JP3521073B2 - Freeze-thaw method and freeze-thaw device - Google Patents
Freeze-thaw method and freeze-thaw deviceInfo
- Publication number
- JP3521073B2 JP3521073B2 JP33126499A JP33126499A JP3521073B2 JP 3521073 B2 JP3521073 B2 JP 3521073B2 JP 33126499 A JP33126499 A JP 33126499A JP 33126499 A JP33126499 A JP 33126499A JP 3521073 B2 JP3521073 B2 JP 3521073B2
- Authority
- JP
- Japan
- Prior art keywords
- freeze
- thaw
- freezing
- substance
- sludge
- 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 - Fee Related
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Landscapes
- Micro-Organisms Or Cultivation Processes Thereof (AREA)
- Treatment Of Sludge (AREA)
Description
【0001】[0001]
【発明の属する技術分野】本発明は凍結融解方法と凍結
融解装置に関し、詳しくは、主として汚泥の脱水プロセ
スの前処理として用いられる凍結融解方法とこれに用い
る凍結融解装置に関する。TECHNICAL FIELD The present invention relates to a freeze-thaw method and a freeze-thaw apparatus, and more particularly to a freeze-thaw method mainly used as a pretreatment for a sludge dewatering process and a freeze-thaw apparatus used therefor.
【0002】[0002]
【従来の技術】排水を浄化するためには、排水中に汚泥
などの固形分が混在しているので、汚泥を水分から分
離、すなわち固液分離を必要とする。しかながら汚泥の
性状は、原水の状態や使用する凝集剤によって異なり、
その成分は一般に、水酸化アルミニウム、粘土質、コロ
イド質、微生物および他の有機、無機の物質で構成され
ていて、水分が多くゼラチン状をなしている。従って、
ろ過性が悪く、しかも分離された汚泥の含水率が高いの
で、輸送費、埋め立て焼却などの後処理に少なくない負
担がかかる。そのため、後処理する前に薬品注入による
凝集作用を利用する方法が用いられている。無機系凝集
剤の石灰、塩化第二鉄を注入薬品として使用する場合、
ろ過性は改善されるが、薬品注入することによって処分
汚泥量が増量するという問題がある。2. Description of the Related Art In order to purify waste water, solid contents such as sludge are mixed in the waste water, so that sludge needs to be separated from water, that is, solid-liquid separation. However, the properties of sludge vary depending on the condition of raw water and the coagulant used.
Its constituents are generally composed of aluminum hydroxide, clays, colloids, micro-organisms and other organic and inorganic substances, which are watery and gelatinous. Therefore,
Poor filterability and the high water content of the separated sludge impose a considerable burden on post-treatment such as transportation costs and landfill incineration. Therefore, a method of utilizing the aggregating action by chemical injection before post-treatment is used. When using inorganic coagulant lime, ferric chloride as injection chemical,
Although the filterability is improved, there is a problem that the amount of sludge to be disposed of is increased by injecting chemicals.
【0003】一方、有機系の高分子凝集剤はどうしても
変性ポリマーを含むため、これらが環境中に漏洩する
と、生物生育を阻害する環境ホルモンとしての働きをす
る恐れがあり、特に浄水処理する分野ではその使用が制
限される。On the other hand, the organic polymer flocculants inevitably contain modified polymers, so if they leak into the environment, they may act as environmental hormones that inhibit biological growth, especially in the field of water purification. Its use is limited.
【0004】そこで、汚泥を脱水する方法としては、無
薬注方式が好ましく、そのうち特に好ましいのは、ろ過
性能がよくて環境に余り影響を与えない凍結融解法であ
る。この凍結融解法は、全ての汚泥に対して適用でき、
低含水率の脱水汚泥が得られ、薬品を使用しないため処
分された汚泥の増量がなく、土壌還元の際に問題を生じ
ない等の優れた特徴がある。Therefore, as a method for dewatering sludge, a non-chemical injection method is preferable, and a freezing and thawing method, which has good filtration performance and does not significantly affect the environment, is particularly preferable. This freeze-thaw method can be applied to all sludge,
Dehydrated sludge with a low water content can be obtained, and since it does not use chemicals, it does not increase the amount of sludge that has been disposed of, and it has excellent characteristics such as no problems during soil reduction.
【0005】凍結融解法の原理は、汚泥中に含有する水
分とその表面に付着する水分が存在することに着目し、
冷凍されることにより水分を氷の結晶として成長させ、
その際に汚泥は未凍結ゾーンに押しやられて微細な粒子
どうしが大きなブロック状に結合合体しながら濃縮し
て、ろ過特性を改善するものである。更に、全体に凍結
すると氷の生成の膨張力により、汚泥に強力な圧縮力が
加わるため、汚泥の組織(蛋白質や炭水化物のミセル構
造あるいはゲル状物質のゲル状構造など)が破壊されて
内部に包含されている水分が流出し、より脱水効果が高
くなる。The principle of the freeze-thaw method is to pay attention to the existence of water contained in sludge and water adhering to the surface of the sludge,
By being frozen, the water grows as ice crystals,
At that time, the sludge is pushed to the unfrozen zone and the fine particles are concentrated while being combined and combined into a large block to improve the filtration characteristics. Furthermore, when the whole is frozen, the expansive force of ice formation gives a strong compressive force to the sludge, which destroys the sludge structure (protein or carbohydrate micelle structure or gel-like structure of gel-like substance) and The contained water flows out, and the dehydration effect becomes higher.
【0006】[0006]
【発明が解決しようとする課題】しかしながら、凍結融
解法は汚泥を凍結させるためのエネルギーを多量に必要
とし、エネルギーコストが高くつくことと、脱水性が高
分子凝集剤などを用いる場合に比べて低いといった問題
がある。However, the freeze-thaw method requires a large amount of energy for freezing the sludge, and the energy cost is high, and the dehydration property is higher than that when a polymer flocculant is used. There is a problem such as low.
【0007】そこで、本発明の目的は、上記従来技術の
有する問題点に鑑みて、汚泥のような被処理物の凍結を
効率よく行うことによって凍結に要するエネルギーを少
なくでき、しかも脱水性を良好にできる凍結融解方法と
凍結融解装置を提供することにある。In view of the above-mentioned problems of the prior art, therefore, the object of the present invention is to efficiently freeze an object to be treated such as sludge, thereby reducing the energy required for freezing and having good dehydration property. Another object of the present invention is to provide a freeze-thaw method and a freeze-thaw apparatus that can be used.
【0008】[0008]
【課題を解決するための手段】上記目的は各請求項記載
の発明により達成される。すなわち、本発明に係る凍結
融解方法の特徴構成は、被処理物を凍結し、凍結された
前記被処理物を融解して脱水する凍結融解方法であっ
て、前記被処理物を凍結する際に、前記被処理物を濃縮
すると共に、この濃縮された前記被処理物を凍結融解す
る前に、予め作成した前記被処理物と氷核活性タンパク
質様物質とを均一分散可能に十分撹拌して予混合物を作
成し、ついでこの予混合物を凍結融解槽に投入し、これ
らをアンモニア吸収冷凍機により凍結と融解とを行うと
共に、前記アンモニア吸収冷凍機を構成する吸収器の冷
却を、凍結した被処理物の融解時に発生する冷熱源を利
用して行うことにある。The above objects can be achieved by the inventions described in the claims. That is, the characteristic configuration of the freeze-thaw method according to the present invention is a freeze-thaw method of freezing the object to be processed, melting and dehydrating the frozen object to be processed, when freezing the object to be processed. , Concentrate the object to be treated
At the same time, freeze and thaw the concentrated product to be treated.
Before mixing, the pre-prepared material to be treated and the ice nucleation active proteinaceous substance are sufficiently stirred so that they can be uniformly dispersed to prepare a pre-mixture.
Form, then put the premix to freeze molten bath, which
When they are frozen and thawed by an ammonia absorption refrigerator,
Together, the cooling of the absorber that constitutes the ammonia absorption refrigerator
Of the cold heat source generated when the frozen processed material is thawed.
To do it.
【0009】この構成によれば、予め被処理物と氷核活
性タンパク質様物質との混合物を作成するため、これら
が均一に入り交じって混合され、これを凍結融解槽に投
入すると、氷核活性タンパク質様物質の存在により被処
理物の凍結開始温度が上昇すると共に、均一分散した氷
核活性タンパク質様物質の周辺から凍結が開始し、これ
ら凍結を開始した多数の微細な被処理物を核として、凍
結融解槽中の被処理物の凍結がムラを生じることなく効
率的に成長し、凍結効率を極めて高いものとすることが
できる。従って、脱水時の濾過比抵抗が小さくなって、
水分を排除し易くなり脱水工程を効率良く行うことがで
きる。又、使用する氷核活性タンパク質様物質は氷核活
性細菌より得られるのであり、生菌のままではないた
め、汚染その他の問題を生じることがなく、取り扱いが
容易であり、作業効率も高いものである。しかも、被処
理物脱水の前処理として、熱駆動によって冷凍サイクル
を作動させることが可能なため消費電力の負担の少ない
アンモニア吸収冷凍機を利用するので、省電力効果を発
揮できると共に、被処理物が汚泥である場合、全ての汚
泥に対して適用でき、低含水率の脱水汚泥が得られ、無
薬注方式であるため処分された汚泥の増量がなく、土壌
還元の際に問題を生じない等の優れた吸収冷凍機の利点
をそのまま生かすことができ、更に、アンモニア吸収冷
凍機により凍結融解し汚泥の融解時に生ずる冷熱を、吸
収冷凍機の吸収器の冷却熱源に一部利用するので、冷凍
機の駆動エネルギーの低温化ならびに成績係数を高め、
一層省エネルギー化および省電力化を達成することがで
きて都合がよい。 According to this structure, since the mixture of the object to be treated and the ice nucleation active proteinaceous substance is prepared in advance, they are mixed uniformly and mixed, and when this is put into the freeze-thaw tank, the ice nucleation activity is The presence of the protein-like substance raises the freezing start temperature of the object to be treated, and freezing starts around the uniformly dispersed ice nuclei active protein-like substance, and many fine objects to be frozen are used as nuclei. The freezing and thawing tank can be efficiently grown without causing unevenness in freezing of the object to be processed, and the freezing efficiency can be made extremely high. Therefore, the filtration specific resistance during dehydration becomes small,
It becomes easier to remove water, and the dehydration process can be performed efficiently. In addition, since the ice nucleation active protein-like substance used is obtained from ice nucleation active bacteria and does not remain viable, it does not cause contamination or other problems, is easy to handle, and has high work efficiency. Is. Moreover, the subject
Refrigeration cycle by heat drive as a pretreatment for physical dehydration
Since it can be operated, the burden of power consumption is small
Ammonia absorption refrigerator is used, resulting in power saving effect.
In addition to being able to volatilize, if the object to be treated is sludge,
It can be applied to mud, and dehydrated sludge with low water content can be obtained.
Since it is a chemical injection system, there is no increase in the amount of sludge that has been
Advantages of an excellent absorption refrigerator that does not cause problems during reduction
Can be used as is, and ammonia absorption cooling
The cold heat generated when the sludge is thawed by freezing and thawing by a freezer is absorbed.
Since it is partially used as a cooling heat source for the absorber of the refrigerator / freezer,
Lowering the driving energy of the machine and increasing the coefficient of performance,
It is possible to achieve further energy saving and power saving.
It's convenient to come.
【0010】その結果、汚泥のような被処理物の凍結を
効率よく行うことによって凍結に要するエネルギーを少
なくでき、しかも次工程での脱水処理の効率を高めて脱
水性を良好にできる凍結融解方法を提供することができ
た。As a result, the freezing and thawing method can efficiently reduce the energy required for freezing by efficiently freezing an object to be treated such as sludge, and further improve the efficiency of the dehydration treatment in the next step to improve the dehydration property. Could be provided.
【0011】尚、本発明にいう汚泥は、浄水場や下水処
理場で発生する汚泥、産業廃水処理汚泥、埋め立て廃水
処理汚泥、し尿処理汚泥などあらゆる種類の汚泥を含む
ものである。The sludge referred to in the present invention includes all kinds of sludge such as sludge generated in water purification plants and sewage treatment plants, industrial wastewater treatment sludge, landfill wastewater treatment sludge, and human waste treatment sludge.
【0012】前記被処理物と氷核活性タンパク質様物質
との予混合物は、濃縮された被処理物に粉末状氷核活性
タンパク質様物質を混合して作成することが好ましい。The pre-mixture of the substance to be treated and the ice-nucleus active protein-like substance is preferably prepared by mixing the concentrated substance to be treated with the powdery ice-nucleus active protein-like substance.
【0013】この構成によれば、被処理物が濃縮されて
いるため凍結効率が高められると共に、氷核活性タンパ
ク質様物質が粉末状であることから取り扱いが容易であ
り、被処理物の凍結開始点としての核を多数かつ均一に
生成することができて都合がよい。According to this structure, the object to be treated is concentrated, so that the freezing efficiency is enhanced, and the ice-nucleus active protein-like substance is in powder form, so that it is easy to handle, and the start of freezing of the object to be treated is started. It is convenient that many nuclei as points can be uniformly generated.
【0014】前記アンモニア吸収冷凍機に接続されてい
る蓄熱槽を利用することが好ましい。この構成によれ
ば、熱の有効利用ができ消費電力の低減につながって都
合がよい。 Connected to the ammonia absorption refrigerator
It is preferable to utilize a heat storage tank. With this configuration
In this way, effective use of heat leads to reduction of power consumption and
Good match.
【0015】前記被処理物に対して、前記氷核活性タン
パク質様物質を0.01〜0.1g/L混合することが
好ましい。被処理物に対して、氷核活性タンパク質様物
質が0.01g/L未満であると凍結効率が低く、0.
1g/Lを越えて混合すると、添加した量の割に効果が
少なくて好ましくないからである。With respect to the object to be treated,
It is possible to mix 0.01-0.1 g / L of proteinaceous substance.
preferable. If the ice nucleation active protein-like substance is less than 0.01 g / L with respect to the object to be treated, the freezing efficiency is low and
This is because mixing more than 1 g / L is not preferable because the effect is small relative to the added amount.
【0016】前記氷核活性タンパク質様物質が、培養さ
れた生菌を0.2μm径のフィルターで濾過・抽出して
使用することが好ましい。[0016] It is preferable that the ice-nucleus active protein-like substance is used by filtering and extracting live cultured bacteria with a filter having a diameter of 0.2 µm.
【0017】この構成によれば、氷核活性細菌の氷核活
性を行う部分が氷核活性細菌の細胞壁外に形成される5
0〜200nm程度の大きさの水泡状の小胞成分(リン
脂質ホスファチジルイノシトールを含む高濃度アミノ基
の連鎖状物からなる)であるため、これらを濾過・抽出
してタンパク質様物質を取り出して使用することによ
り、一層凍結効率を高いものとすることができる。氷核
活性細菌としては、Erwinia herbicola,Pseudomonus fl
uorescens,Pseudomonas syringage 菌などを使用するこ
とができる。According to this structure, the ice nucleus-activating portion of the ice-nucleating bacteria is formed outside the cell wall of the ice-nucleating bacteria. 5
Since it is a blistering vesicle component with a size of about 0 to 200 nm (consisting of a high-concentration chain of amino groups containing phospholipid phosphatidylinositol), these are filtered and extracted to extract a proteinaceous substance for use. By doing so, the freezing efficiency can be further increased. Examples of ice-nucleating bacteria include Erwinia herbicola, Pseudomonus fl
Uorescens, Pseudomonas syringage fungus, etc. can be used.
【0018】更に、本発明に係る凍結融解装置の特徴構
成は、被処理物を収納可能で、収納された前記被処理物
を吸収冷凍機により凍結と融解とを行う凍結融解槽と、
前記吸収冷凍機を冷却する冷却塔とを備えていて、予め
被処理物と氷核活性タンパク質様物質とを均一分散した
予混合物を作成する撹拌機能を備えた予混合槽と、この
予混合槽から前記予混合物を前記凍結融解槽に投入する
機構を有していると共に、前記吸収冷凍機がアンモニア
吸収冷凍機であって、このアンモニア吸収冷凍機を構成
する吸収器の冷却を、凍結した前記被処理物の融解時に
発生する冷熱源を利用して行うことにある。Further, the characteristic constitution of the freeze-thaw apparatus according to the present invention is that the object to be treated can be stored and the stored object to be treated is stored.
A freeze-thaw tank for freezing and thawing with an absorption refrigerator,
Including a cooling tower for cooling the absorption refrigerator,
The object to be treated and the ice nucleation active protein-like substance were uniformly dispersed
A premixing tank with a stirring function to create a premix,
Charge the premix into the freeze-thaw tank from a premix tank
The absorption refrigerator has a mechanism and
Absorption refrigerator, which constitutes this ammonia absorption refrigerator
Cooling of the absorber during melting of the frozen processed material
This is done by using the cold heat source that is generated .
【0019】この構成によれば、被処理物と氷核活性タ
ンパク質様物質との混合物を作成する予混合槽を備えて
いるため、予混合槽により混合されたものを凍結融解槽
に投入することにより、被処理物の凍結開始温度が上昇
すると共に、均一分散した氷核活性タンパク質様物質の
周辺から凍結が開始し、これら凍結を開始した多数の微
細な被処理物を核として、凍結融解槽中の被処理物の凍
結がムラを生じることなく効率的に成長し、凍結効率を
極めて高いものとすることができる。その結果、汚泥の
ような被処理物の凍結を効率よく行うことによって凍結
に要するエネルギーを少なくでき、しかも脱水性を良好
にできる凍結融解装置を提供することができた。しか
も、被処理物脱水の前処理として、熱駆動によって冷凍
サイクルを作動させることが可能なため消費電力の負担
の少ないアンモニア吸収冷凍機を利用するので、省電力
効果を発揮できると共に、被処理物が汚泥である場合、
全ての汚泥に対して適用でき、低含水率の脱水汚泥が得
られ、無薬注方式であるため処分された汚泥の増量がな
く、土壌還元の際に問題を生じない等の優れた吸収冷凍
機の利点をそのまま生かすことができ、更に、アンモニ
ア吸収冷凍機により凍結融解し汚泥の融解時に生ずる冷
熱を、吸収冷凍機の吸収器の冷却熱源に一部利用するの
で、冷凍機の駆動エネルギーの低温化ならびに成績係数
を高め、一層省エネルギー化および省電力化を達成する
ことができて都合がよい。 According to this structure, since the premixing tank for preparing the mixture of the object to be treated and the ice nucleation active protein-like substance is provided, the mixture mixed by the premixing tank is put into the freeze-thaw tank. As a result, the freezing start temperature of the object to be treated rises and freezing starts around the uniformly dispersed ice nuclei active proteinaceous substance. The freezing of the object to be processed can be efficiently grown without causing unevenness, and the freezing efficiency can be made extremely high. As a result, it was possible to provide a freeze-thaw apparatus which can reduce the energy required for freezing by efficiently freezing an object to be treated such as sludge, and can improve the dehydration property. Only
Also, it is frozen by heat drive as a pretreatment for dehydration of the object to be treated
Power consumption due to the ability to operate the cycle
Uses an ammonia absorption refrigerator with less energy consumption
In addition to being able to exert the effect, when the object to be treated is sludge,
Applicable to all types of sludge and obtains dehydrated sludge with low water content
The non-chemical injection method does not increase the amount of sludge that has been disposed.
And excellent absorption refrigeration that does not cause problems during soil reduction
You can use the advantages of the machine as it is,
A) Freezing and thawing by an absorption chiller and cooling that occurs when the sludge is thawed
Part of the heat is used as a cooling heat source for the absorption refrigerator's absorber
Therefore, lowering the driving energy of the refrigerator and the coefficient of performance
To further reduce energy consumption and power consumption
It is convenient to be able to.
【0020】前記アンモニア吸収冷凍機に蓄熱槽が接続
されていることが好ましい。A heat storage tank is connected to the ammonia absorption refrigerator.
It is preferable to have been.
【0021】この構成によれば、熱の有効利用ができ消
費電力の低減につながって都合がよい。 According to this structure, heat can be effectively utilized and consumed.
This is convenient because it leads to a reduction in power consumption.
【0022】[0022]
【発明の実施の形態】本発明の実施の形態を、図面を参
照して詳細に説明する。図1は、汚泥凍結融解処理シス
テムを氷蓄熱システムに利用した場合の概略全体構造を
示す。この凍結融解装置は、冷却源である冷却塔1と被
処理物である汚泥を凍結あるいは融解する凍結融解槽2
と吸収冷凍機3とからなる。冷却塔1は、吸収冷凍機3
で使用する冷媒のアンモニアを冷却する冷却水を冷却す
るために設けられている。凍結融解槽2は、図1では1
台のみを示すが、通常、複数台並列して設置されてい
る。吸収冷凍機3で使用する冷媒としてアンモニアを用
いると、消費電力の負担が少ないので省電力効果を発揮
できるのみならず、全ての汚泥に対して適用でき、低含
水率の脱水汚泥が得られ、無薬注方式であるため処分さ
れた汚泥の増量がなく、土壌還元の際に問題を生じるこ
とがない。BEST MODE FOR CARRYING OUT THE INVENTION Embodiments of the present invention will be described in detail with reference to the drawings. FIG. 1 shows a schematic overall structure when the sludge freeze-thaw treatment system is used for an ice heat storage system. This freeze-thaw apparatus comprises a cooling tower 1 as a cooling source and a freeze-thaw tank 2 for freezing or thawing sludge as an object to be treated.
And an absorption refrigerator 3. The cooling tower 1 is an absorption refrigerator 3.
It is provided to cool the cooling water that cools the ammonia used as the refrigerant. The freeze-thaw tank 2 is 1 in FIG.
Although only a stand is shown, a plurality of stands are usually installed in parallel. When ammonia is used as the refrigerant used in the absorption refrigerator 3, the burden of power consumption is small so that not only the power saving effect can be exhibited but also it can be applied to all sludges, and a dehydrated sludge with a low water content can be obtained. Since it is a non-chemical injection method, there is no increase in the amount of sludge that has been disposed, and there is no problem in soil reduction.
【0023】凍結融解槽2には、図2に示す工程に従い
汚泥が投入されるようになっている。すなわち、汚泥を
含む原水は一旦排泥池15に導入されてある程度の量に
なるまで貯蔵され、この排泥池15から順次ポンプPに
より濃縮槽16に送られ、ここで汚泥はモータM駆動の
攪拌機21により攪拌されつつ数%程度に濃縮されてか
ら、濃縮された汚泥を汚泥貯槽17で貯槽し、ここでも
モータM駆動の攪拌機22により十分攪拌する。つい
で、攪拌された濃縮汚泥を遠心分離機18に順次送給
し、汚泥を更に濃縮し、濃縮された汚泥を順次、濃縮汚
泥槽19に送り込む。この濃縮汚泥槽19でも、モータ
M駆動の攪拌機23により汚泥を十分に攪拌する。そし
て、濃縮汚泥槽19で濃縮された汚泥を凍結融解槽2に
送給する前に、比較的小容量の予混合槽20を配置して
おき、この予混合槽20に送られた濃縮汚泥に、粉末状
をした氷核活性タンパク質様物質を適量投入し、両者が
均一に分散されるように攪拌装置24を用いて十分攪拌
する。このようにして均一分散された濃縮汚泥と氷核活
性タンパク質様物質とが、凍結融解槽2に投入され、汚
泥に含有されている水分の分離ならびに固形物の凝集が
なされる。通常、凍結融解槽2で凍結される汚泥は、−
10℃以下に冷却する必要があるが、氷核活性タンパク
質様物質を混入しているため、−2〜−5℃で凍結は開
始し、汚泥の量にもよるが、約−10℃で凍結融解槽に
投入される全汚泥は確実に凍結される。従って、凍結融
解槽における冷却に要するエネルギーコストを、従来技
術に比べて著しく少なくできることになる。Sludge is put in the freeze-thaw tank 2 according to the process shown in FIG. That is, the raw water containing sludge is once introduced into the sludge basin 15 and stored until it reaches a certain amount, and is sequentially sent from the sludge basin 15 to the concentration tank 16 by the pump P, where the sludge is driven by the motor M. After being agitated by the agitator 21 and being concentrated to about several%, the concentrated sludge is stored in the sludge storage tank 17, and the agitator 22 driven by the motor M also sufficiently agitates the sludge. Next, the stirred concentrated sludge is sequentially fed to the centrifugal separator 18, the sludge is further concentrated, and the concentrated sludge is sequentially fed to the concentrated sludge tank 19. Even in the concentrated sludge tank 19, the agitator 23 driven by the motor M sufficiently agitates the sludge. Then, before sending the sludge concentrated in the thickened sludge tank 19 to the freeze-thaw tank 2, a relatively small capacity premixing tank 20 is arranged, and the thickened sludge sent to this premixing tank 20 is Then, an appropriate amount of powdery ice-nucleus active protein-like substance is added and sufficiently stirred using a stirring device 24 so that both are uniformly dispersed. The concentrated sludge thus uniformly dispersed and the ice nucleus active protein-like substance are put into the freeze-thaw tank 2 to separate the water contained in the sludge and agglomerate the solid matter. Usually, the sludge frozen in the freeze-thaw tank 2 is-
It needs to be cooled to 10 ℃ or less, but because ice-nucleus active protein-like substance is mixed, freezing starts at -2 to -5 ℃ and it freezes at about -10 ℃, depending on the amount of sludge. All the sludge put into the melting tank is surely frozen. Therefore, the energy cost required for cooling in the freeze-thaw tank can be significantly reduced as compared with the prior art.
【0024】解凍された汚泥は、更に真空脱水機などの
脱水装置25により脱水ケーキとされ、乾燥されて処理
されるが、汚泥が粒状化しているため、脱水し易くなっ
ている。脱水装置としては、真空脱水機の他、遠心分離
機、加圧脱水機などを使用できる。乾燥された汚泥ケー
キは、焼却炉などにより焼却処理される。その排熱は、
吸収冷凍機3の駆動源として利用することができる。The thawed sludge is further made into a dehydrated cake by a dehydrating device 25 such as a vacuum dehydrator and dried and processed. However, since the sludge is granulated, it is easily dehydrated. As the dehydrator, a vacuum separator, a centrifugal separator, a pressure dehydrator, or the like can be used. The dried sludge cake is incinerated in an incinerator or the like. The exhaust heat is
It can be used as a drive source for the absorption refrigerator 3.
【0025】尚、氷核活性タンパク質様物質としては、
氷核活性細菌であるErwinia herbicola,Pseudomonus fl
uorescens,Pseudomonas syringage 菌などをL培地その
他を用いて培養し、集菌すると共に物理的に破壊して殺
菌し、これを凍結乾燥後、粉砕して粉末状にしたものを
使用した。As the ice nucleation active protein-like substance,
Erwinia herbicola and Pseudomonus fl are ice-nucleating bacteria
Uorescens, Pseudomonas syringage, etc. were cultivated in L medium or the like to collect the bacteria, physically destroy them to sterilize, freeze-dry this, and then pulverize into powder.
【0026】次に、図1を参照して凍結融解装置につい
て更に詳しく説明する。吸収冷凍機3は、冷媒、例えば
アンモニアを放熱液化する凝縮器4と、アンモニアを蒸
発させる蒸発器5と、この蒸発器5で蒸発したアンモニ
ア蒸気を吸収剤である水に吸収させる吸収器6とを備え
て構成されている。もっとも、この吸収器6により冷媒
を十分に含んだアンモニア水溶液を溶液ポンプ(図示
略)で加圧して送給される発生器と、アンモニア濃度を
高めてこれを凝縮器4に送る精留器とを備えさせてもよ
い。更に、吸収冷凍機3を作動させる駆動源として、図
示はしないが、汚泥の焼却、コージェネレーション等の
排熱エネルギーが供給されるようになっている。Next, the freeze-thaw apparatus will be described in more detail with reference to FIG. The absorption refrigerator 3 includes a condenser 4 that liquefies a refrigerant such as ammonia by heat radiation, an evaporator 5 that evaporates ammonia, and an absorber 6 that absorbs the ammonia vapor evaporated by the evaporator 5 into water that is an absorbent. It is configured with. However, a generator that pressurizes and feeds an aqueous ammonia solution containing a sufficient amount of refrigerant with a solution pump (not shown) by the absorber 6, and a rectifier that raises the ammonia concentration and sends it to the condenser 4. May be provided. Further, as a drive source for operating the absorption refrigerator 3, although not shown, waste heat energy such as incineration of sludge and cogeneration is supplied.
【0027】高圧、高濃度アンモニア蒸気は凝縮器4に
送られ、ここで冷却塔1からの冷却水と熱交換されて凝
縮液化される。凝縮器4に、凝縮しないガス成分を除去
する抽気装置を設けてもよい。不凝縮ガスは凝縮あるい
は吸収など伝熱特性を低下させるので、これを除去する
と、伝熱特性を良好に維持できて都合がよい。尚、図1
で図番14は冷却水を送る冷却水ポンプである。The high-pressure, high-concentration ammonia vapor is sent to the condenser 4, where it is heat-exchanged with the cooling water from the cooling tower 1 to be condensed and liquefied. The condenser 4 may be provided with an extraction device that removes a gas component that does not condense. Since the non-condensable gas deteriorates the heat transfer characteristics such as condensation or absorption, it is convenient to remove the non-condensed gas because the heat transfer characteristics can be maintained well. Incidentally, FIG.
Reference number 14 is a cooling water pump for sending cooling water.
【0028】更に、蒸発器5と吸収器6にはブライン回
路が接続されている。このブライン回路は、低温の冷ブ
ラインタンク11と冷ブラインを送給する冷ブラインポ
ンプ12とからなる冷ブライン回路B1と、高温の温ブ
ラインタンク9と温ブラインを送給する温ブラインポン
プ10とからなる温ブライン回路B2とを備えていると
共に、温ブライン回路B2と冷ブライン回路B1とを切
り換える一対の冷温切換バルブ13,13’が設けられ
ている。そして、蒸発器5には冷ブライン回路B1が接
続されていると共に、吸収器6には温ブライン回路B2
が接続されている。凍結融解槽2に送給された汚泥を凍
結するときには、吸収冷凍機3の蒸発器5で冷却された
冷ブラインが直接凍結融解槽2に送り込まれて汚泥を凍
結する。尚、図番7は蓄熱槽であり、例えば、夏期の夜
間に冷熱をこの蓄熱槽に導いて氷蓄熱を行い、冬期の夜
間に温熱を蓄熱槽に導き、温水として蓄熱するように利
用する。もっとも、蓄熱槽7は本実施形態において必ず
しも必要ではないが、これを設けておくと、熱の有効利
用ができ消費電力の低減につながって都合がよい。図番
8,8’は、蓄熱槽7を利用るための切り換えバルブで
ある。Further, a brine circuit is connected to the evaporator 5 and the absorber 6. This brine circuit includes a cold brine circuit B1 including a low temperature cold brine tank 11 and a cold brine pump 12 that feeds cold brine, a hot brine tank 9 and a hot brine pump 10 that feeds warm brine. And a pair of cold temperature switching valves 13 and 13 'for switching between the hot brine circuit B2 and the cold brine circuit B1. A cold brine circuit B1 is connected to the evaporator 5, and a warm brine circuit B2 is connected to the absorber 6.
Are connected. When the sludge sent to the freeze-thaw tank 2 is frozen, the cold brine cooled by the evaporator 5 of the absorption refrigerator 3 is directly sent to the freeze-thaw tank 2 to freeze the sludge. It should be noted that FIG. 7 is a heat storage tank, and for example, it is used to guide cold heat to this heat storage tank at night in summer to perform ice heat storage, and to guide warm heat to the heat storage tank at night in winter to store heat as hot water. Of course, the heat storage tank 7 is not always necessary in the present embodiment, but if it is provided, the heat can be effectively used and the power consumption can be reduced, which is convenient. The reference numbers 8 and 8 ′ are switching valves for using the heat storage tank 7.
【0029】[0029]
【実施例】(実施例1)上記した氷核活性タンパク質様
物質と汚泥とを予め小型の混合槽に収納して攪拌混合し
たものを、凍結融解槽に順次投入したときの凍結温度、
濾過比抵抗、および含水率を測定した結果を、表1に示
す。尚、濾過比抵抗は、汚泥の脱水処理に関するヌッチ
ェ試験(日本下水道協会規定の「下水道試験方法」によ
る)を実施することにより測定した。Example 1 Freezing temperature when the above ice nucleation active protein-like substance and sludge were placed in a small mixing tank in advance and stirred and mixed, and then sequentially charged into a freeze-thaw tank,
Table 1 shows the results of measuring the filtration specific resistance and the water content. The filtration resistivity was measured by carrying out a Nutsche test for dehydration treatment of sludge (according to "Sewer Test Method" stipulated by the Japan Sewer Association).
【0030】[0030]
【表1】
表1からわかるように、氷核活性タンパク質様物質を
0.01g/L 以上添加すると、凍結開始温度が確実に高
くなり、濾過比抵抗が著しく小さくなって、しかも含水
率も低下したものが得られる。[Table 1] As can be seen from Table 1, when the ice nucleation active protein-like substance is added in an amount of 0.01 g / L or more, the freezing start temperature is certainly increased, the filtration resistivity is remarkably reduced, and the water content is reduced. To be
【0031】(実施例2)次に、予め小型の混合槽に収
納した汚泥に氷核活性タンパク質様物質を0.04g/L
添加し、5〜15分攪拌混合して作成した混合物を凍結
融解槽に投入した場合aと、予混合することなく凍結融
解槽に汚泥と氷核活性タンパク質様物質(添加量0.0
4g/L )を投入した場合bとの夫々について、投入物全
体が凍結する時間を比較した。その結果を図3に示す。
図3から明らかなように、予混合処理をした方aは、し
なかった場合bに比べて、投入物全体が凍結する温度
(約−10℃)に達する速度が早く、凍結時間を約2/
3に短縮できた。(Example 2) Next, 0.04 g / L of ice nucleus active protein-like substance was added to sludge previously stored in a small mixing tank.
When the mixture prepared by adding and stirring for 5 to 15 minutes is put into a freeze-thaw tank a, sludge and an ice nucleus active protein-like substance (added amount 0.0
4 g / L), the time when the entire charge was frozen was compared for each of b and b. The result is shown in FIG.
As is clear from FIG. 3, in the case of the pre-mixing treatment a, the temperature at which the entire input material freezes (about -10 ° C.) is faster than that in the case where the pre-mixing treatment is not performed, and the freezing time is about 2 /
I was able to shorten to 3.
【0032】[0032]
【0033】(1) 複数の凍結融解槽に対して温ブラ
イン回路と冷ブライン回路とを常に作動させるようにし
てもよい。つまり、1の凍結融解槽に対して汚泥を凍結
すべく冷ブライン回路を作動しておき、その間他の凍結
融解槽において既に凍結した汚泥を解凍すべく温ブライ
ン回路を作動するようにする。このような操作を順次複
数の凍結融解槽に対して行うことにより、汚泥の脱水前
処理を効率的に行うことができ、処理効率を高いものと
することができる。( 1 ) The hot brine circuit and the cold brine circuit may be always operated for a plurality of freeze-thaw tanks. That is, the cold brine circuit is operated to freeze the sludge in one freeze-thaw tank, while the warm brine circuit is operated to thaw the sludge already frozen in the other freeze-thaw tank. By sequentially performing such an operation on a plurality of freeze-thaw tanks, the pre-dewatering treatment of sludge can be efficiently performed, and the treatment efficiency can be increased.
【図1】本発明の一実施形態に係る凍結融解装置の概略
全体構成図FIG. 1 is a schematic overall configuration diagram of a freeze-thaw device according to an embodiment of the present invention.
【図2】図1の凍結融解装置を構成する凍結融解槽へ投
入する被処理物の処理を示す概略工程図FIG. 2 is a schematic process diagram showing the treatment of the object to be treated, which is put into a freeze-thaw tank constituting the freeze-thaw apparatus of FIG.
【図3】汚泥と氷核活性タンパク質様物質との予混合有
り無しについての凍結結果を示すグラフFIG. 3 is a graph showing the results of freezing with and without premixing of sludge and ice nucleation active proteinaceous substance.
2 凍結融解槽 3 吸収冷凍機 6 吸収器 20 予混合槽 2 Freeze-thaw tank 3 absorption refrigerator 6 absorber 20 premixing tank
───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI (C12N 1/00 C12R 1:39 C12R 1:38) (C12N 1/00 C12R 1:39) (C12N 1/20 C12R 1:18) (C12N 1/20 C12R 1:38) (C12N 1/20 C12R 1:39) (56)参考文献 特開 平4−126600(JP,A) 特開 平2−76595(JP,A) 特開 昭52−86257(JP,A) 特開 平9−264629(JP,A) (58)調査した分野(Int.Cl.7,DB名) C02F 11/00 - 11/20 C12N 1/00,1/20 ─────────────────────────────────────────────────── ─── Continued Front Page (51) Int.Cl. 7 Identification Code FI (C12N 1/00 C12R 1:39 C12R 1:38) (C12N 1/00 C12R 1:39) (C12N 1/20 C12R 1: 18) (C12N 1/20 C12R 1:38) (C12N 1/20 C12R 1:39) (56) References JP-A-4-126600 (JP, A) JP-A-2-76595 (JP, A) Kai 52-86257 (JP, A) JP-A-9-264629 (JP, A) (58) Fields investigated (Int.Cl. 7 , DB name) C02F 11/00-11/20 C12N 1/00, 1/20
Claims (5)
理物を融解して脱水する凍結融解方法であって、前記被
処理物を凍結する際に、前記被処理物を濃縮すると共
に、この濃縮された前記被処理物を凍結融解する前に、
予め作成した前記被処理物と氷核活性タンパク質様物質
とを均一分散可能に十分撹拌して予混合物を作成し、つ
いでこの予混合物を凍結融解槽に投入し、これらをアン
モニア吸収冷凍機により凍結と融解とを行うと共に、前
記アンモニア吸収冷凍機を構成する吸収器の冷却を、凍
結した被処理物の融解時に発生する冷熱源を利用して行
うことを特徴とする凍結融解方法。1. A freeze-thaw method for freezing an object to be processed, thawing the frozen object to be processed and dehydrating the same, wherein the object to be processed is concentrated when the object to be processed is frozen.
Before freeze-thawing the concentrated product to be treated,
The pre-prepared object to be treated and the ice nucleation active proteinaceous substance are sufficiently stirred so that they can be uniformly dispersed to prepare a pre-mixture.
Pour this premix into a freeze-thaw bath and unload them.
Freezing and thawing with a monia absorption refrigerator,
Freeze the cooling of the absorber that constitutes the ammonia absorption refrigerator.
Using the cold heat source that is generated when the bonded objects are melted
Freeze-thaw method, characterized in that the cormorant.
質との予混合物は、濃縮された被処理物に粉末状氷核活
性タンパク質様物質を混合して作成する請求項1の凍結
融解方法。2. The freeze-thaw method according to claim 1, wherein the pre-mixture of the substance to be treated and the ice-nucleus active protein-like substance is prepared by mixing the concentrated substance to be treated with the powdery ice-nucleus active protein-like substance. .
いる蓄熱槽を利用する請求項1又は2の凍結融解方法。3. Connected to the ammonia absorption refrigerator
The freezing and thawing method according to claim 1 or 2, which utilizes a heat storage tank .
被処理物を吸収冷凍機により凍結と融解とを行う凍結融
解槽と、前記吸収冷凍機を冷却する冷却塔とを備える凍
結融解装置であって、予め被処理物と氷核活性タンパク
質様物質とを均一分散した予混合物を作成する撹拌機能
を備えた予混合槽と、この予混合槽から前記予混合物を
前記凍結融解槽に投入する機構を有していると共に、前
記吸収冷凍機がアンモニア吸収冷凍機であって、このア
ンモニア吸収冷凍機を構成する吸収器の冷却を、凍結し
た前記被処理物の融解時に発生する冷熱源を利用して行
うことを特徴とする凍結融解装置。 4. An object to be processed can be stored, and the stored object
Freezing and thawing that freezes and thaws the object to be processed with an absorption refrigerator.
Freezing provided with a thaw tank and a cooling tower for cooling the absorption refrigerator.
It is a melting and melting device, and the object to be treated and the ice nucleation active protein are previously prepared.
Stirring function to create a pre-mixture in which a substance like substance is uniformly dispersed
And a premixing tank equipped with
In addition to having a mechanism to put in the freeze-thaw tank,
If the absorption refrigerator is an ammonia absorption refrigerator,
Freeze the cooling of the absorber that constitutes the
In addition, the cold heat source generated when the processed material is melted is used.
Freezing and thawing device characterized by:
続されている請求項4の凍結融解装置。 5. A heat storage tank is connected to the ammonia absorption refrigerator.
The freeze-thaw apparatus according to claim 4, which is continued.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP33126499A JP3521073B2 (en) | 1999-11-22 | 1999-11-22 | Freeze-thaw method and freeze-thaw device |
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| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP33126499A JP3521073B2 (en) | 1999-11-22 | 1999-11-22 | Freeze-thaw method and freeze-thaw device |
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| Publication Number | Publication Date |
|---|---|
| JP2001145900A JP2001145900A (en) | 2001-05-29 |
| JP3521073B2 true JP3521073B2 (en) | 2004-04-19 |
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ID=18241753
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|---|---|---|---|
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