なわれていたが、その海洋投棄も世界的に禁止される方向にある。
【0003】
一部では、焼酎廃液を濃縮して有機固形分濃度を高めたものを飼料又は肥料として再利用することが行なわれているが、この濃縮にはバッチ式の蒸発釜が採用されており、有機固形分が蒸発釜の内壁や撹拌翼、加熱管等に付着し、焦げ付いたりして、蒸発能力を低下させるほか、濃縮液も変色や焦げ付き臭を有するものとなり易かった。因みに、廃液中の有機固形分は醗酵残渣、高粘性物、多糖類などからなっている。
【0004】
これに対し、缶内に多数の加熱管を設けた真空濃縮方式として、加熱管内を流れる廃液の流速を大にする試み(特公平1−56836号公報)、加熱管間の流速の均等化をはかる試み(実公平1−41444号公報)などが行なわれている。
【0005】
しかし、これらの手段は濃縮であって有機固形分濃度を18〜20%までしか高めることができず、水分に着目すれば、[0002]で述べた有機固形分濃度5〜7%の廃液、すなわち、残余の水分93%〜95%の廃液を水分80〜82%程度に濃縮するものであり、腐敗に問題があるほか保管や輸送にコストを要して、その利用に限界があり、廃液処理の根本的な解決手段とはなっていない。なお、廃液を上記濃度までしか濃縮できないのは、有機固形分濃度を20%以上に高めると、液体としての流動性を失うようになるからである。
【0006】
他方、濃縮液を濃縮装置から取り出して、別な乾燥機で乾燥するという試みもある。例えば、回転ドラムの表面で濃縮液を乾燥させる、多段円板乾燥機の円板上で乾燥するなどであるが、何れも大気圧下での乾燥であるため、水分の乾燥加熱源として100℃以上の加熱水蒸気を使用することから、乾燥品に着色や焦げ付き臭を伴う。又、回転混合乾燥機、その他類似の機器によって真空乾燥する試みにおいても、含有水分40〜50%の乾燥中途品となった辺りで、回転混合作用によって持ち上げられた乾燥中途品が下に存在する乾燥中途品上に落下した時の衝撃で塊状化が助長され、表面は乾燥しているが、内部は水分が多いといった状況を呈するほか、乾燥品が乾燥機内に付着して容易に取り出せないのである。又、例え乾燥品を得ても粉砕を必要とする上、含有水分を20%以下とするに至らず、乾燥品の保管中に黴や腐敗を生じ易いという問題もある。
【0007】
【発明が解決しようとする問題点】
本発明は上述の問題に鑑みてなされ、蒸溜廃液の濃縮と乾燥とを同一の槽で行ない得て、かつ顆粒状ないしは小フレーク状に乾燥し得る真空濃縮乾燥槽、及びその真空濃縮乾燥方法を提供することを目的とする。
【0008】
【問題点を解決するための手段】
以上の目的は、少なくとも槽の直胴部内面及び底面からなる槽内面を加熱する外部加熱手段と、該外部加熱手段に対応する前記槽内面を摺動するように設けられた複数枚の羽根と、真空排気口とを具備する蒸留酒廃液の真空濃縮乾燥槽において、前記羽根がばね材によって弾性的に保持されており、前記羽根が前記蒸留酒廃液の濃縮によって生ずる前記槽内面への塊状の付着物を掻き取り、かつ前記底面へ落下した前記塊状の付着物を含む濃縮物を前記羽根と前記底面との間で擂り潰しつつ濃縮度を高め、最終的に顆粒状またはフレーク状の乾燥された有機固形分を与えることを特徴とする蒸留酒廃液の真空濃縮乾燥槽、によって達成される。
【0009】
又、以上の目的は、少なくとも槽の直胴部内面及び底面からなる槽内面を外部加熱し、前記外部加熱に対応する前記槽内面を複数枚の羽根で摺動させ、真空排気する蒸溜酒廃液の真空濃縮乾燥方法において、蒸留酒廃液の濃縮と共に生ずる前記槽内面への塊状の付着物をばね材で弾性的に保持した前記羽根によって掻き取り、かつ前記底面へ落下した前記塊状の付着物を含む濃縮物を前記羽根と前記底面との間で擂り潰しつつ濃縮度を高める濃縮工程と、含有水分が約30%以下となった状態で加熱温度および前記羽根の摺動回数を前記濃縮工程より低下させ、顆粒状またはフレーク状の有機固形分となるまで乾燥する乾燥工程とからなることを特徴とする蒸留酒廃液の真空濃縮乾燥方法、によって達成される。
【0010】
【作用】
槽の直胴部内面への付着物を対応する羽根が掻き取り、底面へ落下した付着物を対応する羽根がこすり付けて潰すように働くので、蒸溜酒廃液の濃縮乾燥を連続して同一の槽内で行なうことができ、かつ真空下で水分を蒸発させる濃縮、乾燥であるため低温の操作となり、廃液中の有機固形分を着色、焦げ付き臭のない顆粒状ないしは小フレーク状まで乾燥し得る。
【0011】
又、濃縮工程から乾燥工程へ移る過程において、攪拌の回転数を小とし、加熱温度を低くすることによって、濃縮効率の向上と所要動力の低減が達成され、被乾燥物の熱劣化が防止される。
【0012】
【実施例】
以下、本発明の実施例による焼酎廃液の真空濃縮乾燥槽及びその真空濃縮乾燥方法について、図面を参照して説明する。
【0013】
図1に示すように、真空濃縮乾燥槽100はフラットな底板3を備えた槽本体1と温水管49付きの分離塔40を備えた蓋体2とによって構成され、蓋体2に取り付けた正逆回転可能の減速機構を有する駆動モータ5によって撹拌シャフト6が回転される。そして撹拌シャフト6の下端は図示しない部材によって固定された軸受7に支持されている。
【0014】
廃液は槽本体1の直胴部に設けた廃液ノズル11によって仕込まれる。乾燥品の取出口14は底板3の中央部に設けられており、温水導入口13a、温水排出口13bを有する着脱可能なプラグ部材13によって気密に閉じられている。又更には、蓋体2には上記駆動モータ5以外にマンホール15と分離塔40が取り付けられている。分離塔40の内部にはミストに伴われる有機固形分を衝突させて捕捉分離させるための邪魔板48が配置されており、外側には保温のための温水管49が巻装されている。そして、分離塔40の上部には真空排気管42が設けられている。
【0015】
又、槽本体1の直胴部の外面には加熱用の温水ジャケット21、22が、底板3の外面には同じく温水ジャケット23が取り付けられており、それぞれに温水導入口21a、22a、23a、温水排出口21b、22b、23bが設けられている。
【0016】
温水ジャケット21、22に対応する槽本体1の直胴部内面には、これを摺動するフッ素樹脂(商品名テフロン)の厚板からなる羽根81、82が撹拌シャフト6に固定されたアーム61、62の先端部のばね材71、72によって保持されている。なお、図1における[2]−[2]線方向の断面を示す図2に見られるように、アーム61は61a、61b、61cの3本のアームからなり、それぞれの先端に固定したばね材71a、71b、71cによって羽根81a、81b、81cが保持されている。そして羽根81a、81b、81cの直径方向の長さを短くしているが、このことは後述する羽根82、83についても同様である。なお、図1はアーム61b、61cを省略して描かれている。又、以下の説明においても、それらを区別する必要のある場合を除き、アーム61、ばね材71、羽根81として示す。
【0017】
更には、図1における[3]−[3]線方向の断面を示す図3に見られるように、アーム62も3本あって、それぞれにばね材72、羽根82が設けられていることはアーム61の場合と同様である。更にはアーム62には、図1も参照して、槽本体1の底面を摺動する羽根83が取り付けられている。そして図3に示すように羽根83は、アーム62aに83a1 、83a2 の2枚が取り付けられており、このことはアーム62b、62cについても同様である。そして、アーム62aに固定されている2枚の羽根83a1 、83a2 と撹拌シャフト6との間の距離は、アーム62b、アーム62cにおいては、それぞれ異なった距離として固定されており、これら6枚の羽根83が分担して底面4上を余す所なく摺動するようになっている。
【0018】
なお、図4は図3における[4]−[4]線方向の側面を示し、羽根83a1 の取り付けの詳細を示す。すなわち、アーム62aに支持部材63a1 を介して固定されたブラケット64a1 にばね材73a1 を取り付け、このばね材73a1 にフッ素樹脂の厚板からなる羽根83a1 が保持されている。この取り付け構造は他の5枚の羽根83についても同様である。
【0019】
更には図1には示されていないが、温水導入口22aと同じ高さレベルの槽本体1の直胴側壁に、図5に示すように4本の窒素ガス導入ノズル31a、31b、31c、31dが取り付けられており、窒素ガスは廃液の撹拌を介助するべく吹き込まれる。
【0020】
本発明の実施例による真空濃縮乾燥槽100は以上のように構成されるが、次にこの作用について説明する。
【0021】
焼酎を蒸溜した釜残としての廃液が図示しない真空ポンプで排気された真空濃縮乾燥槽100へ廃液ノズル11から仕込まれる。所定量の廃液が仕込まれた後、廃液ラインは閉とされる。次いで駆動モータ5によって撹拌シャフト6を20〜35rpmの回転速度で回転させると、撹拌シャフト6に固定されているアーム61、62の先端の羽根81、82による槽本体1の直胴部内面の摺動、アーム62の中央部近辺に下向きに固定されている羽根83による底面4の摺動が開始される。同時に、図示しないバルブを開いて、真空排気管42とこれも図示しない真空排気系とを接続し、かつ各温水ジャケット21、22、23及びプラグ部材13にそれぞれの温水導入口21a、22a、23a、13aから75〜80℃の温水を導入して廃液の加熱を開始する。この温度で加熱しても13×103 Paから50Paに至る真空排気で水分が蒸発し、蒸発潜熱が奪われることもあって、廃液の温度は濃縮される間も50℃を越えることはない。
【0022】
この真空下での加熱によって有機固形分5〜7%の廃液は水分を蒸発され、有機固形分濃度が18〜20%になる迄の間、廃液は流動性を持って濃縮される。この間、温水ジャケット21、22、23による加熱面に有機固形分の付着傾向は見られるものの、それぞれの温水ジャケットに対応して設けられている羽根81、82、83が加熱面を比較的早い速度で摺動しているので、常に新しい加熱面が得られ、伝熱効率の低下が防がれる。又、上記の機械的撹拌に加えて、濃縮中に粘度の上昇した廃液の撹拌と塊状化抑制のために窒素ガスを導入ノズル31から間欠的に吹き込む。なお、濃縮過程中に、水分蒸発量相当の廃液を追加仕込みしながら排気処理を行うこともできる。
【0023】
更に濃縮が進んで固形分濃度が約30%を越えるようになると廃液は流動性を全く失い、加熱面への付着、塊状化が顕著に現われ始める。これらの傾向に対しフッ素樹脂の厚板からなる羽根81、82、83が付着物を掻き取るように働き、かつ底面4上に落下した状の付着物を含めて底面4上の濃縮物に対しては、底面4を摺動する羽根83が、これを保持しているばね材73によって、やや傾斜した状態で底面4との間に濃縮物を挟み込み、こすり付けるように働いて濃縮物を擂り潰す。又、羽根83は6枚が分担して底面4の全体を隈なく摺動するように配置されているので、塊状の付着物を含む濃縮物が潰されずに残留し成長することが防がれている。
【0024】
濃縮が更に進んで含有水分が30%以下になると小さい塊は撹拌によって崩れるようになり乾燥が始まる。この乾燥工程においては撹拌シャフト6の回転速度を約1/2に低下させて、撹拌による塊状化を防ぐと同時に動力負荷を減少させる。又温水温度も約60℃として乾燥品の熱劣化を可及的に防ぐ。
【0025】
このような濃縮、乾燥によって塊状化が防がれ、廃液中の有機固形物は顆粒状又はフレーク状となるので、内部まで均一な含有水分10%以下の乾燥が可能であり、乾燥時間も従来と比較して約1/2に短縮出来る。
【0026】
乾燥終了後、プラグ部材13を取り外して取出口14から乾燥品を外部へ取り出すが、槽本体1の直胴部内面や底面4への乾燥末期における付着物も羽根81、82、83で掻き取られており、取り出しは容易である。
【0027】
本実施例による焼酎廃液の真空濃縮乾燥槽100は以上のように構成され、作用するが、本発明はこれに限定されることなく、本発明の技術的思想に基いて種々の変形が可能である。
【0028】
例えば実施例においては槽本体1の直胴部内面、底面4を摺動する羽根81、82、83にフッ素樹脂の厚板を使用したが、他の樹脂厚板、又は樹脂ブロックとしてもよい。又、金属ワイヤブラシを用いても同様な効果が得られた。
【0029】
又、実施例においては、乾燥品の取出口14を底板3の中央部に設けたが、槽本体1の直胴部の底板3に近い位置に設けてもよい。
【0030】
又実施例では、真空濃縮乾燥槽を縦型としたが、実施例においての詳説したように付着物を掻き取り、こすり付けて擂り潰す作用を有する羽根を備えるものであれば横型としてもよい。
【0031】
【発明の効果】
以上述べたように本発明の真空濃縮乾燥槽および真空濃縮乾燥方法によれば、蒸溜酒廃液の濃縮と乾燥とを同一の槽で行なうことができ、かつ廃液に含まれる有機固形分を着色、焦げ付き臭なく、顆粒状又は小フレーク状に乾燥できるので、これ迄は環境汚染物であった蒸溜酒の廃液を飼料又は肥料として商業ベースで再利用することが可能である。
【図面の簡単な説明】
【図1】 本発明の実施例による真空濃縮乾燥槽の破断側面図である。
【図2】 図1における[2]−[2]線方向の断面図である。
【図3】 図1における[3]−[3]線方向の断面図である。
【図4】 図3における[4]−[4]線方向の側面図である。
【図5】 実施例の真空濃縮乾燥槽に設けられた窒素ガス導入ノズルの配置図である。
【符号の説明】
1 槽本体
2 蓋体
3 底板
4 底面
6 撹拌シャフト
21 温水ジャケット
22 温水ジャケット
23 温水ジャケット
40 分離塔
42 真空排気管
61 アーム
62 アーム
81 羽根
82 羽根
83 羽根
100 真空濃縮乾燥装置
[0001]
[Industrial application fields]
TECHNICAL FIELD The present invention relates to a vacuum concentrated drying tank and a vacuum concentrated drying method for distilled liquor waste liquor generated as a residue in a distilled spirit in the manufacturing process of shochu and other distilled spirits.
[0002]
[Prior art and its problems]
For example, in the manufacturing process of shochu, the waste liquid remaining as the residue after distillation contains 5-7% organic solids and is classified as organic sludge, so it cannot be discharged into a general river as it is. Therefore, ocean dumping has been performed until now, but the ocean dumping is also in the direction of being prohibited worldwide.
[0003]
In some cases, concentrated shochu waste liquor is used to increase the concentration of organic solids and reused as feed or fertilizer. The solid content adhered to the inner wall of the evaporation kettle, the stirring blade, the heating tube, etc., and burned to reduce the evaporation ability, and the concentrated liquid was liable to have a discoloration or burnt odor. Incidentally, the organic solid content in the waste liquid consists of fermentation residues, highly viscous substances, polysaccharides and the like.
[0004]
On the other hand, as a vacuum concentration method in which a large number of heating tubes are provided in the can, an attempt to increase the flow rate of the waste liquid flowing in the heating tube (Japanese Patent Publication No. 1-56836), the equalization of the flow rate between the heating tubes is performed. An attempt has been made (actual publication No. 1-441444).
[0005]
However, these means are concentrated and can only increase the organic solid concentration to 18 to 20%. If attention is paid to moisture, the waste liquid having an organic solid concentration of 5 to 7% described in [0002], In other words, the remaining liquid with a water content of 93% to 95% is concentrated to a water content of about 80 to 82%, and there is a problem with spoilage. It is not a fundamental solution for processing. The reason why the waste liquid can be concentrated only to the above-mentioned concentration is that when the organic solid content concentration is increased to 20% or more, the fluidity as a liquid is lost.
[0006]
On the other hand, there is an attempt to take out the concentrate from the concentrator and dry it with another dryer. For example, the concentrated liquid is dried on the surface of a rotating drum, or is dried on a disk of a multi-stage disk dryer, but both are dried under atmospheric pressure. Since the above heated steam is used, the dried product is accompanied by coloring and a burning odor. Moreover, even in an attempt to vacuum dry with a rotary mixing dryer or other similar equipment, there is a dry intermediate product lifted by the rotary mixing action around the point where the moisture content is 40-50%. The agglomeration is promoted by the impact when dropped on the product in the middle of drying, and the surface is dry, but the inside has a lot of moisture, and the dried product adheres to the dryer and cannot be easily removed. is there. In addition, even if a dried product is obtained, pulverization is required and the moisture content does not reach 20% or less, and there is a problem that wrinkles and rot easily occur during storage of the dried product.
[0007]
[Problems to be solved by the invention]
The present invention has been made in view of the above-mentioned problems. A vacuum concentration drying tank capable of performing concentration and drying of distilled waste liquid in the same tank and drying in a granular or small flake form, and a vacuum concentration drying method thereof The purpose is to provide.
[0008]
[Means for solving problems]
The above object is to provide an external heating means for heating at least the inner surface of the tank and the inner surface of the tank, and a plurality of sheets provided to slide on the inner surface of the tank corresponding to the external heating means. In a vacuum concentration drying tank for distilled liquor waste liquid comprising a blade and a vacuum exhaust port, the blade is elastically held by a spring material, and the blade is generated by concentrating the distilled liquor waste liquid. The concentrated matter is scraped off and the concentrate containing the massive deposit that has fallen to the bottom surface is crushed between the blades and the bottom surface to increase the concentration, and finally the granular or small flakes Achieved by a vacuum concentrated drying tank of distilled liquor waste liquor, characterized by providing a dried organic solid in the form of a liquid.
[0009]
Further, the above purpose is a distillation in which at least the inner surface of the tank composed of the inner surface and the bottom surface of the tank is externally heated, the inner surface of the tank corresponding to the external heating is slid with a plurality of blades, and evacuated. In the vacuum concentration drying method of liquor waste liquor, lump deposits on the inner surface of the tank that are generated along with the concentration of distilled liquor waste liquor are scraped by the blades elastically held by a spring material and dropped to the bottom surface The concentration step for increasing the concentration while crushing the concentrate containing deposits between the blade and the bottom surface, and the heating temperature and the number of sliding times of the blade in a state where the moisture content is about 30% or less It is achieved by a vacuum concentration drying method for distilled liquor waste liquor, characterized by comprising a drying step that is lowered from the concentration step and dried to a granular or small flake organic solid content.
[0010]
[Action]
Corresponding blades scrape off the deposits on the inner surface of the body of the tank, and the corresponding blades scrape and crush the deposits falling to the bottom. It can be performed in a tank, and it is concentrated and dried to evaporate moisture under vacuum, so it can be operated at low temperature, and the organic solid content in the waste liquid can be colored and dried to granular or small flakes without a burning odor. .
[0011]
Also, in the process of moving from the concentration process to the drying process, by reducing the number of rotations of stirring and lowering the heating temperature, an increase in concentration efficiency and a reduction in required power can be achieved, and thermal deterioration of the material to be dried is prevented. The
[0012]
【Example】
Hereinafter, the vacuum concentration drying tank and the vacuum concentration drying method of the shochu waste liquid by the Example of this invention are demonstrated with reference to drawings.
[0013]
As shown in FIG. 1, the vacuum concentration drying tank 100 includes a tank body 1 having a flat bottom plate 3 and a lid body 2 having a separation tower 40 with a hot water pipe 49, and is attached to the lid body 2. The agitation shaft 6 is rotated by a drive motor 5 having a speed reducing mechanism capable of reverse rotation. The lower end of the stirring shaft 6 is supported by a bearing 7 fixed by a member (not shown).
[0014]
The waste liquid is charged by a waste liquid nozzle 11 provided in the straight body portion of the tank body 1. The dry product outlet 14 is provided at the center of the bottom plate 3 and is hermetically closed by a detachable plug member 13 having a hot water inlet 13a and a hot water outlet 13b. Furthermore, the lid 2 is provided with a manhole 15 and a separation tower 40 in addition to the drive motor 5. A baffle plate 48 for colliding and separating the organic solids accompanying the mist by colliding with the mist is disposed inside the separation tower 40, and a hot water pipe 49 for keeping heat is wound around the outside. A vacuum exhaust pipe 42 is provided in the upper part of the separation tower 40.
[0015]
Moreover, warm water jackets 21 and 22 for heating are attached to the outer surface of the straight body portion of the tank body 1, and warm water jackets 23 are also attached to the outer surface of the bottom plate 3, and hot water inlets 21 a, 22 a, 23 a, Hot water discharge ports 21b, 22b, and 23b are provided.
[0016]
On the inner surface of the straight body portion of the tank body 1 corresponding to the hot water jackets 21 and 22, blades 81 and 82 made of a thick plate of fluororesin (trade name Teflon) sliding on the tank 61 are fixed to the stirring shaft 6. , 62 are held by spring members 71, 72 at the tip portions. As shown in FIG. 2 showing a cross section in the [2]-[2] line direction in FIG. 1, the arm 61 is composed of three arms 61a, 61b, 61c, and is a spring material fixed to the respective tips. The blades 81a, 81b, 81c are held by 71a, 71b, 71c. The lengths of the blades 81a, 81b, 81c in the diameter direction are shortened, and this is the same for the blades 82, 83 described later. In FIG. 1, the arms 61b and 61c are omitted. Also, in the following description, the arm 61, the spring material 71, and the blade 81 are shown unless they need to be distinguished.
[0017]
Further, as shown in FIG. 3 showing a cross section in the [3]-[3] line direction in FIG. 1, there are also three arms 62, and spring members 72 and blades 82 are provided respectively. This is the same as the case of the arm 61. Furthermore, with reference to FIG. 1, a blade 83 that slides on the bottom surface 4 of the tank body 1 is attached to the arm 62. As shown in FIG. 3, two blades 83a1 and 83a2 are attached to the arm 62a as shown in FIG. 3, and this also applies to the arms 62b and 62c. The distance between the two blades 83a1 and 83a2 fixed to the arm 62a and the stirring shaft 6 is fixed as different distances in the arm 62b and the arm 62c, respectively. 83 is assigned and slides on the bottom surface 4 without leaving any space.
[0018]
FIG. 4 shows the side surface in the [4]-[4] line direction in FIG. 3, and shows details of attachment of the blade 83a1. That is, a spring material 73a1 is attached to a bracket 64a1 fixed to the arm 62a via a support member 63a1, and a blade 83a1 made of a fluororesin thick plate is held on the spring material 73a1. This mounting structure is the same for the other five blades 83.
[0019]
Although not further shown in Figure 1, the cylindrical body portion side wall of the tank body 1 at the same height level as the hot water inlet 22a, 4 pieces of nitrogen gas inlet nozzle 31a as shown in FIG. 5, 31b, 31c , 31d, and nitrogen gas is blown to assist in stirring the waste liquid.
[0020]
Although the vacuum concentration drying tank 100 by the Example of this invention is comprised as mentioned above, next, this effect | action is demonstrated.
[0021]
The waste liquid as the kettle residue obtained by distilling the shochu is charged from the waste liquid nozzle 11 into the vacuum concentration drying tank 100 evacuated by a vacuum pump (not shown). After a predetermined amount of waste liquid is charged, the waste liquid line is closed. Next, when the agitation shaft 6 is rotated at a rotational speed of 20 to 35 rpm by the drive motor 5, the inner surface of the tank body 1 is slid by the blades 81 and 82 at the tips of the arms 61 and 62 fixed to the agitation shaft 6. The sliding of the bottom surface 4 by the blade 83 fixed downward near the center of the arm 62 is started. At the same time, a valve (not shown) is opened to connect the vacuum exhaust pipe 42 and a vacuum exhaust system (not shown), and the hot water inlets 21a, 22a, 23a are connected to the hot water jackets 21, 22, 23 and the plug member 13, respectively. Then, warm water of 75 to 80 ° C. is introduced from 13a, and heating of the waste liquid is started. Even when heated at this temperature, the water is evaporated by evacuation from 13 × 10 3 Pa to 50 Pa, and the latent heat of vaporization may be lost, and the temperature of the waste liquid does not exceed 50 ° C. even during concentration.
[0022]
By the heating under vacuum, the waste liquid having an organic solid content of 5 to 7% is evaporated, and the waste liquid is concentrated with fluidity until the organic solid content becomes 18 to 20%. During this time, although there is a tendency for organic solids to adhere to the heated surfaces of the hot water jackets 21, 22, and 23, the blades 81, 82, and 83 provided for the respective hot water jackets move the heated surfaces at a relatively high speed. Therefore, a new heating surface can always be obtained, and a decrease in heat transfer efficiency can be prevented. In addition to the mechanical stirring described above, nitrogen gas is intermittently blown from the introduction nozzle 31 in order to stir the waste liquid whose viscosity has been increased during concentration and to suppress agglomeration. During the concentration process, exhaust treatment can be performed while additionally adding waste liquid corresponding to the amount of water evaporation.
[0023]
As the concentration further progresses and the solid concentration exceeds about 30%, the waste liquid loses fluidity at all, and adhesion to the heating surface and agglomeration begin to appear remarkably. Act as blades 81, 82 and 83 for these tendencies consisting of fluororesin plank scrape deposits, and including the bottom masses like deposits 4 was dropped onto the concentrate on the bottom surface 4 On the other hand, the blade 83 that slides on the bottom surface 4 is sandwiched between the bottom surface 4 in a slightly inclined state by the spring material 73 that holds the blade 83, and works to rub the concentrate. Crush. In addition, since the blades 83 are arranged so that the six blades share and slide over the entire bottom surface 4, it is possible to prevent the concentrate containing the massive deposits from remaining without being crushed and growing. ing.
[0024]
When the concentration further proceeds and the water content becomes 30% or less, the small lump is broken by stirring and drying begins. In this drying step, the rotational speed of the stirring shaft 6 is reduced to about ½ to prevent agglomeration due to stirring and simultaneously reduce the power load. Also, the hot water temperature is set to about 60 ° C. to prevent thermal degradation of the dried product as much as possible.
[0025]
The agglomeration is prevented by such concentration and drying, and the organic solids in the waste liquid are in the form of granules or small flakes. Therefore, it is possible to dry the moisture content uniformly 10% or less to the inside, and the drying time is also long. Compared to the conventional case, it can be shortened to about ½.
[0026]
After the drying is finished, the plug member 13 is removed and the dried product is taken out from the outlet 14. However, the blade 81, 82, 83 scrapes off the deposits on the inner surface of the tank body 1 and the bottom surface 4 at the end of drying. It is easy to take out.
[0027]
Concentrated in vacuo drying tank 100 of shochu effluent according to this embodiment is constructed as described above, acts, the present invention is not limited thereto, various modifications may be had based Dzu the technical idea of the present invention It is.
[0028]
For example, in the embodiment, the fluororesin thick plates are used for the blades 81, 82, and 83 that slide on the inner surface of the straight body portion and the bottom surface 4 of the tank body 1, but other resin thick plates or resin blocks may be used. The same effect was obtained even when a metal wire brush was used.
[0029]
In the embodiment, the dry product outlet 14 is provided at the center of the bottom plate 3, but it may be provided at a position close to the bottom plate 3 of the straight body portion of the tank body 1.
[0030]
In the embodiment, the vacuum concentration drying tank is a vertical type. However, as described in detail in the embodiment, it may be a horizontal type as long as it has blades that scrape off and rub the deposits.
[0031]
【The invention's effect】
As described above, according to the vacuum concentration drying tank and the vacuum concentration drying method of the present invention, the concentration and drying of the distilled liquor waste liquid can be performed in the same tank, and the organic solid content contained in the waste liquid is colored. Since it can be dried in the form of granules or small flakes without a burning odor, it is possible to reuse the waste liquor, which has been an environmental pollutant, on a commercial basis as feed or fertilizer.
[Brief description of the drawings]
FIG. 1 is a cutaway side view of a vacuum concentration drying tank according to an embodiment of the present invention.
2 is a cross-sectional view taken along line [2]-[2] in FIG.
3 is a cross-sectional view taken along line [3]-[3] in FIG.
4 is a side view taken along the line [4]-[4] in FIG. 3;
FIG. 5 is a layout diagram of nitrogen gas introduction nozzles provided in the vacuum concentration drying tank of the example.
[Explanation of symbols]
DESCRIPTION OF SYMBOLS 1 Tank main body 2 Cover body 3 Bottom plate 4 Bottom face 6 Stirring shaft 21 Hot water jacket 22 Hot water jacket 23 Hot water jacket 40 Separation tower 42 Vacuum exhaust pipe 61 Arm 62 Arm 81 Blade 82 Blade 83 Blade 100 Vacuum concentration drying apparatus

Claims (11)

少なくとも槽の直胴部内面及び底面からなる槽内面を加熱する外部加熱手段と、該外部加熱手段に対応する前記槽内面を摺動するように設けられた複数枚の羽根と、真空排気口とを具備する蒸留酒廃液の真空濃縮乾燥槽において、
前記羽根がばね材によって弾性的に保持されており、前記羽根が蒸留酒廃液の濃縮によって生ずる前記槽内面への塊状の付着物を掻き取り、かつ前記底面へ落下した前記塊状の付着物を含む濃縮物を前記羽根と前記底面との間で擂り潰しつつ濃縮度を高め、最終的に顆粒状またはフレーク状の乾燥された有機固形分を与えることを特徴とする蒸留酒廃液の真空濃縮乾燥槽。
External heating means for heating at least the inner surface of the tank consisting of the inner surface and bottom surface of the tank, a plurality of blades provided to slide on the inner surface of the tank corresponding to the external heating means, and vacuum exhaust In a vacuum concentration drying tank of distilled liquor waste liquid having a mouth,
The blade is elastically held by a spring material, and the blade scrapes off the massive deposit on the inner surface of the tank caused by the concentration of distilled liquor waste liquid, and removes the massive deposit that has fallen to the bottom surface. Vacuum concentration of distilled liquor waste liquor characterized by increasing the concentration while crushing the concentrate containing between the blades and the bottom surface, and finally giving dried organic solids in the form of granules or small flakes Drying tank.
前記乾燥された有機固形分の含有水分が10%以下である請求項1に記載の蒸溜酒廃液の真空濃縮乾燥槽。  The vacuum concentrated drying tank for distilled liquor waste liquid according to claim 1, wherein the moisture content of the dried organic solid content is 10% or less. 前記羽根がばね材によって弾性的に保持された樹脂厚板、樹脂ブロック又は金属ワイヤブラシである請求項1または請求項2に記載の蒸溜酒廃液の真空濃縮乾燥槽。  The vacuum concentrated drying tank of distilled liquor waste liquid according to claim 1 or 2, wherein the blade is a resin thick plate, a resin block or a metal wire brush elastically held by a spring material. 前記底面に対応する複数枚の前記羽根が前記底面の全体を分担して摺動するように配置されている請求項1から請求項3に記載の蒸留酒廃液の真空濃縮乾燥槽。  The vacuum concentrating and drying tank for distilled liquor waste liquid according to claim 1, wherein a plurality of the blades corresponding to the bottom surface are arranged to slide while sharing the entire bottom surface. 前記槽の底部に窒素ガス吹込み口が設けられている請求項1から請求項3までの何れかに記載の蒸溜酒廃液の真空濃縮乾燥槽。  The vacuum concentrated drying tank for distilled liquor waste liquid according to any one of claims 1 to 3, wherein a nitrogen gas blowing port is provided at the bottom of the tank. 前記外部加熱手段が濃縮時には温度75℃から80℃の温水によるジャケット加熱、乾燥時には温度約60℃の温水によるジャケット加熱である請求項1から請求項4までの何れかに記載の蒸溜酒廃液の真空濃縮乾燥槽。  The distilled liquor waste liquor according to any one of claims 1 to 4, wherein the external heating means is jacket heating with warm water at a temperature of 75 ° C to 80 ° C during concentration, and jacket heating with warm water at a temperature of about 60 ° C during drying. Vacuum concentration drying tank. 少なくとも槽の直胴部内面及び底面からなる槽内面を外部加熱し、前記外部加熱に対応する前記槽内面を複数枚の羽根で摺動させ、真空排気する蒸溜酒廃液の真空濃縮乾燥方法において、
蒸留酒廃液の濃縮と共に生ずる前記槽内面への塊状の付着物をばね材で弾性的に保持した前記羽根によって掻き取り、かつ前記底面へ落下した前記塊状の付着物を含む濃縮物を前記羽根と前記底面との間で擂り潰しつつ濃縮度を高める濃縮工程と、含有水分が約30%以下となった状態で加熱温度および前記羽根の摺動回数を前記濃縮工程より低下させ、顆粒状またはフレーク状の有機固形分となるまで乾燥する乾燥工程とからなることを特徴とする蒸留酒廃液の真空濃縮乾燥方法。
Vacuum concentrating drying method of distilled liquor waste liquid that externally heats at least a tank inner surface composed of an inner surface and a bottom surface of the tank, slides the tank inner surface corresponding to the external heating with a plurality of blades, and evacuates In
The blade- like deposits which are elastically held by a spring material are scraped off by the blades elastically held by the spring material , and the concentrate containing the block-like deposits dropped to the bottom surface is generated by the concentration of the distilled liquor waste liquid. Reducing the heating temperature and the number of sliding times of the blades in a state where the moisture content is about 30% or less than the concentration step, A vacuum concentration drying method for distilled liquor waste liquor, comprising a drying step of drying until a small flaky organic solid content is obtained.
前記乾燥工程において含有水分が10%以下の顆粒状またはフレーク状の有機固形分が得られるまで乾燥する請求項7に記載の蒸留酒廃液の真空濃縮乾燥方法。The method for vacuum concentrating and drying distilled liquor waste liquid according to claim 7, wherein the drying step is performed until a granular or small flake organic solid content having a water content of 10% or less is obtained. ばね材を介して弾性的に保持された樹脂厚板、樹脂ブロック又は金属ワイヤブラシからなる前記羽根によって前記槽内面を摺動させる請求項7または請求項8に記載の蒸留酒廃液の真空濃縮乾燥方法。  The vacuum concentration of distilled liquor waste liquid according to claim 7 or 8, wherein the inner surface of the tank is slid by the blades made of a resin thick plate, a resin block or a metal wire brush elastically held through a spring material. Drying method. 前記濃縮工程において、前記槽内へ窒素ガスを間欠的に吹き込む請求項7から請求項9までの何れかに記載の蒸溜酒廃液の真空濃縮乾燥方法。  The method for vacuum concentration drying of distilled liquor waste liquid according to any one of claims 7 to 9, wherein nitrogen gas is intermittently blown into the tank in the concentration step. 前記外部加熱を前記濃縮工程では75℃から80℃の温水を使用し、前記乾燥工程では約60℃の温水を使用するジャケット加熱によって行う請求項7から請求項10までの何れかに記載の蒸溜酒廃液の真空濃縮乾燥方法。  The distillation according to any one of claims 7 to 10, wherein the external heating is performed by jacket heating using hot water of 75 ° C to 80 ° C in the concentration step and using hot water of about 60 ° C in the drying step. Vacuum concentration drying method for liquor waste liquor.
JP35010093A 1993-12-27 1993-12-27 Vacuum concentration drying tank for distilled liquor waste liquor and vacuum concentration drying method Expired - Lifetime JP3693687B2 (en)

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