JP5020202B2 - Incineration ash washing equipment - Google Patents

Incineration ash washing equipment Download PDF

Info

Publication number
JP5020202B2
JP5020202B2 JP2008231750A JP2008231750A JP5020202B2 JP 5020202 B2 JP5020202 B2 JP 5020202B2 JP 2008231750 A JP2008231750 A JP 2008231750A JP 2008231750 A JP2008231750 A JP 2008231750A JP 5020202 B2 JP5020202 B2 JP 5020202B2
Authority
JP
Japan
Prior art keywords
ash
water
washing
incineration ash
incineration
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.)
Active
Application number
JP2008231750A
Other languages
Japanese (ja)
Other versions
JP2010082487A (en
Inventor
範明 仙波
晋太郎 阿部
利昌 白井
実 倉西
範雄 吉光
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Mitsubishi Heavy Industries Environmental and Chemical Engineering Co Ltd
Original Assignee
Mitsubishi Heavy Industries Environmental and Chemical Engineering Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Mitsubishi Heavy Industries Environmental and Chemical Engineering Co Ltd filed Critical Mitsubishi Heavy Industries Environmental and Chemical Engineering Co Ltd
Priority to JP2008231750A priority Critical patent/JP5020202B2/en
Publication of JP2010082487A publication Critical patent/JP2010082487A/en
Application granted granted Critical
Publication of JP5020202B2 publication Critical patent/JP5020202B2/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Description

本発明は、焼却灰を水洗処理して塩素分を除去する焼却灰の水洗処理方法及びシステムに関し、特に、水洗処理を行う洗浄槽内での焼却灰と水との撹拌混合性を高め、塩素除去効率を向上させることを可能とした焼却灰の水洗処理装置に関する。 The present invention relates to an incineration ash water washing method and system for removing chlorine by washing the incineration ash, and in particular, improving the stirring and mixing properties of the incineration ash and water in the washing tank in which the water washing treatment is performed. The present invention relates to an incineration ash washing apparatus capable of improving removal efficiency.

従来より、都市ごみや下水汚泥等の一般廃棄物又は各種工場から排出される産業廃棄物は、減容化及び無害化のために焼却により処理されている。一般に、焼却炉から排出される焼却灰の処理方法としては、埋め立て処理、溶融スラグ化、建築資材への再資源化などが挙げられる。特に近年では、これらの灰をセメント原料、人工骨材、植栽用土、路床材、路盤材、焼成タイルなどの製品に加工して有効利用することが求められている。しかし、焼却灰を再資源化するに際して、焼却灰には塩素分が含まれているため、灰の用途に応じて、塩素濃度を基準値以下まで低減する必要がある。   Conventionally, general waste such as municipal waste and sewage sludge or industrial waste discharged from various factories has been treated by incineration for volume reduction and detoxification. In general, methods for treating incineration ash discharged from an incinerator include landfill treatment, melting slag, recycling to building materials, and the like. Particularly in recent years, it has been demanded that these ashes be processed into products such as cement raw materials, artificial aggregates, planting soil, roadbed materials, roadbed materials, fired tiles, and the like to be effectively used. However, when recycling incineration ash, since the incineration ash contains chlorine, it is necessary to reduce the chlorine concentration below the reference value depending on the use of the ash.

一般的な焼却灰の処理方法としては、金属片等の異物を除去した後、焼却灰を水洗することにより塩素分を低減する方法が用いられている。しかしながら、大部分の塩素分は水洗で除去可能であるが、高品質の再資源化原料として付加価値を与えるためには、単に水洗するのみでは塩素低減は不十分であった。そこで、水洗にて洗浄水のpHを酸性若しくは6〜10に調整したり、粉砕したり、或いは洗浄回数を複数回に増加することにより対応している。   As a general method for treating incineration ash, a method of reducing the chlorine content by removing foreign matters such as metal pieces and then washing the incineration ash with water is used. However, most of the chlorine content can be removed by washing with water, but in order to give added value as a high-quality recycling material, simply washing with water was insufficient in reducing chlorine. Therefore, this is dealt with by adjusting the pH of the washing water to acidic or 6 to 10 by water washing, pulverizing, or increasing the number of washings to a plurality of times.

例えば、特許文献1(特許第3368372号公報)には、焼却灰を粉砕した後、複数回洗浄を行うようにした焼却灰のセメント原料化方法が開示されている。このとき、洗浄時の液pHが6〜10、好適にはpH8〜10となるようにし、これにより焼却灰の重金属の溶出を抑制しつつ塩素分を溶解除去するようにしている。
特許文献2(特開2005−288328号公報)には、複数設置した洗浄槽で焼却灰を洗浄し、さらに洗浄槽に二酸化炭素ガスを導入して洗浄するとともに、洗浄槽が具備する循環配管路に設けられた湿式破砕機により焼却灰を破砕するようにした構成が開示されている。
For example, Patent Document 1 (Japanese Patent No. 3368372) discloses a method for converting incineration ash into a cement raw material in which incineration ash is pulverized and then washed multiple times. At this time, the pH of the solution at the time of washing is adjusted to 6 to 10, preferably 8 to 10, whereby the chlorine content is dissolved and removed while suppressing the elution of heavy metals in the incinerated ash.
In Patent Document 2 (Japanese Patent Laid-Open No. 2005-288328), incineration ash is washed in a plurality of installed washing tanks, and further, carbon dioxide gas is introduced into the washing tank for washing, and a circulation pipe line provided in the washing tank A configuration in which the incinerated ash is crushed by a wet crusher provided in the above is disclosed.

また、水洗処理は、水を貯留した洗浄槽内に焼却灰を供給し、水と焼却灰を混合して焼却灰に含有される塩素分を水に溶出させるが、撹拌混合性が不十分だと焼却灰が水と十分に接触せず、塩素除去効率が低下してしまう。そこで、特許文献3(特開2002−254041号公報)には、撹拌翼を回転させることにより混合する手段、ジェットポンプにより水を循環させる手段により撹拌力を向上させる方法が開示されている。   In addition, in the washing process, incineration ash is supplied into the washing tank in which water is stored, and water and incineration ash are mixed to elute the chlorine contained in the incineration ash into water, but the stirring and mixing properties are insufficient. And the incineration ash is not in sufficient contact with water, and the chlorine removal efficiency is reduced. Therefore, Patent Document 3 (Japanese Patent Laid-Open No. 2002-254041) discloses a method for improving the stirring force by means for mixing by rotating a stirring blade and means for circulating water by a jet pump.

特許第3368372号公報Japanese Patent No. 3368372 特開2005−288328号公報JP 2005-288328 A 特開2002−254041号公報JP 2002-254041 A

上記したように、焼却灰中の塩素分を除去する際には水洗処理が一般に多く用いられており、焼却灰に含まれる大部分の塩素分は水洗で除去可能であるが、水洗処理のみでは不十分であったため、特許文献1、2に記載されるように、洗浄槽にてpH調整をしたり、粉砕したり、洗浄回数を複数回に増加するなどして対応していた。   As mentioned above, when removing chlorine from the incineration ash, a water washing process is generally used, and most of the chlorine contained in the incineration ash can be removed by water washing. Since it was insufficient, as described in Patent Documents 1 and 2, the pH was adjusted in the washing tank, pulverized, or the number of washings was increased to a plurality of times.

しかしながら、このような対策を講じても、水と焼却灰との接触が不十分であると塩素分が水に溶出することを妨げ、塩素除去率を高く維持することは困難である。そこで、特許文献3等に記載されるように、洗浄槽内にプロペラ型の撹拌翼を挿入して撹拌することが一般に広く用いられているが、焼却灰は比重が大きいため十分な混合が難しく、また撹拌動力の増大、若しくは装置が大きくなるなどの欠点がある。また、特許文献3に記載されるように、ジェットポンプによる撹拌混合も提案されているが、焼却灰が混合した水を単にポンプで循環させることは、ポンプ及び循環系統の配管の磨耗が問題となる。   However, even if such measures are taken, if the contact between water and incineration ash is insufficient, it is difficult to keep the chlorine removal rate high by preventing the chlorine component from eluting into the water. Therefore, as described in Patent Document 3 and the like, it is generally widely used to stir by inserting a propeller-type stirring blade in the washing tank, but incineration ash has a large specific gravity and is difficult to sufficiently mix. In addition, there are disadvantages such as an increase in stirring power or a larger apparatus. In addition, as described in Patent Document 3, stirring and mixing by a jet pump has also been proposed. However, simply circulating water mixed with incineration ash with a pump is a problem of wear of the pump and piping of the circulation system. Become.

従って、本発明は上記従来技術の問題点に鑑み、洗浄槽内での焼却灰と水の撹拌混合性を高め、塩素除去効率を向上させることができる焼却灰の水洗処理装置を提供することを目的とする。 Therefore, in view of the above-mentioned problems of the prior art, the present invention provides an incinerated ash washing apparatus that can improve the mixing and mixing of incinerated ash and water in the washing tank and improve the chlorine removal efficiency. Objective.

そこで、本発明は係る課題を解決するために、
却灰が供給される洗浄槽と、該洗浄槽内にて水に浸漬された焼却灰を撹拌する撹拌手段とを備える焼却灰の水洗処理装置において、
前記撹拌手段が、前記焼却灰を洗浄槽内上方に持ち上げる機械的手段であり、該機械的手段により持ち上げた焼却灰を重力沈降させて、該焼却灰を少なくとも鉛直方向に撹拌し、
前記機械的手段が、前記洗浄槽底部に堆積した焼却灰をすくい上げて洗浄槽内上方に搬送する灰搬送部と、前記灰搬送部が所定間隔で複数取り付けられ、水洗処理した後の前記焼却灰を排出する灰排出コンベアとしての無端環状ガイドと、を備え、
前記無端環状ガイドは、前記灰搬送部の灰載置面が上方に向いた状態で該灰搬送部を上方に移動させ、所定位置で前記灰搬送部を反転させて、該灰搬送部上の焼却灰を落下させるように形成され、
前記無端環状ガイドは、前記焼却灰の排出時には正回転に駆動されて前記灰搬送部の裏面で前記焼却灰を押し出し排出し、前記焼却灰の水洗時には逆回転に駆動されて前記灰搬送部の灰載置面で前記焼却灰を持ち上げ、該焼却灰を撹拌することを特徴とする。
Then, in order to solve the problem which this invention relates,
A cleaning tank baked却灰is supplied, the washing processing apparatus ash and a stirring means for stirring the soaked ash in water at the washing tank,
The stirring means is a mechanical means for lifting the incineration ash upward in the washing tank, and the incineration ash lifted by the mechanical means is gravity settled to stir the incineration ash at least in the vertical direction ,
The incinerated ash after the mechanical means scoops up the incinerated ash deposited on the bottom of the washing tank and conveys the incineration ash upward in the washing tank, and a plurality of the ash conveying parts are attached at predetermined intervals and washed with water. An endless annular guide as an ash discharge conveyor for discharging
The endless annular guide moves the ash transport unit upward with the ash placement surface of the ash transport unit facing upward, and inverts the ash transport unit at a predetermined position, Formed to drop incineration ash,
The endless annular guide is driven to rotate forward at the time of discharging the incinerated ash to push out the incinerated ash at the back surface of the ash transport unit, and is driven to rotate in the reverse direction at the time of washing the incinerated ash to wash the ash transport unit. The incineration ash is lifted by an ash mounting surface, and the incineration ash is stirred .

構成によれば、灰排出コンベアが灰撹拌用コンベア(無端環状ガイド)の機能を兼ね備えることにより、装置の高効率化、小型化が可能となる。 According to this configuration, by crawling Deco conveyors is combine the functions of the ash stirred conveyor (endless annular guide), it is possible to high efficiency, miniaturization of the apparatus.

さらに、前記灰搬送部は、前記焼却灰を載置する平板と、該平板の灰載置面側にツメが具備されたバケット状に形成されてなることを特徴とする。このように、灰搬送部をバケット状に形成することにより、焼却灰の取り込みを容易にし、また載置した焼却灰を取りこぼすことなく確実に上方に搬送することが可能となる。
さらにまた、前記洗浄槽内の死水域に空気又は水を噴出して水流を形成する灰詰まり防止手段を備えることを特徴とする。これにより、焼却灰が死水域に滞留することを防止し、焼却灰の水洗処理を効率的に行うことが可能となる。
Further, the ash transport unit is formed in a bucket shape in which the incinerated ash is placed, and a claw is provided on the ash placement surface side of the flat plate. In this way, by forming the ash transport portion in a bucket shape, it is possible to easily capture the incineration ash, and it is possible to reliably transport the incineration ash placed on the upper side without dropping it.
Still further, the present invention is characterized by comprising ash clogging preventing means for jetting air or water into a dead water area in the washing tank to form a water flow. Thereby, it is possible to prevent the incinerated ash from staying in the dead water area, and to efficiently perform the washing treatment of the incinerated ash.

以上記載のごとく本発明によれば、焼却灰を鉛直方向に撹拌する機械的手段を備えることにより、撹拌混合性を高めることができ、焼却灰と水の接触を多くすることにより塩素除去率を大幅に向上させ、処理時間を短縮化することが可能となる。よって、水洗処理により塩素濃度の低い焼却灰を得ることができ、焼却灰をセメント原料等の再資源化原料として好適に用いることが可能となる。
また、機械的手段により焼却灰をすくい上げて洗浄槽内上方に持ち上げた後、重力により沈降させるようにし、焼却灰を鉛直方向に撹拌することにより、比重が大きい焼却灰であっても、撹拌混合性を高めることができ、焼却灰が水と十分に接触するため塩素除去率が向上するとともに、処理時間の短縮化が可能となる。さらに、焼却灰を強制的にすくい上げて洗浄槽内上方に持ち上げているため、確実に且つ十分に鉛直方向の撹拌を行うことができる。
As described above, according to the present invention, by providing mechanical means for stirring the incinerated ash in the vertical direction, it is possible to improve the stirring and mixing properties, and by increasing the contact between the incinerated ash and water, the chlorine removal rate can be increased. This greatly improves the processing time. Therefore, incineration ash having a low chlorine concentration can be obtained by washing with water, and the incineration ash can be suitably used as a recycled material such as a cement material.
In addition, the incineration ash is scooped up by mechanical means, lifted upward in the washing tank, and then settled by gravity. By stirring the incineration ash in the vertical direction, even if the incineration ash has a large specific gravity, it is stirred and mixed. The incineration ash is in sufficient contact with water, so that the chlorine removal rate is improved and the processing time can be shortened. Furthermore, since the incineration ash is forcibly picked up and lifted upward in the cleaning tank, the vertical agitation can be reliably and sufficiently performed.

らに、灰排出コンベアが灰撹拌用コンベアの機能を兼ね備えるように構成することにより、装置の高効率化、小型化が可能となる。 Et al is, by crawling Deco conveyer is configured to combine the functions of the conveyor stirring ash, it becomes possible to high efficiency, miniaturization of the apparatus.

以下、図面を参照して本発明の好適な実施例を例示的に詳しく説明する。但しこの実施例に記載されている構成部品の寸法、材質、形状、その相対的配置等は特に特定的な記載がない限りは、この発明の範囲をそれに限定する趣旨ではなく、単なる説明例に過ぎない。
図1〜図3は本発明の実施例1〜実施例3に係る水洗処理装置の概略側面図を夫々示し、図4は図3に示した水洗処理装置のX−X断面図、図5は図3に示した水洗処理装置が備えるバケットスクレーパの側面図、図6は本発明の実施形態が適用される焼却灰処理システムの一例を示すブロック図である。
Hereinafter, exemplary embodiments of the present invention will be described in detail with reference to the drawings. However, the dimensions, materials, shapes, relative arrangements, and the like of the components described in this embodiment are not intended to limit the scope of the present invention unless otherwise specified, but are merely illustrative examples. Not too much.
1 to 3 show schematic side views of the water washing apparatus according to Embodiments 1 to 3 of the present invention, respectively. FIG. 4 is a sectional view taken along line XX of the water washing apparatus shown in FIG. The side view of the bucket scraper with which the water-washing processing apparatus shown in FIG. 3 is provided, FIG. 6 is a block diagram which shows an example of the incineration ash processing system with which embodiment of this invention is applied.

本実施形態に係る焼却灰の水洗処理装置は、水が貯留された洗浄槽を備え、該洗浄槽内に供給された焼却灰を上方に持ち上げる機械的手段が設けられている。洗浄槽内の焼却灰は、前記機械的手段により洗浄槽内上方まで持ち上げられた後、重力により落下沈降し、これを繰り返すことにより鉛直方向に撹拌される。
焼却灰は比重が大きく、水平方向のみの撹拌では十分な撹拌混合性が得られないため、本実施形態のように鉛直方向に撹拌する機械的手段を備えることにより、撹拌混合性を高めることができ、焼却灰と水の接触を多くすることにより塩素除去率を大幅に向上させ、処理時間を短縮化することが可能となる。よって、水洗処理により塩素濃度の低い焼却灰を得ることができ、焼却灰をセメント原料等の再資源化原料として好適に用いることが可能となる。
The incineration ash washing apparatus according to the present embodiment includes a washing tank in which water is stored, and mechanical means for lifting the incineration ash supplied into the washing tank upward is provided. The incinerated ash in the washing tank is lifted up to the upper part in the washing tank by the mechanical means, then falls and settles by gravity, and is stirred in the vertical direction by repeating this.
Incinerated ash has a large specific gravity, and sufficient stirring and mixing properties cannot be obtained by stirring only in the horizontal direction.Thus, by providing mechanical means for stirring in the vertical direction as in this embodiment, the stirring and mixing properties can be improved. In addition, by increasing the contact of the incinerated ash with water, the chlorine removal rate can be greatly improved and the processing time can be shortened. Therefore, incineration ash having a low chlorine concentration can be obtained by washing with water, and the incineration ash can be suitably used as a recycled material such as a cement material.

本実施形態が適用される焼却灰処理システムの一例を図6に示す。尚、水洗設備100の構成は、図1に示した構成に限定されるものではない。
この焼却灰処理システムは、焼却炉から排出された焼却灰1が投入される比重差分離装置51と、該比重差分離装置51にて金属片等の異物が除去された焼却灰が供給される水洗処理設備と、を備える。
前記比重差分離装置51は、分離液を介して、比重の大きい金属片や大径焼却灰等の異物と、比重の小さい焼却灰とを分離する周知の装置である。
前記水洗処理設備は、前段側水洗処理設備と後段側水洗処理設備が直列に配設された2構成となっており、夫々洗浄槽52、54、固液分離装置53、55を備える。本実施形態の洗浄槽は、洗浄槽52又は洗浄槽54の何れか一方、又は両方に適用できる。前段側水洗処理設備では焼却灰の10〜40倍量、後段側水洗処理設備では焼却灰の5〜20倍量の水で洗浄する。
An example of the incineration ash treatment system to which this embodiment is applied is shown in FIG. In addition, the structure of the water-washing equipment 100 is not limited to the structure shown in FIG.
This incineration ash treatment system is supplied with a specific gravity difference separation device 51 into which the incineration ash 1 discharged from the incinerator is charged, and incineration ash from which foreign matters such as metal pieces have been removed by the specific gravity difference separation device 51. Water washing treatment equipment.
The specific gravity difference separation device 51 is a well-known device for separating foreign matter such as metal pieces having a large specific gravity or large-diameter incineration ash and incineration ash having a low specific gravity through a separating liquid.
The water-washing treatment equipment has two configurations in which a front-side water-washing treatment equipment and a rear-stage-side water washing treatment equipment are arranged in series, and includes washing tanks 52 and 54 and solid-liquid separators 53 and 55, respectively. The cleaning tank of this embodiment can be applied to either the cleaning tank 52 or the cleaning tank 54, or both. The front-stage flushing equipment is washed with 10 to 40 times the amount of incinerated ash, and the rear-stage flushing equipment is washed with 5 to 20 times the amount of incinerated ash.

前段側水洗処理設備において、洗浄槽52には、水3と、硫酸タンク56から供給される硫酸とからなる洗浄水が貯留されており、該洗浄槽52内に、比重差分離装置51にて異物が除去された焼却灰が供給される。洗浄槽52は、焼却灰1を鉛直方向に撹拌する機械的手段を備えている。この機械的手段を備えた洗浄槽52の構成については、実施例1〜実施例3にて後述する。尚、本構成ではpH調整に用いる酸として硫酸を例に挙げて示したが、これに限定されるものではなく、他の酸であってもよい。
洗浄槽52には、焼却灰の水洗時に洗浄水のpH値を測定するpH計63が設置されており、該洗浄水のpHを逐次監視している。pH調整は、バルブ61を制御して硫酸タンク56からの硫酸供給量を調整することにより行われる。硫酸は、焼却灰1tに対して10kgから100kg添加され、pHは10〜11に調整される。
後段側水洗処理設備は、前記前段側水洗処理設備と同様の構成を備える。
In the pre-stage water washing treatment facility, washing water comprising water 3 and sulfuric acid supplied from the sulfuric acid tank 56 is stored in the washing tank 52, and the specific gravity difference separation device 51 contains the washing water in the washing tank 52. Incineration ash from which foreign matter has been removed is supplied. The washing tank 52 includes mechanical means for stirring the incineration ash 1 in the vertical direction. The configuration of the cleaning tank 52 provided with this mechanical means will be described later in Examples 1 to 3. In this configuration, sulfuric acid is shown as an example of the acid used for pH adjustment. However, the acid is not limited to this, and other acids may be used.
The washing tank 52 is provided with a pH meter 63 for measuring the pH value of the washing water when the incinerated ash is washed, and sequentially monitors the pH of the washing water. The pH adjustment is performed by controlling the valve 61 to adjust the amount of sulfuric acid supplied from the sulfuric acid tank 56. Sulfuric acid is added from 10 kg to 100 kg with respect to 1 ton of incinerated ash, and the pH is adjusted to 10-11.
The latter-stage water washing treatment facility has the same configuration as the preceding-stage water washing treatment facility.

本構成において、前段側の洗浄槽52では、焼却灰を粗洗浄することにより塩素濃度を大幅に低下させ、後段側の洗浄槽54では、仕上げ洗浄することにより塩素濃度を極めて低濃度となるまで洗浄するようになっている。
前段側水洗処理設備の洗浄槽52にて水洗された後の焼却灰を含む処理水は、固液分離装置53に導入され、該固液分離装置53にて焼却灰4と排水5とに分離される。焼却灰4は、後段側水洗処理設備の洗浄槽54に供給され、該洗浄槽54にて水洗された後、固液分離装置55にて処理灰7と排水8とに分離される。
In this configuration, in the cleaning tank 52 on the front stage, the chlorine concentration is greatly reduced by roughly cleaning the incineration ash, and in the cleaning tank 54 on the rear stage, the chlorine concentration is reduced to a very low concentration by finishing cleaning. It is designed to be washed.
The treated water containing the incinerated ash after being washed in the washing tank 52 of the front-side water washing treatment facility is introduced into the solid-liquid separator 53, and separated into the incinerated ash 4 and the waste water 5 by the solid-liquid separator 53. Is done. The incinerated ash 4 is supplied to the washing tank 54 of the subsequent-stage water washing treatment facility, washed with water in the washing tank 54, and then separated into the treated ash 7 and the waste water 8 by the solid-liquid separator 55.

また、本構成では、排水発生量を低減するために以下の構成を備えることが好ましい。
前段側水洗処理設備の固液分離装置53にて分離された排水5を系外へ排出する排出ラインと、該排水5を洗浄槽52に返送する循環ラインとを備え、排出ライン上にはバルブ62が設置されている。また、排水5の電導度を測定する電導度計64を備えており、該電導度計64の測定値に基づいてバルブ62を制御し、洗浄槽52への循環量を制御するようになっている。即ち、水洗初期は排水5を循環して洗浄に用い、排水5中の不純物濃度、好適には塩素濃度が所定濃度以上となったらバルブ62を開放して系外へ排水6を排出するようにしている。排水6を系外に排出したときは、水3のバルブ60を制御して、新たに水3を補給する。
Moreover, in this structure, in order to reduce wastewater generation amount, it is preferable to provide the following structures.
A discharge line for discharging the waste water 5 separated by the solid-liquid separation device 53 of the front-side water washing treatment facility to the outside of the system and a circulation line for returning the waste water 5 to the cleaning tank 52 are provided, and a valve is provided on the discharge line. 62 is installed. In addition, a conductivity meter 64 for measuring the conductivity of the drainage 5 is provided, and the valve 62 is controlled based on the measured value of the conductivity meter 64 to control the circulation amount to the cleaning tank 52. Yes. That is, in the initial stage of water washing, the waste water 5 is circulated and used for washing. When the impurity concentration in the waste water 5, preferably the chlorine concentration, exceeds a predetermined concentration, the valve 62 is opened to discharge the waste water 6 outside the system. ing. When the waste water 6 is discharged out of the system, the water 3 valve 60 is controlled to replenish water 3.

同様に、後段側水洗処理設備においても、固液分離装置55にて分離された排水8を系外へ排出する排出ラインと、該排水8を洗浄槽54に返送する循環ラインとを備え、排出ライン上にはバルブ67が設置されている。また、排水8の電導度を測定する電導度計69を備えており、該電導度計69の測定値に基づいてバルブ67を制御し、洗浄槽54への循環量を制御するようになっている。即ち、水洗初期は排水8を循環して洗浄に用い、排水8中の不純物濃度が高くなったら系外へ排水9を排出する。排水9を系外に排出したときは、水3のバルブ65を制御して、新たに水3を補給する。このように、直列に2段配置された水洗処理設備にて、個々に排水を循環使用する構成とすることにより、排水発生量を低減することが可能である。   Similarly, the rear-side water washing treatment facility is also provided with a discharge line for discharging the waste water 8 separated by the solid-liquid separator 55 to the outside of the system, and a circulation line for returning the waste water 8 to the cleaning tank 54. A valve 67 is installed on the line. Further, an electric conductivity meter 69 for measuring the electric conductivity of the drainage 8 is provided, and the valve 67 is controlled based on the measured value of the electric conductivity meter 69 to control the circulation amount to the cleaning tank 54. Yes. That is, at the initial stage of water washing, the waste water 8 is circulated and used for washing. When the impurity concentration in the waste water 8 becomes high, the waste water 9 is discharged out of the system. When the drainage 9 is discharged out of the system, the water 3 valve 65 is controlled to replenish water 3. In this way, it is possible to reduce the amount of generated wastewater by using a configuration in which wastewater is circulated and used individually in the washing treatment facilities arranged in two stages in series.

本明細書において、実施例1は全て参考例1である。図1を参照して、本実施形態における具体的構成の一例として、実施例1に係るリフター方式の水洗処理装置につき以下に説明する。
本実施例1の水洗処理装置は、水3が貯留された洗浄槽10と、該洗浄槽上部に設けられた焼却灰投入部10aと、洗浄槽下部に設けられた処理灰排出部11と、洗浄槽底部に堆積した焼却灰1を洗浄槽内上方に持ち上げるリフター(機械的手段)12とを備える。図1では、鉛直方向に長辺を有する方形状の洗浄槽10を示しているが、洗浄槽10の形状は限定されない。また、洗浄槽10の底面をホッパ状に形成し、そのホッパ下端にバルブ(不図示)を設けて、水洗処理後にバルブを開放して処理灰2を排出する構成としているが、処理灰排出部11はこれに限定されるものではなく、例えば洗浄槽上方から処理灰をすくい出して排出する構成など、他の手段を用いることも可能である。
In this specification, Example 1 is all Reference Example 1. With reference to FIG. 1, as an example of a specific configuration in the present embodiment, a lifter-type water washing treatment apparatus according to Example 1 will be described below.
The washing apparatus of the first embodiment includes a washing tank 10 in which water 3 is stored, an incinerated ash charging part 10a provided at the upper part of the washing tank, a treated ash discharge part 11 provided at the lower part of the washing tank, And a lifter (mechanical means) 12 for lifting the incinerated ash 1 deposited on the bottom of the cleaning tank upward in the cleaning tank. Although FIG. 1 shows a rectangular cleaning tank 10 having long sides in the vertical direction, the shape of the cleaning tank 10 is not limited. Moreover, although the bottom face of the washing tank 10 is formed in a hopper shape, a valve (not shown) is provided at the lower end of the hopper, and the treated ash 2 is discharged by opening the valve after the water washing process. 11 is not limited to this, and other means such as a configuration for scooping out and discharging the treated ash from above the cleaning tank may be used.

前記リフター12は、洗浄槽上部と下部に、少なくとも一対のスプロケット13、13が設けられ、該スプロケット13、13に無端環状のチェーンガイド14が掛け渡され、該チェーンガイド14にはバケット15が所定間隔毎に複数取り付けられている。バケット15は、チェーンガイド14に対して外側に取り付けられる。スプロケット13、13には、これを回転駆動する駆動手段(不図示)が接続されており、該スプロケット13、13が同一方向に回転することによりチェーンガイド14が回転し、チェーンガイド14とともにバケット15も所定方向に移動するようになっている。バケット15は、回転方向前方に該バケット15の開口部が向くように取り付けられている。   The lifter 12 is provided with at least a pair of sprockets 13 and 13 at an upper part and a lower part of the cleaning tank, and an endless annular chain guide 14 is stretched over the sprockets 13 and 13. A plurality are attached at intervals. The bucket 15 is attached to the outside with respect to the chain guide 14. Driving means (not shown) for rotating the sprockets 13 and 13 are connected to the sprockets 13 and 13, and the chain guide 14 rotates when the sprockets 13 and 13 rotate in the same direction. Are also moved in a predetermined direction. The bucket 15 is attached so that the opening of the bucket 15 faces forward in the rotational direction.

リフター12の最下部の位置は、洗浄槽底面から数mm〜数十mm、好適には2mm〜10mmに設定することが好ましい。これにより、焼却灰1がリフター12の最下部と洗浄槽底面の間に噛み込まれ、破損することを防止可能である。また、死水域が小さくなるように、洗浄槽10の形状、リフター12の構成を設定することが好ましく、これにより焼却灰1の堆積を軽減することが可能である。   The position of the lowermost part of the lifter 12 is preferably set to several mm to several tens mm, preferably 2 mm to 10 mm from the bottom of the cleaning tank. Thereby, it is possible to prevent the incinerated ash 1 from being caught between the lowermost part of the lifter 12 and the bottom surface of the washing tank and being damaged. Moreover, it is preferable to set the shape of the washing tank 10 and the configuration of the lifter 12 so that the dead water area becomes small, and thus the accumulation of the incinerated ash 1 can be reduced.

上記構成を備えた水洗処理装置において、焼却灰投入部10aより洗浄槽10内に投入された焼却灰1は、その比重により一旦、洗浄槽底部に沈降して堆積するが、リフター12を回転駆動させることにより、バケット15が洗浄槽底部に堆積した焼却灰1をすくい上げて洗浄槽上方に持ち上げ搬送し、チェーンガイド14の折り返し点で反転してバケット15内の焼却灰1を放出する。リフタの回転速度は、約1〜6m/分である。放出された焼却灰1は重力により落下し、洗浄槽底部に沈降して再度バケット15により上方に持ち上げられる。この動作を繰り返すことにより、洗浄槽10内で焼却灰は鉛直方向に撹拌される。所定時間、撹拌して水洗処理した後の処理灰2は、処理灰排出部11より排出される。   In the washing apparatus having the above-described configuration, the incinerated ash 1 charged into the cleaning tank 10 from the incinerated ash charging unit 10a is once settled and deposited on the bottom of the cleaning tank due to its specific gravity, but the lifter 12 is driven to rotate. As a result, the bucket 15 scoops up the incinerated ash 1 deposited on the bottom of the cleaning tank, lifts and conveys the incinerated ash 1 above the cleaning tank, and reverses it at the turning point of the chain guide 14 to discharge the incinerated ash 1 in the bucket 15. The rotation speed of the lifter is about 1-6 m / min. The discharged incinerated ash 1 falls by gravity, sinks to the bottom of the washing tank, and is lifted upward by the bucket 15 again. By repeating this operation, the incinerated ash is stirred in the vertical direction in the cleaning tank 10. The treated ash 2 after being stirred and washed with water for a predetermined time is discharged from the treated ash discharge unit 11.

本実施例1によれば、リフター12により焼却灰1を洗浄槽内上方に持ち上げた後、重力により沈降させるようにし、焼却灰1を鉛直方向に撹拌することにより、比重が大きい焼却灰であっても、撹拌混合性を高めることができ、焼却灰が水と十分に接触するため塩素除去率が向上するとともに、処理時間の短縮化が可能となる。また、リフター12により焼却灰1を強制的に持ち上げているため、確実に且つ十分に鉛直方向の撹拌を行うことができる。   According to the first embodiment, after the incineration ash 1 is lifted upward in the washing tank by the lifter 12, the incineration ash 1 is made to settle by gravity, and the incineration ash 1 is stirred in the vertical direction. However, the stirring and mixing properties can be improved, and the incineration ash is sufficiently in contact with water, so that the chlorine removal rate is improved and the processing time can be shortened. Further, since the incineration ash 1 is forcibly lifted by the lifter 12, the vertical agitation can be reliably and sufficiently performed.

本明細書において、実施例2は全て参考例2である。図2を参照して、実施例に係る循環方式の水洗処理装置につき以下に説明する。
本実施例2の水洗処理装置は、水3が貯留された洗浄槽16と、該洗浄槽上部に設けられた焼却灰投入部16aと、洗浄槽下部に設けられた処理灰排出部16bと、洗浄槽底部に堆積した焼却灰1を上方に持ち上げる循環手段(機械的手段)17とを備える。図2では、鉛直方向に長辺を有する方形状の洗浄槽16を示しているが、洗浄槽16の形状は限定されない。また、処理灰排出部16bを洗浄槽下部に設けた構成を示しているが、これに限定されるものではなく、例えば洗浄槽上方から処理灰をすくい出して排出する構成など、他の手段を用いることも可能である。
In this specification, Example 2 is all Reference Example 2. With reference to FIG. 2, it demonstrates below about the water-washing processing apparatus of the circulation system which concerns on Example 2. FIG.
The water washing treatment apparatus of the second embodiment includes a washing tank 16 in which water 3 is stored, an incinerated ash charging part 16a provided at the upper part of the washing tank, a treated ash discharge part 16b provided at the lower part of the washing tank, Circulating means (mechanical means) 17 for lifting the incinerated ash 1 deposited on the bottom of the cleaning tank upward is provided. Although FIG. 2 shows a rectangular cleaning tank 16 having long sides in the vertical direction, the shape of the cleaning tank 16 is not limited. Moreover, although the structure which provided the process ash discharge | emission part 16b in the washing tank lower part is shown, it is not limited to this, For example, other means, such as a structure which scoops out process ash from the washing tank upper part and discharges, are shown. It is also possible to use it.

前記循環手段17は、洗浄槽上部から水3を吸引し、循環配管18を介して洗浄槽底部に設けたノズル18aより所定流速で噴出させる。循環配管18にはポンプ19が設けられている。ノズル18aは、洗浄槽底面に複数設置されている。また、循環配管18の水吸引口が接続される洗浄槽上部には、該水吸引口に焼却灰1が吸引されないように、フード16cが設けられている。   The circulation means 17 sucks the water 3 from the upper part of the cleaning tank and ejects it at a predetermined flow rate from a nozzle 18a provided at the bottom of the cleaning tank via a circulation pipe 18. The circulation pipe 18 is provided with a pump 19. A plurality of nozzles 18a are installed on the bottom surface of the cleaning tank. A hood 16c is provided at the upper part of the cleaning tank to which the water suction port of the circulation pipe 18 is connected so that the incineration ash 1 is not sucked into the water suction port.

上記構成を備えた水洗処理装置において、焼却灰投入部16aより洗浄槽16内に投入された焼却灰1は、その比重により一旦、洗浄槽底部に沈降して堆積するが、ポンプ19を駆動させて循環配管18で洗浄槽上部の水を吸引し、ノズル18aより噴出させることにより、洗浄槽16内に上昇流が形成され、洗浄槽底部に堆積した焼却灰1は上方に持ち上げられ、重力により沈降することによって鉛直方向に撹拌される。ノズル18aからの水の突出流速は、1m/s以上とする。
所定時間、撹拌して水洗処理した処理灰2は、処理灰排出部16bより排出される。
In the washing apparatus having the above-described configuration, the incineration ash 1 charged into the cleaning tank 16 from the incineration ash charging unit 16a is once settled and deposited on the bottom of the cleaning tank due to its specific gravity, but the pump 19 is driven. Then, the water in the upper part of the washing tank is sucked by the circulation pipe 18 and ejected from the nozzle 18a, so that an upward flow is formed in the washing tank 16, and the incineration ash 1 deposited on the bottom of the washing tank is lifted upward, and by gravity Stir in the vertical direction by settling. The protrusion velocity of water from the nozzle 18a is 1 m / s or more.
The treated ash 2 that has been stirred and washed with water for a predetermined time is discharged from the treated ash discharger 16b.

本実施例2によれば、循環手段17により洗浄槽16内に上昇流を形成し、焼却灰1を洗浄槽内上方に持ち上げた後、重力により沈降させるようにし、焼却灰1を鉛直方向に撹拌することにより、比重が大きい焼却灰であっても、撹拌混合性を高めることができ、焼却灰が水と十分に接触するため塩素除去率が向上するとともに、処理時間の短縮化が可能となる。また、本実施例2では循環手段17により形成した上昇流によって焼却灰1を撹拌しているため、簡単な装置構成とすることが可能となる。さらに、循環させる水は、灰の少ない上澄み液を吸引しているため、循環配管18が焼却灰により閉塞したり、磨耗することを防止できる。   According to the second embodiment, the circulating means 17 forms an upward flow in the cleaning tank 16, lifts the incineration ash 1 upward in the cleaning tank, and then sinks it by gravity. By stirring, even incineration ash with a large specific gravity can be mixed with stirring, the incineration ash can be in sufficient contact with water, improving the chlorine removal rate and reducing the processing time. Become. In the second embodiment, the incineration ash 1 is agitated by the upward flow formed by the circulation means 17, so that a simple device configuration can be achieved. Furthermore, since the water to be circulated sucks the supernatant liquid with less ash, it is possible to prevent the circulation pipe 18 from being blocked or worn by the incinerated ash.

本明細書において、実施例3は全て実施例1である。図3〜図5を参照して、実施例3に係るコンベア方式の水洗処理装置につき以下に説明する。
図3に示すように、本実施例3の水洗処理装置は、水3が貯留された洗浄槽20と、該洗浄槽上部に設けられた焼却灰投入部21と、洗浄槽下部に設けられた処理灰排出部22と、洗浄槽底部に堆積した焼却灰1を上方に持ち上げるコンベア(機械的手段)30とを備える。尚、本実施例3では、コンベア30が水洗処理後の処理灰2を排出する機能を兼ね備えた構成につき説明するが、撹拌用のコンベア30とは別に、処理灰排出用のコンベアを備えた構成としてもよい。
In this specification, Example 3 is all Example 1. With reference to FIGS. 3-5, it demonstrates below about the water washing processing apparatus of the conveyor system which concerns on Example 3. FIG.
As shown in FIG. 3, the water washing treatment apparatus according to the third embodiment is provided with a washing tank 20 in which water 3 is stored, an incinerated ash charging unit 21 provided at the upper part of the washing tank, and a lower part of the washing tank. A treated ash discharge unit 22 and a conveyor (mechanical means) 30 for lifting the incinerated ash 1 deposited on the bottom of the washing tank upward are provided. In addition, although the present Example 3 demonstrates about the structure which the conveyor 30 combined also with the function which discharges | emits the processed ash 2 after a water washing process, the structure provided with the conveyor for process ash discharge | emission separately from the stirring conveyor 30 It is good.

コンベア30は、複数のスプロケット32と、これらのスプロケット32に掛け渡されたコンベアチェーン31と、該コンベアチェーン31の外側に取り付けられた複数のバケットスクレーパ40と、を備える。図3のX−X断面図を図4に示す。
コンベアチェーン31は、洗浄槽20底面に沿って平行に配置された部位Aと、部位Aから上方に向けて延設された部位Bと、部位Bから洗浄槽上面に沿って配置された部位Cと、部位Cから一旦上方に突出した後、下降するように配置された部位Dと、部位Dから斜め上方に向けて延設された部位Eと、部位Eから反転する部位Fと、部位Fから斜め下方に向けて延設された部位Gとからなる。スプロケット32は、この形状にコンベアチェーン31を形成する位置に夫々設置される。
The conveyor 30 includes a plurality of sprockets 32, a conveyor chain 31 that spans the sprockets 32, and a plurality of bucket scrapers 40 that are attached to the outside of the conveyor chain 31. FIG. 4 is a sectional view taken along line XX in FIG.
The conveyor chain 31 includes a part A disposed in parallel along the bottom surface of the cleaning tank 20, a part B extending upward from the part A, and a part C disposed from the part B along the top surface of the cleaning tank. And a part D arranged so as to descend once after projecting upward from the part C, a part E extending obliquely upward from the part D, a part F inverted from the part E, and a part F It consists of the site | part G extended toward diagonally downward from. The sprockets 32 are respectively installed at positions where the conveyor chain 31 is formed in this shape.

スプロケット32には、これを回転駆動する駆動手段(不図示)が接続されており、該スプロケット32が同時期に同一方向に回転することによりコンベアチェーン31が回転し、コンベアチェーン31とともにバケットスクレーパ40も所定方向に移動するようになっている。
バケットスクレーパ40は、図5に示すように、正回転時の進行方向には平板状のスクレーパ42を有し、逆回転時の進行方向にはバケット41を有する。
The sprocket 32 is connected to driving means (not shown) for rotationally driving the sprocket 32. When the sprocket 32 rotates in the same direction at the same time, the conveyor chain 31 is rotated, and the bucket scraper 40 together with the conveyor chain 31 is rotated. Are also moved in a predetermined direction.
As shown in FIG. 5, the bucket scraper 40 has a flat plate scraper 42 in the traveling direction during forward rotation and a bucket 41 in the traveling direction during reverse rotation.

コンベア30は、必要に応じて正回転、逆回転に切替可能になっており、図中、実線矢印で示す正回転時には、水洗処理後の処理灰2をスクレーパ42側で底面に沿って押し出し、部位A、部位Gを通って処理灰排出部22より排出するようになっている。一方、破線矢印で示す逆回転時には、洗浄槽20の底部に堆積した焼却灰1を、部位Aにてバケット41側ですくい取り、部位Bにて焼却灰1を上方に持ち上げた後、部位Dにてバケット41の開口部を下方に向けることにより焼却灰を落下させ、重力により沈降させる。この動作により焼却灰1は洗浄槽20内で鉛直方向に撹拌されることとなる。   The conveyor 30 can be switched between forward rotation and reverse rotation as necessary. In the figure, during forward rotation indicated by a solid line arrow, the treated ash 2 after water washing treatment is pushed out along the bottom surface on the scraper 42 side, It discharges from the processing ash discharge part 22 through the part A and the part G. On the other hand, at the time of reverse rotation indicated by a broken line arrow, the incinerated ash 1 deposited on the bottom of the cleaning tank 20 is scooped up at the bucket 41 side at the site A, and the incinerated ash 1 is lifted upward at the site B, and then the site D The incinerated ash is dropped by directing the opening of the bucket 41 downward, and settled by gravity. By this operation, the incineration ash 1 is stirred in the vertical direction in the cleaning tank 20.

コンベア30の最下部の位置は、洗浄槽底面から数mm〜数十mm、好適には2mm〜10mmに設定することが好ましい。これにより、焼却灰1がコンベア30の最下部と洗浄槽底面の間に噛み込まれ、破損することを防止可能である。また、死水域が小さくなるように、洗浄槽20の形状、コンベア30の構成を設定することが好ましく、これにより焼却灰1の堆積を軽減することが可能である。
また、図4に示すように、死水域に対して水又は空気を吹き込むノズル25を設けることが好ましい。
The lowermost position of the conveyor 30 is preferably set to several mm to several tens mm, preferably 2 mm to 10 mm from the bottom of the cleaning tank. Thereby, it is possible to prevent the incinerated ash 1 from being bitten between the lowermost part of the conveyor 30 and the bottom surface of the washing tank and being damaged. Moreover, it is preferable to set the shape of the washing tank 20 and the configuration of the conveyor 30 so as to reduce the dead water area, and this can reduce the accumulation of the incinerated ash 1.
Moreover, as shown in FIG. 4, it is preferable to provide the nozzle 25 which blows in water or air with respect to a dead water area.

上記構成を備えた水洗処理装置において、焼却灰投入部21より洗浄槽20内に投入された焼却灰1は、その比重により一旦、洗浄槽底部に沈降して堆積するが、コンベア30を逆回転に駆動させることにより、バケットスクレーパ40のバケット41が洗浄槽底部に堆積した焼却灰1をすくい上げて洗浄槽上方に持ち上げ搬送し、コンベア40の部位Dにてバケット41内の焼却灰1を放出する。放出された焼却灰1は重力により落下し、洗浄槽底部に沈降して再度バケット41により上方に持ち上げられる。この動作を繰り返すことにより、洗浄槽20内で焼却灰は鉛直方向に撹拌される。
所定時間、撹拌して水洗処理した後、コンベア30の回転方向を正回転に切り替え、洗浄槽底部に堆積した処理灰2をバケットスクレーパ40のスクレーパ42で押し出し移動させ、処理灰排出部22より排出する。
In the washing apparatus having the above-described configuration, the incinerated ash 1 charged into the cleaning tank 20 from the incinerated ash charging unit 21 once settles and accumulates on the bottom of the cleaning tank due to its specific gravity, but reversely rotates the conveyor 30. , The bucket 41 of the bucket scraper 40 scoops up the incineration ash 1 deposited on the bottom of the cleaning tank, lifts and conveys the incineration ash 1 above the cleaning tank, and discharges the incineration ash 1 in the bucket 41 at the site D of the conveyor 40. . The discharged incinerated ash 1 falls by gravity, sinks to the bottom of the washing tank, and is lifted upward by the bucket 41 again. By repeating this operation, the incineration ash is stirred in the vertical direction in the cleaning tank 20.
After stirring and washing with water for a predetermined time, the rotation direction of the conveyor 30 is switched to normal rotation, and the treated ash 2 deposited on the bottom of the washing tank is pushed out by the scraper 42 of the bucket scraper 40 and discharged from the treated ash discharge unit 22. To do.

本実施例3によれば、コンベア30により焼却灰1を洗浄槽内上方に持ち上げた後、重力により沈降させるようにし、焼却灰1を少なくとも鉛直方向に撹拌することにより、比重が大きい焼却灰であっても、撹拌混合性を高めることができ、焼却灰が水と十分に接触するため塩素除去率が向上するとともに、処理時間の短縮化が可能となる。また、コンベア30により焼却灰1を強制的に持ち上げているため、確実に且つ十分に鉛直方向の撹拌を行うことができる。
さらに、焼却灰1の撹拌用コンベア30が、水洗処理後の処理灰排出機能を兼ね備えることにより、装置の高効率化、小型化が可能となる。
さらにまた、実施例1及び実施例3において、洗浄槽内に空気又は水を供給して水流を形成するようにしてもよく、これにより、バケットに収容された焼却灰近傍の水が局所的に塩素濃度が高くなった場合にも、水流により常に新しい水に入れ替わり、塩素除去効果を高めることが可能となる。
According to the third embodiment, after the incineration ash 1 is lifted upward in the washing tank by the conveyor 30, it is allowed to settle by gravity, and the incineration ash 1 is stirred at least in the vertical direction so that the incineration ash having a large specific gravity can be obtained. Even if it exists, since stirring mixing property can be improved and incineration ash fully contacts with water, while a chlorine removal rate improves, processing time can be shortened. Moreover, since the incinerated ash 1 is forcibly lifted by the conveyor 30, the vertical stirring can be performed reliably and sufficiently.
Furthermore, since the stirring conveyor 30 for the incinerated ash 1 also has a function of discharging the processed ash after the water washing process, the apparatus can be highly efficient and downsized.
Furthermore, in Example 1 and Example 3, air or water may be supplied into the cleaning tank to form a water flow, whereby the water in the vicinity of the incinerated ash contained in the bucket is locally Even when the chlorine concentration becomes high, the water flow is always replaced with new water, and the chlorine removal effect can be enhanced.

本発明は、洗浄槽内での焼却灰と水の撹拌混合性を高めて塩素除去効率を向上させ、水洗処理灰の塩素濃度を常に低く抑えることが可能であるため、焼却灰からセメント原料等の再資源化原料を製造する設備にて好適に用いられる。   The present invention improves the mixing efficiency of incineration ash and water in the washing tank to improve the chlorine removal efficiency, and can always keep the chlorine concentration of the water-washed ash low. It is suitably used in equipment for producing a recycled material.

本発明の実施例1に係る水洗処理装置の概略側面図である。It is a schematic side view of the water-washing processing apparatus which concerns on Example 1 of this invention. 本発明の実施例2に係る水洗処理装置の概略側面図である。It is a schematic side view of the water-washing processing apparatus which concerns on Example 2 of this invention. 本発明の実施例3に係る水洗処理装置の概略側面図である。It is a schematic side view of the water-washing processing apparatus which concerns on Example 3 of this invention. 図3に示した水洗処理装置のX−X断面図である。It is XX sectional drawing of the water-washing processing apparatus shown in FIG. 図3に示した水洗処理装置が備えるバケットスクレーパの側面図である。It is a side view of the bucket scraper with which the water-washing processing apparatus shown in FIG. 3 is provided. 本発明の実施形態が適用される焼却灰処理システムの一例を示すブロック図である。It is a block diagram showing an example of an incineration ash processing system to which an embodiment of the present invention is applied.

符号の説明Explanation of symbols

1 焼却灰
2 処理灰
3 水
10、16 洗浄槽
12 リフター
15 バケット
17 循環手段
18 循環配管
18a ノズル
19 ポンプ
20 洗浄槽
30 コンベア
31 コンベアチェーン
32 スプロケット
33 持ち上げ部
34 落下部
40 バケットスクレーパ
41 バケット
42 スクレーパ
DESCRIPTION OF SYMBOLS 1 Incinerated ash 2 Treated ash 3 Water 10, 16 Washing tank 12 Lifter 15 Bucket 17 Circulating means 18 Circulating piping 18a Nozzle 19 Pump 20 Cleaning tank 30 Conveyor 31 Conveyor chain 32 Sprocket 33 Lifting part 34 Dropping part 40 Bucket scraper 41 Bucket 42 Scraper

Claims (3)

焼却灰が供給される洗浄槽と、該洗浄槽内にて水に浸漬された焼却灰を撹拌する撹拌手段とを備える焼却灰の水洗処理装置において、
前記撹拌手段が、前記焼却灰を洗浄槽内上方に持ち上げる機械的手段であり、該機械的手段により持ち上げた焼却灰を重力沈降させて、該焼却灰を少なくとも鉛直方向に撹拌し、
前記機械的手段が、前記洗浄槽底部に堆積した焼却灰をすくい上げて洗浄槽内上方に搬送する灰搬送部と、前記灰搬送部が所定間隔で複数取り付けられ、水洗処理した後の前記焼却灰を排出する灰排出コンベアとしての無端環状ガイドと、を備え、
前記無端環状ガイドは、前記灰搬送部の灰載置面が上方に向いた状態で該灰搬送部を上方に移動させ、所定位置で前記灰搬送部を反転させて、該灰搬送部上の焼却灰を落下させるように形成され、
前記無端環状ガイドは、前記焼却灰の排出時には正回転に駆動されて前記灰搬送部の裏面で前記焼却灰を押し出し排出し、前記焼却灰の水洗時には逆回転に駆動されて前記灰搬送部の灰載置面で前記焼却灰を持ち上げ、該焼却灰を撹拌することを特徴とする焼却灰の水洗処理装置。
In an incineration ash washing apparatus comprising a washing tank to which incineration ash is supplied and a stirring means for stirring the incineration ash immersed in water in the washing tank,
The stirring means is a mechanical means for lifting the incineration ash upward in the washing tank, and the incineration ash lifted by the mechanical means is gravity settled to stir the incineration ash at least in the vertical direction,
The incinerated ash after the mechanical means scoops up the incinerated ash deposited on the bottom of the washing tank and conveys the incineration ash upward in the washing tank, and a plurality of the ash conveying parts are attached at predetermined intervals and washed with water. An endless annular guide as an ash discharge conveyor for discharging
The endless annular guide moves the ash transport unit upward with the ash placement surface of the ash transport unit facing upward, and inverts the ash transport unit at a predetermined position, Formed to drop incineration ash,
The endless annular guide is driven to rotate forward at the time of discharging the incinerated ash to push out the incinerated ash at the back surface of the ash transport unit, and is driven to rotate in the reverse direction at the time of washing the incinerated ash to wash the ash transport unit. lift the ash in Heino surface, washing treatment apparatus baked却灰you characterized by stirring the ash.
前記灰搬送部は、前記焼却灰を載置する平板と、該平板の灰載置面側にツメが具備されたバケット状に形成されてなることを特徴とする請求項1に記載の焼却灰の水洗処理装置。 2. The incineration ash according to claim 1, wherein the ash transport unit is formed in a bucket shape in which a flat plate on which the incineration ash is placed and a claw is provided on the ash placement surface side of the flat plate. Water washing treatment equipment. 前記洗浄槽の死水域に空気又は水を噴出して水流を形成する灰詰まり防止手段を備えることを特徴とする請求項1又は2に記載の焼却灰の水洗処理装置。 The incineration ash washing apparatus according to claim 1 or 2 , further comprising ash clogging prevention means for jetting air or water into a dead water area of the washing tank to form a water flow.
JP2008231750A 2008-09-03 2008-09-10 Incineration ash washing equipment Active JP5020202B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2008231750A JP5020202B2 (en) 2008-09-03 2008-09-10 Incineration ash washing equipment

Applications Claiming Priority (3)

Application Number Priority Date Filing Date Title
JP2008226004 2008-09-03
JP2008226004 2008-09-03
JP2008231750A JP5020202B2 (en) 2008-09-03 2008-09-10 Incineration ash washing equipment

Publications (2)

Publication Number Publication Date
JP2010082487A JP2010082487A (en) 2010-04-15
JP5020202B2 true JP5020202B2 (en) 2012-09-05

Family

ID=42246981

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2008231750A Active JP5020202B2 (en) 2008-09-03 2008-09-10 Incineration ash washing equipment

Country Status (1)

Country Link
JP (1) JP5020202B2 (en)

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP6332990B2 (en) * 2014-02-07 2018-05-30 Jx金属株式会社 Water-seal conveyor life extension method and chain cleaning device
JP6333089B2 (en) * 2014-06-30 2018-05-30 新日鉄住金エンジニアリング株式会社 Fine particle settling apparatus and settling method
CN115193863B (en) * 2022-05-30 2023-09-15 江苏省环境工程技术有限公司 Device and method for dechlorinating fly ash by carbon dioxide-assisted three-stage countercurrent washing
CN116274291B (en) * 2023-03-13 2024-04-05 杭州银江环保科技有限公司 Waste incineration fly ash washing equipment

Family Cites Families (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0315144Y2 (en) * 1987-02-20 1991-04-03
DE4107029C1 (en) * 1991-03-01 1993-02-25 Veag Vereinigte Energiewerke Ag, O-1140 Berlin, De Method of selecting incompletely burnt ash - involves separating ash into floating and wet fractions and discharges wet ash fraction.
JPH09236222A (en) * 1996-02-27 1997-09-09 Mitsui Eng & Shipbuild Co Ltd Pyrolysis residue separator for waste treating apparatus
JP3391371B2 (en) * 1997-09-19 2003-03-31 三菱マテリアル株式会社 Apparatus and method for removing chlorine and metals from municipal waste incineration ash
JP2004066004A (en) * 2002-08-01 2004-03-04 Hitachi Ltd Waste treating facility
JP4315690B2 (en) * 2003-01-17 2009-08-19 大平洋機工株式会社 Cleaning classifier

Also Published As

Publication number Publication date
JP2010082487A (en) 2010-04-15

Similar Documents

Publication Publication Date Title
KR20070000615A (en) Apparatus for separating wastes from the scrapped materials in recycling system of waste materials
JP5020202B2 (en) Incineration ash washing equipment
JP2010227827A (en) System and method for treating granule
CN109925785B (en) Method for removing kitchen waste slurry settled sand and light impurities and settled sand system thereof
CN112958596B (en) Multi-stage hot washing screening method and system for oil-containing sludge sundries
CN110204157B (en) Oil sludge treatment process
JP2012106158A (en) Contaminated soil washing tank
KR100453932B1 (en) A type of water tank for separating apparatus of construction waste
KR200409534Y1 (en) Apparatus For Washing and Cleaning Aggregates of Rotary Type with High Efficiency
KR20070052104A (en) Apparatus for washing and cleaning aggregates of rotary type with high efficiency
CN112024071A (en) Industrial waste recovery device for environmental protection
JP4502531B2 (en) Sedimentation and residue processing equipment
JP4981734B2 (en) Sand basin
JP2008290005A (en) Incinerated ash treatment method and system
CN210543506U (en) Oil-water separator
CN110238115B (en) Oil sludge cleaning machine
JP2004141818A (en) Apparatus for transferring solid substance from grit tank by fluid
JP2010234217A (en) Powdery particle material treatment system, and powdery particle material treatment method
KR101897462B1 (en) Multistage sludge dewatering device
JP5143070B2 (en) Powder processing system and powder processing method
CN206474275U (en) A kind of construction refuse resource spiral autogenous grinding purification separation device
JP2003094069A (en) Method and equipment for treating waste water
JP2008168203A (en) Grit treatment facility and grit treatment method
JP2006095401A (en) Screen residue treatment device
JP4956910B2 (en) Method and apparatus for wet pulverization of incinerated ash

Legal Events

Date Code Title Description
RD03 Notification of appointment of power of attorney

Free format text: JAPANESE INTERMEDIATE CODE: A7423

Effective date: 20110610

A625 Written request for application examination (by other person)

Free format text: JAPANESE INTERMEDIATE CODE: A625

Effective date: 20110908

A977 Report on retrieval

Free format text: JAPANESE INTERMEDIATE CODE: A971007

Effective date: 20120223

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20120313

A521 Request for written amendment filed

Free format text: JAPANESE INTERMEDIATE CODE: A523

Effective date: 20120427

A521 Request for written amendment filed

Free format text: JAPANESE INTERMEDIATE CODE: A821

Effective date: 20120501

TRDD Decision of grant or rejection written
A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

Effective date: 20120529

A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

A61 First payment of annual fees (during grant procedure)

Free format text: JAPANESE INTERMEDIATE CODE: A61

Effective date: 20120612

R150 Certificate of patent or registration of utility model

Ref document number: 5020202

Country of ref document: JP

Free format text: JAPANESE INTERMEDIATE CODE: R150

Free format text: JAPANESE INTERMEDIATE CODE: R150

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20150622

Year of fee payment: 3

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250