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JP3751307B2 - Sludge drying system - Google Patents
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JP3751307B2 - Sludge drying system - Google Patents

Sludge drying system Download PDF

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JP3751307B2
JP3751307B2 JP2004045276A JP2004045276A JP3751307B2 JP 3751307 B2 JP3751307 B2 JP 3751307B2 JP 2004045276 A JP2004045276 A JP 2004045276A JP 2004045276 A JP2004045276 A JP 2004045276A JP 3751307 B2 JP3751307 B2 JP 3751307B2
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sludge
hot air
hollow chamber
drying system
sludge drying
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祐介 酒井
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日本建鐵株式会社
株式会社マルミ
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Description

本発明は、排水処理設備等で大量に発生する汚泥を減量し、処理経費の削減を達成することのできる汚泥乾燥システムに関する。   The present invention relates to a sludge drying system capable of reducing sludge generated in a large amount in a wastewater treatment facility and the like and achieving reduction in treatment costs.

工場、汚水処理場等では大量の汚泥が発生する。汚泥はそのままでは含水率が高く、容積も大きいため、一般に脱水処理によって減量することが行われる。汚泥の性状によってシックナ、フィルタ等を組み合わせ、例えば重量で1/10、含水率を98〜99%程度から70〜80%程度にまで低下させることができる。   A large amount of sludge is generated in factories and sewage treatment plants. Since sludge has a high moisture content and a large volume as it is, it is generally reduced by dehydration. Thickeners, filters and the like can be combined depending on the properties of the sludge, for example, 1/10 by weight, and the moisture content can be reduced from about 98 to 99% to about 70 to 80%.

しかしながら、汚泥の発生量は廃水量自体および廃水中の有機物濃度に比例するため、廃水量が多く、かつ有機物濃度が高い場合にはこれらの従来の脱水処理を行ってもその処理量は膨大であり、さらなる減量を図るためには乾燥処理を行うことが必要である。しかし一般に乾燥処理施設は大型で広大なスペースを必要とし、乾燥に伴って臭気処理を必要とするケースも多いため、新たに建物を建築して室内にこれらの施設を収容しなければならないなど、設置にはさまざまな困難が伴っている。   However, since the amount of sludge generated is proportional to the amount of wastewater itself and the organic matter concentration in the wastewater, if the amount of wastewater is large and the organic matter concentration is high, the treatment amount is enormous even if these conventional dehydration treatments are performed. In order to further reduce the weight, it is necessary to perform a drying process. However, in general, drying treatment facilities require a large and vast space, and there are many cases that require odor treatment as they dry, so it is necessary to construct a new building and accommodate these facilities indoors, etc. There are various difficulties associated with installation.

ところで、特許文献1には豆腐製造の際に発生する豆腐殻(おから)を熱風により乾燥する豆腐殻乾燥装置が記載されている。図3によりこれを説明する。   By the way, Patent Document 1 describes a tofu shell drying apparatus that dries tofu shell (okara) generated in the production of tofu with hot air. This will be described with reference to FIG.

この図は豆腐殻乾燥装置11の内部構造を示す断面図で、セラミックを主成分とする所定径の多数のペレットPを収容し、横向きに設置された円筒形の中空室111と、この中空室111の上方に配置され、下端がこの中空室111に連通する箱状の上部中空室112と、前記中空室111の底部付近において先端をこの中空室111の外周面に開口し、この中空室111の接線方向に配置され、図示しない熱風発生装置からの熱風をこの中空室111内に供給するための熱風供給路113と、前記上部中空室112と前記熱風供給路113との間において先端を前記中空室111の外周面に開口し、直立して前記中空室111の接線方向に配置され、豆腐殻を前記中空室111内に供給するための豆腐殻供給路114と、前記上部中空室112の上端付近に設けられ、上部中空室112内の内容物が熱風とともに排出される排出口116とからなる。115は豆腐殻供給路114に設けたロータリー式のフィーダである。   This figure is a cross-sectional view showing the internal structure of the tofu husk drying apparatus 11, which accommodates a large number of pellets P having a predetermined diameter mainly composed of ceramic and is installed in a horizontal direction, and the hollow chamber 111. A box-shaped upper hollow chamber 112 disposed above the hollow chamber 111 and having a lower end communicating with the hollow chamber 111, and a tip opened to the outer peripheral surface of the hollow chamber 111 in the vicinity of the bottom of the hollow chamber 111. The hot air supply path 113 for supplying hot air from a hot air generator (not shown) into the hollow chamber 111, and the tip between the upper hollow chamber 112 and the hot air supply path 113 are arranged in the tangential direction of Opened in the outer peripheral surface of the hollow chamber 111, and is arranged upright and tangentially to the hollow chamber 111, and the tofu shell supply path 114 for supplying the tofu shell into the hollow chamber 111, and the upper hollow chamber 112 It is provided near the upper end, and the contents in the upper hollow chamber 112 are discharged with hot air. Made from the discharge port 116. that. Reference numeral 115 denotes a rotary feeder provided in the tofu husk supply path 114.

豆腐殻供給路114から中空室111内に豆腐殻を供給しつつ熱風供給路113から熱風を送り込むと、中空室111内のペレットPが熱風に吹き上げられて中空室111の内周面および上部の上部中空室112の内壁に衝突しながら飛び交い、供給される豆腐殻とも衝突を繰り返すため、豆腐殻は粉砕されて表面積が増大し、熱風によって乾燥を受けるとともに、ペレットPも熱風によって加熱、蓄熱され、遠赤外線を放出して一層の乾燥を促進し、粉砕され、乾燥されて軽くなった豆腐殻は気流に乗って舞い上がる。上部中空室112は分級チャンバであり、軽くなるにつれて上昇し、乾燥の終わったものが熱風と共に上部中空室112の排出口116から排出される。   When hot air is sent from the hot air supply passage 113 while supplying the tofu shell into the hollow chamber 111 from the tofu shell supply passage 114, the pellets P in the hollow chamber 111 are blown up by the hot air, and the inner peripheral surface and the upper portion of the hollow chamber 111 are The tofu husks collide with the inner wall of the upper hollow chamber 112 and repeatedly collide with the supplied tofu husks, so the tofu husks are crushed to increase the surface area and dried by hot air, and the pellets P are also heated and stored by hot air The far-infrared rays are emitted to promote further drying, and the crushed, dried and lightened tofu husks soar in the air current. The upper hollow chamber 112 is a classification chamber and rises as it becomes lighter, and the dried product is discharged from the outlet 116 of the upper hollow chamber 112 together with hot air.

さらに特許文献2には、図3とほぼ同じ装置を使用し、内部に収容するペレットPを機械的強度の大きい金属酸化物を主成分とするセラミックに限定して豆腐殻よりも比重の大きい含水物質(例えば陶土)を乾燥することが記載されているが、実験によれば汚泥の性状、とくに比重の違いによって汚泥が中空室111の内周面および上部の上部中空室112の内壁に付着したり、内部で塊状になって成長したり、充分に乾燥できないなどの問題点がある。また、熱風は高温のまま排出されるため熱効率も悪い。
特開平6−105663号公報 特開2000−146433号公報
Further, Patent Document 2 uses the same device as in FIG. 3 and limits the pellet P accommodated therein to a ceramic mainly composed of a metal oxide having a high mechanical strength, and has a higher specific gravity than tofu shell. Although it is described that a substance (for example, porcelain clay) is dried, according to experiments, the sludge adheres to the inner peripheral surface of the hollow chamber 111 and the inner wall of the upper hollow chamber 112 due to the difference in specific gravity. There is a problem that it grows in a lump shape inside or cannot be dried sufficiently. Moreover, since the hot air is discharged at a high temperature, the thermal efficiency is also poor.
JP-A-6-105663 JP 2000-146433 A

本発明は、汚泥のさまざまな含水率、比重などの相違に対応して的確な乾燥を行うことができるとともに、熱効率がよく、環境への2次汚染などの問題のない汚泥乾燥システムを実現することを目的とする。   The present invention realizes a sludge drying system that can perform accurate drying in response to differences in various moisture contents and specific gravity of sludge, has high thermal efficiency, and has no problems such as secondary pollution to the environment. For the purpose.

本発明は、金属または金属化合物を主成分とする所定径の多数のペレットを収容し、横向きに設置された円筒形の中空室と、この中空室の上方に配置され、下端がこの中空室に連通する箱状の上部中空室と、前記中空室の底部付近において先端をこの中空室の外周面に開口し、この中空室の接線方向に配置され、熱風をこの中空室内に供給するための熱風供給路と、前記上部中空室と前記熱風供給路との間において先端を前記中空室の外周面に開口し、直立して前記中空室の接線方向に配置され、汚泥を前記中空室内に供給するための汚泥供給路と、前記上部中空室の上端付近に設けられ、上部中空室内の内容物が熱風とともに排出される排出口とからなる汚泥乾燥装置本体に、前記熱風供給路に熱風を供給する熱風発生装置を付設してなる汚泥乾燥装置と、
前記排出口から排出されるペレットを捕捉して上部中空室内に戻すスクリーンと、前記排出口から排出される熱風から乾燥汚泥を分離する集塵装置と、この集塵装置で分離された乾燥汚泥を貯留する乾燥汚泥貯留手段と、この集塵装置で乾燥汚泥を分離された熱風を清浄化するガス清浄装置と
で構成したことを特徴とする汚泥乾燥システムであり、望ましくは前記のペレットの径が6.0ないし10.0mmの範囲である前記の汚泥乾燥システムであり、また前記のペレットの表面を非付着性の材質とした前記の汚泥乾燥システムであり、さらに前記の中空室および上部中空室の内壁面を非付着性の材質とした前記の汚泥乾燥システムである。
The present invention accommodates a large number of pellets having a predetermined diameter mainly composed of a metal or a metal compound, and is disposed in a horizontal direction in a cylindrical hollow chamber and above the hollow chamber, and the lower end is located in the hollow chamber. A box-shaped upper hollow chamber that communicates, and a hot air for supplying hot air into the hollow chamber, the tip opening at the outer peripheral surface of the hollow chamber in the vicinity of the bottom of the hollow chamber, arranged in the tangential direction of the hollow chamber A tip is opened in the outer peripheral surface of the hollow chamber between the supply passage, the upper hollow chamber, and the hot air supply passage, and is arranged upright and tangentially to the hollow chamber to supply sludge into the hollow chamber. The hot air is supplied to the hot air supply path to a sludge drying apparatus body which is provided near the upper end of the upper hollow chamber and a discharge port through which the contents in the upper hollow chamber are discharged together with the hot air. A hot air generator is attached. And mud drying device,
A screen that captures pellets discharged from the discharge port and returns them to the upper hollow chamber, a dust collector that separates dry sludge from hot air discharged from the discharge port, and a dry sludge separated by the dust collector A sludge drying system comprising a dry sludge storage means for storing and a gas cleaning device for purifying hot air from which dry sludge has been separated by the dust collector, and preferably the diameter of the pellets is The sludge drying system in the range of 6.0 to 10.0 mm, the sludge drying system in which the surface of the pellet is a non-adhesive material, and the inner wall surfaces of the hollow chamber and the upper hollow chamber It is the said sludge drying system which used non-adhesive material.

また、前記の熱風発生装置からの風量が変更可能であるか、前記の集塵装置で乾燥汚泥を分離された熱風を前記の熱風供給路に戻す熱風戻し経路を備えたものであるか、前記の熱風戻し経路と前記の熱風供給路との中間に脱臭装置を備えたものであるか、前記の乾燥汚泥貯留手段に貯留された乾燥汚泥を前記の汚泥供給路に戻す乾燥汚泥戻し経路を備えたものであるか、前記の汚泥供給路の上流に、汚泥を脱水する脱水手段と、脱水した汚泥を貯留する脱水汚泥貯留手段、ならびに貯留した汚泥を前記汚泥供給路に向けて移送する移送手段とからなる汚泥前処理装置を設けた前記の汚泥乾燥システムであり、さらに前記の汚泥前処理装置に、前記脱水手段により脱水された汚泥を破砕する破砕手段を備えた前記の汚泥乾燥システムである。   In addition, whether the air volume from the hot air generating device can be changed, or whether there is a hot air return path for returning the hot air separated dry sludge by the dust collector to the hot air supply path, A deodorizing device is provided between the hot air return path and the hot air supply path, or a dry sludge return path for returning the dried sludge stored in the dry sludge storage means to the sludge supply path. Or dewatering means for dewatering sludge upstream of the sludge supply path, dewatered sludge storage means for storing the dewatered sludge, and transfer means for transferring the stored sludge toward the sludge supply path. The sludge drying system provided with the sludge pretreatment device comprising: and the sludge drying system further comprising a crushing means for crushing the sludge dehydrated by the dewatering means in the sludge pretreatment device. .

本発明によれば、汚泥のさまざまな含水率、比重などの相違に対応して的確な乾燥を行うことができるとともに、熱風を循環使用することにより熱効率がよく、集塵や脱臭を徹底して環境への2次汚染などの問題のない汚泥乾燥システムが実現し、焼却、埋め立て等の最終処分のために運搬しなければならない汚泥の量が大幅に減少して産廃処分費が減少するという、優れた効果を奏する。例えばこれまで含水率85%の汚泥をトラック6台で埋め立て地まで輸送していたとすれば、本発明によれば含水率が10%以下となり、トラックは1台ですむ。また含水率が低下することで腐敗が防止され、汚泥の長期間の貯留が可能となるとともに悪臭の発生防止にも効果的である。   According to the present invention, it is possible to perform accurate drying in response to various differences in moisture content, specific gravity, etc. of sludge, and heat efficiency is improved by circulating hot air, and thorough dust collection and deodorization are performed. A sludge drying system without problems such as secondary pollution to the environment will be realized, and the amount of sludge that must be transported for final disposal such as incineration and landfill will be greatly reduced, and industrial waste disposal costs will be reduced. Excellent effect. For example, if the sludge having a moisture content of 85% has been transported to the landfill site with six trucks, according to the present invention, the moisture content is 10% or less and only one truck is required. In addition, since the moisture content is reduced, the rot is prevented, the sludge can be stored for a long time, and the generation of bad odor is also effective.

本発明の実施例を図1により説明する。この図は実施例の汚泥乾燥システムの構成図で、1は汚泥を熱風で乾燥する汚泥乾燥装置、11は汚泥乾燥装置本体でその構造は図3に示した豆腐殻乾燥装置と基本的に変わりはない。12は熱風発生装置、13は熱風の脱臭装置、2は汚泥乾燥装置本体の出側、すなわち排出口116の下流に設けられ、熱風と乾燥汚泥を通過させ、飛び出そうとするペレットPを捕捉することのできるスクリーン、3は熱風と乾燥汚泥とを分離するサイクロン等の集塵装置、4は貯留槽等の乾燥汚泥貯留手段、5はベンチュリースクラバ等のガス清浄装置で、ここで汚泥が除去され、さらに脱臭、冷却されて無害になった排気は大気に放散される。必要に応じてさらに電気集塵機等の集塵手段を用いてもよい。   An embodiment of the present invention will be described with reference to FIG. This figure is a block diagram of the sludge drying system of the embodiment. 1 is a sludge drying device that dries sludge with hot air, 11 is a sludge drying device body, and its structure is basically different from the tofu shell drying device shown in FIG. There is no. 12 is a hot air generating device, 13 is a hot air deodorizing device, 2 is provided on the outlet side of the sludge drying device main body, that is, downstream of the discharge port 116, passes hot air and dry sludge, and captures the pellets P to be ejected. 3 is a dust collector such as a cyclone that separates hot air and dry sludge, 4 is a dry sludge storage means such as a storage tank, and 5 is a gas purifier such as a venturi scrubber, where sludge is removed. In addition, exhaust gas that has been deodorized and cooled and rendered harmless is dissipated into the atmosphere. You may use dust collection means, such as an electric dust collector, as needed.

集塵装置3からの排気はまだ90℃近い高温にあるため、できるだけ熱風発生装置12の出口に戻し、熱風として循環利用するのが熱効率の点で好ましい。このため集塵装置3からの高温の排気を熱風に混入するための熱風戻し経路31を設けて熱風発生装置12の出口につなぎ込み、脱臭装置13を経て熱風供給路113に接続する。集塵装置3からの排気は汚泥による臭気が含まれるためで、かつ白金等の触媒は高温で使用することが望ましいからである。したがって、この熱風戻し経路31を設けない場合は脱臭装置13も不要である。   Since the exhaust from the dust collector 3 is still at a high temperature close to 90 ° C., it is preferable from the viewpoint of thermal efficiency that it is returned to the outlet of the hot air generator 12 as much as possible and recycled as hot air. For this reason, a hot air return path 31 for mixing the hot exhaust gas from the dust collector 3 into the hot air is provided, connected to the outlet of the hot air generator 12, and connected to the hot air supply path 113 via the deodorizing device 13. This is because the exhaust from the dust collector 3 contains odor due to sludge, and it is desirable to use a catalyst such as platinum at a high temperature. Therefore, if this hot air return path 31 is not provided, the deodorizing device 13 is also unnecessary.

6は汚泥乾燥装置1に投入する汚泥を必要に応じて前処理する汚泥前処理装置で、その内容は追って説明する。31は前記の熱風戻し経路、41は乾燥汚泥貯留手段4に貯留された乾燥汚泥の一部を汚泥乾燥装置1に供給する汚泥に混入するための乾燥汚泥戻し経路である。   6 is a sludge pretreatment device that pretreats the sludge to be introduced into the sludge drying device 1 as necessary, and the contents will be described later. 31 is the hot air return path, and 41 is a dried sludge return path for mixing a part of the dried sludge stored in the dried sludge storage means 4 into the sludge supplied to the sludge drying apparatus 1.

水処理場等から受け入れた含水率の高い汚泥は、直接、あるいは必要に応じて汚泥前処理装置6を経由して汚泥乾燥装置1に供給される。図3に示した汚泥供給路114から中空室111内へ供給されることは、いうまでもない。一方の熱風は、ガスバーナ、ファン等で構成される熱風発生装置から図3に示した熱風供給路113を経由して中空室111内に供給される。汚泥の種類にもよるが、熱風温度を例えば350℃とする。温度はガスバーナの燃焼量やファンの風量によって任意に調整可能である。   Sludge having a high water content received from a water treatment plant or the like is supplied to the sludge drying device 1 directly or via the sludge pretreatment device 6 as necessary. Needless to say, the sludge supply path 114 shown in FIG. One hot air is supplied into the hollow chamber 111 from a hot air generator composed of a gas burner, a fan or the like via the hot air supply path 113 shown in FIG. Depending on the type of sludge, the hot air temperature is set to 350 ° C., for example. The temperature can be arbitrarily adjusted according to the combustion amount of the gas burner and the air volume of the fan.

汚泥乾燥装置本体11の排出口116からは熱風とともに乾燥された汚泥が排出されるが、ペレットPの一部が飛び出すこともあり得る。そこで排出口116の下流に、熱風と乾燥汚泥を通過させ、飛び出そうとするペレットPを捕捉することのできるスクリーン2を設ける。   Although the sludge dried with hot air is discharged from the discharge port 116 of the sludge drying apparatus body 11, a part of the pellet P may be ejected. Therefore, a screen 2 is provided downstream of the discharge port 116 to allow the hot air and dried sludge to pass through and capture the pellets P that are about to jump out.

中空室111内には金属、あるいは酸化珪素、窒化珪素、酸化アルミニウム(アルミナ)、ジルコニア等の金属化合物(いわゆるファインセラミックス)を主成分とする所定径の多数のペレットPが収容されている。ペレットPの径は6.0ないし10.0mmの範囲である。ファインセラミックスの嵩比重は3.2〜6.0程度であるから、ペレットPの径が6.0mm以下であると、気流に乗ってペレットPが飛び出しやすい。逆に10.0mm以上であると内部で熱風によって飛び上がらないので汚泥との衝突が起こりにくく、乾燥に効果がない。ペレットPの投入量は操業状態により任意ではあるが、目安として中空室111の内容積の3〜5%程度である。   The hollow chamber 111 accommodates a large number of pellets P having a predetermined diameter mainly composed of metal or a metal compound (so-called fine ceramics) such as silicon oxide, silicon nitride, aluminum oxide (alumina), or zirconia. The diameter of the pellet P is in the range of 6.0 to 10.0 mm. Since the bulk specific gravity of the fine ceramics is about 3.2 to 6.0, when the diameter of the pellet P is 6.0 mm or less, the pellet P is likely to jump out on the air current. On the other hand, if it is 10.0 mm or more, it will not fly up with hot air inside, so it will not easily collide with sludge and will not be effective for drying. The input amount of the pellets P is arbitrary depending on the operation state, but is approximately 3 to 5% of the internal volume of the hollow chamber 111 as a guide.

汚泥の種類によっては付着性が高く、ペレットPの表面や中空室111の内周面、上部中空室112の内壁に付着する場合がある。ペレットPの表面に汚泥が付着すれば衝突による粉砕効果が減少するし、内壁に付着した汚泥が成長すれば内部がせまくなって乾燥処理の効率が低下する。ペレットPの表面への付着を防止するにはペレットPの材質を付着しにくいものとすることが有効である。表面がざらざらしているものよりツルツルしているものの方が付着は少ないので、この点ではアルミナ系のものよりもジルコン(ZiO2-SiO2)系がよい。また内壁への付着を防止するには、摩擦係数の低い材質、例えばフッ素樹脂等でライニングすることが有効である。 Depending on the type of sludge, the adhesiveness is high and may adhere to the surface of the pellet P, the inner peripheral surface of the hollow chamber 111, and the inner wall of the upper hollow chamber 112. If sludge adheres to the surface of the pellet P, the pulverization effect due to the collision is reduced, and if the sludge attached to the inner wall grows, the inside becomes clogged and the efficiency of the drying process is reduced. In order to prevent adhesion of the pellet P to the surface, it is effective to make the material of the pellet P difficult to adhere. Since the surface that is smoother is less adhered than the surface that is rough, the zircon (ZiO 2 —SiO 2 ) system is better than the alumina system in this respect. In order to prevent adhesion to the inner wall, it is effective to line with a material having a low friction coefficient, such as a fluororesin.

汚泥乾燥装置1における処理量は、およそその内容積によって決定される。すでに製作された装置において処理量の変化に対応するには、熱風の風量を変化させればよい。したがって熱風発生装置の熱風供給経路にダンパを設け、送風機を風量制御可能なものとすることが好ましい。熱風の調整によって、付着のほか汚泥の焦げつきも防止できる。   The processing amount in the sludge drying apparatus 1 is determined approximately by its internal volume. In order to cope with a change in the processing amount in an already manufactured apparatus, the amount of hot air may be changed. Therefore, it is preferable to provide a damper in the hot air supply path of the hot air generator so that the air volume of the blower can be controlled. By adjusting the hot air, it is possible to prevent adhesion of sludge as well as adhesion.

つぎに図1における汚泥前処理装置6の一実施例を図2により説明する。61は脱水機等の脱水手段、62は脱水された汚泥を貯留する脱水汚泥貯留手段、63は貯留された脱水汚泥を切り出して汚泥乾燥装置1に向けて移送するコンベヤ、空気輸送等の移送手段である。また脱水機の種類によっては脱水ケーキが固化して塊状となり、以後の処理に支障をきたすおそれもあり、このような場合には脱水された汚泥を破砕する破砕手段64を設ける必要がある。   Next, an embodiment of the sludge pretreatment device 6 in FIG. 1 will be described with reference to FIG. 61 is a dewatering means such as a dehydrator, 62 is a dewatered sludge storage means for storing the dewatered sludge, 63 is a conveyor for cutting out the stored dewatered sludge and transferring it to the sludge drying apparatus 1, and a transport means such as pneumatic transportation It is. Further, depending on the type of dehydrator, the dehydrated cake may solidify and become a lump, which may hinder subsequent processing. In such a case, it is necessary to provide a crushing means 64 for crushing the dewatered sludge.

廃水処理場等から受け入れた含水率98%の汚泥を脱水手段61により85%程度に脱水する。容積としては受入れ汚泥を100とすればこの段階で10程度に減量されている。この汚泥をさらに汚泥乾燥装置で乾燥することにより含水率10%、容積で2程度に減量できる。   The sludge with a moisture content of 98% received from a wastewater treatment plant is dehydrated to about 85% by the dehydration means 61. The volume is reduced to about 10 at this stage if the receiving sludge is 100. By further drying this sludge with a sludge dryer, the water content can be reduced to about 2% by volume.

安定した乾燥処理を行うため、汚泥乾燥装置1に投入する汚泥の含水率を80〜90%の範囲とすることが好ましいので、含水率がこの範囲より高い場合は上記の汚泥前処理装置6を通過させ、その必要のない場合は直接投入する。あるいは図1に示した乾燥汚泥戻し経路41を使用して乾燥汚泥貯留手段4に貯留されている乾燥汚泥を受入れ汚泥に混入することにより含水率を調整することもできる。   In order to perform a stable drying treatment, it is preferable that the moisture content of the sludge to be introduced into the sludge drying device 1 is in the range of 80 to 90%. If the moisture content is higher than this range, the sludge pretreatment device 6 is used. If it is not necessary, pass it directly. Alternatively, the moisture content can be adjusted by receiving the dried sludge stored in the dried sludge storage means 4 and mixing it into the sludge using the dried sludge return path 41 shown in FIG.

本発明の汚泥乾燥システムは、内部への付着や焦げつきを起こすことなく効率よく乾燥を行うことができるので、汚泥の他、豆腐殻はもとより食品や酒類の搾りかす、調理後の食材残渣等さまざまなものの乾燥を行うことができる。   The sludge drying system of the present invention can efficiently dry without causing internal adhesion or scorching. Therefore, in addition to sludge, various types of food residues such as tofu husks, foods and alcoholic beverages, and cooking residue Can be dried.

本発明の実施例の汚泥乾燥システムの構成図である。It is a block diagram of the sludge drying system of the Example of this invention. 図1における汚泥前処理装置の実施例の構成図である。FIG. 2 is a configuration diagram of an embodiment of the sludge pretreatment device in FIG. 従来の技術における豆腐殻乾燥装置の断面図である。It is sectional drawing of the tofu shell drying apparatus in a prior art.

符号の説明Explanation of symbols

1 汚泥乾燥装置
2 スクリーン
3 集塵装置
4 乾燥汚泥貯留手段
5 ガス清浄装置
6 汚泥前処理装置
11 汚泥乾燥装置本体(豆腐殻乾燥装置)
12 熱風発生装置
13 脱臭装置
31 熱風戻し経路
41 乾燥汚泥戻し経路
61 脱水手段
62 脱水汚泥貯留手段
63 移送手段
64 破砕手段
111 中空室
112 上部中空室
113 熱風供給路
114 汚泥供給路(豆腐殻供給路)
115 フィーダ
116 排出口
P ペレット
DESCRIPTION OF SYMBOLS 1 Sludge drying apparatus 2 Screen 3 Dust collector 4 Dried sludge storage means 5 Gas cleaning apparatus 6 Sludge pretreatment apparatus
11 Sludge dryer body (tofu shell dryer)
12 Hot air generator
13 Deodorizer
31 Hot air return path
41 Dry sludge return route
61 Dehydration means
62 Dewatered sludge storage means
63 Transportation means
64 Crushing means
111 Hollow chamber
112 Upper hollow chamber
113 Hot air supply path
114 Sludge supply channel (tofu shell supply channel)
115 feeder
116 Discharge port P Pellet

Claims (10)

金属または金属化合物を主成分とする所定径の多数のペレット(P)を収容し、横向きに設置された円筒形の中空室(111)と、この中空室(111)の上方に配置され、下端がこの中空室(111)に連通する箱状の上部中空室(112)と、前記中空室(111)の底部付近において先端をこの中空室(111)の外周面に開口し、この中空室(111)の接線方向に配置され、熱風をこの中空室(111)内に供給するための熱風供給路(113)と、前記上部中空室(112)と前記熱風供給路(113)との間において先端を前記中空室(111)の外周面に開口し、直立して前記中空室(111)の接線方向に配置され、汚泥を前記中空室(111)内に供給するための汚泥供給路(114)と、前記上部中空室(112)の上端付近に設けられ、上部中空室(112)内の内容物が熱風とともに排出される排出口(116)とからなる汚泥乾燥装置本体(11)に、前記熱風供給路(113)に熱風を供給する熱風発生装置(12)を付設してなる汚泥乾燥装置(1)と、
前記排出口(116)から排出されるペレット(P)を捕捉して上部中空室(112)内に戻すスクリーン(2)と、前記排出口(116)から排出される熱風から乾燥汚泥を分離する集塵装置(3)と、この集塵装置(3)で分離された乾燥汚泥を貯留する乾燥汚泥貯留手段(4)と、この集塵装置(3)で乾燥汚泥を分離された熱風を清浄化するガス清浄装置(5)と
で構成したことを特徴とする汚泥乾燥システム。
A cylindrical hollow chamber (111) containing a large number of pellets (P) having a predetermined diameter mainly composed of a metal or a metal compound and disposed horizontally, and disposed above the hollow chamber (111), has a lower end. Has a box-shaped upper hollow chamber (112) that communicates with the hollow chamber (111), and a tip that opens to the outer peripheral surface of the hollow chamber (111) in the vicinity of the bottom of the hollow chamber (111). 111) is arranged in the tangential direction of the hot air supply passage (113) for supplying hot air into the hollow chamber (111), and between the upper hollow chamber (112) and the hot air supply passage (113). A sludge supply path (114) for opening the tip to the outer peripheral surface of the hollow chamber (111), standing upright and being arranged in the tangential direction of the hollow chamber (111), and supplying sludge into the hollow chamber (111) ) And the upper hollow chamber (112) near the upper end, and the contents in the upper hollow chamber (112) are discharged together with hot air. The sludge drying apparatus body consisting outlet and (116) (11) which, sludge drying device formed by attaching a hot-air generator (12) for supplying hot air to the hot air supply path (113) and (1),
The dried sludge is separated from the screen (2) that captures the pellet (P) discharged from the discharge port (116) and returns it to the upper hollow chamber (112), and the hot air discharged from the discharge port (116). Clean the dust collector (3), the dry sludge storage means (4) for storing the dried sludge separated by the dust collector (3), and the hot air from which the dried sludge is separated by the dust collector (3) The sludge drying system characterized by comprising with the gas purifier (5) which changes.
前記のペレット(P)の径が6.0ないし10.0mmの範囲である請求項1に記載の汚泥乾燥システム。   The sludge drying system according to claim 1, wherein the diameter of the pellet (P) is in the range of 6.0 to 10.0 mm. 前記のペレット(P)の表面を非付着性の材質とした請求項1または2に記載の汚泥乾燥システム。   The sludge drying system according to claim 1 or 2, wherein the surface of the pellet (P) is a non-adhesive material. 前記の中空室(111)および上部中空室(112)の内壁面を非付着性の材質とした請求項1ないし3のいずれかに記載の汚泥乾燥システム。   The sludge drying system according to any one of claims 1 to 3, wherein the inner wall surfaces of the hollow chamber (111) and the upper hollow chamber (112) are made of a non-adhesive material. 前記の熱風発生装置(12)からの風量が変更可能である請求項1ないし4のいずれかに記載の汚泥乾燥システム。   The sludge drying system according to any one of claims 1 to 4, wherein the amount of air from the hot air generator (12) is changeable. 前記の集塵装置(3)で乾燥汚泥を分離された熱風を前記の熱風供給路(113)に戻す熱風戻し経路(31)を備えた請求項1ないし5のいずれかに記載の汚泥乾燥システム。   The sludge drying system according to any one of claims 1 to 5, further comprising a hot air return path (31) for returning the hot air separated from the dried sludge by the dust collector (3) to the hot air supply path (113). . 前記の熱風戻し経路(31)と前記の熱風供給路(113)との中間に脱臭装置(13)を備えた請求項6に記載の汚泥乾燥システム。   The sludge drying system according to claim 6, further comprising a deodorizing device (13) between the hot air return path (31) and the hot air supply path (113). 前記の乾燥汚泥貯留手段(4)に貯留された乾燥汚泥を前記の汚泥供給路(114)に戻す乾燥汚泥戻し経路(41)を備えた請求項1ないし7のいずれかに記載の汚泥乾燥システム。   The sludge drying system according to any one of claims 1 to 7, further comprising a dried sludge return path (41) for returning the dried sludge stored in the dried sludge storage means (4) to the sludge supply path (114). . 前記の汚泥供給路(114)の上流に、汚泥を脱水する脱水手段(61)と、脱水した汚泥を貯留する脱水汚泥貯留手段(62)、ならびに貯留した汚泥を前記汚泥供給路(114)に向けて移送する移送手段(63)とからなる汚泥前処理装置(6)を設けた請求項1ないし8のいずれかに記載の汚泥乾燥システム。   Upstream of the sludge supply path (114), a dewatering means (61) for dewatering sludge, a dewatered sludge storage means (62) for storing the dewatered sludge, and the stored sludge to the sludge supply path (114). The sludge drying system according to any one of claims 1 to 8, further comprising a sludge pretreatment device (6) comprising a transfer means (63) for transferring the sludge. 前記の汚泥前処理装置(6)に、前記脱水手段(61)により脱水された汚泥を破砕する破砕手段(64)を備えた請求項9に記載の汚泥乾燥システム。   The sludge drying system according to claim 9, further comprising a crushing means (64) for crushing the sludge dehydrated by the dewatering means (61) in the sludge pretreatment device (6).
JP2004045276A 2004-02-20 2004-02-20 Sludge drying system Expired - Fee Related JP3751307B2 (en)

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