JP3952768B2 - Final disposal method of treated water - Google Patents
Final disposal method of treated water Download PDFInfo
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- JP3952768B2 JP3952768B2 JP2001386671A JP2001386671A JP3952768B2 JP 3952768 B2 JP3952768 B2 JP 3952768B2 JP 2001386671 A JP2001386671 A JP 2001386671A JP 2001386671 A JP2001386671 A JP 2001386671A JP 3952768 B2 JP3952768 B2 JP 3952768B2
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A20/00—Water conservation; Efficient water supply; Efficient water use
- Y02A20/124—Water desalination
- Y02A20/138—Water desalination using renewable energy
- Y02A20/141—Wind power
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/30—Wastewater or sewage treatment systems using renewable energies
- Y02W10/37—Wastewater or sewage treatment systems using renewable energies using solar energy
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Description
【0001】
【発明の属する技術分野】
本発明は、処理水の最終処分方法に関し、特に、水処理施設から排出される処理水を蒸発乾燥させて処分する処理水の最終処分方法に関する。
【0002】
【従来の技術】
廃棄物の埋立処分に用いられる最終処分場は、通常、底部とその四周に連なる側壁部とに遮水工が施され、上部側が開口した凹形容器状の廃棄物収容部が形成され、この収容部の上方側から順次廃棄物が埋立てられる。
【0003】
そして、所定量の廃棄物が収容部に埋立てられると、その上部に最終覆土を設けて、廃棄物の処分を完了し、廃棄物から発生する浸出水は、処分場に隣接設置される水処理施設で所定の廃水処理を行い、水処理施設で処理された後の浸出水処理水は、そのまま公共水域などに放流していた。
【0004】
しかしながら、このような最終処分方法にあっては、以下に説明する問題があった。
【0005】
【発明が解決しようとする課題】
まず、主として焼却灰を埋立た処分場からの浸出水処理水には、焼却過程で発生する塩化物イオンが含まれており、このイオンを除去しない状態で放流した場合には、農作物などに対する塩害が懸念される。
【0006】
このため、製塩工場などで採用されている膜処理や加熱脱水処理を利用し、浸出水処理水から塩化物イオンを除去し、この後に浸出水処理水を公共水域に放流する方法が考えられるが、このような方法では、塩害を防止することはできても、塩化物イオンの除去に大電力や莫大な火力エネルギーを必要とするため、浸出水処理水の処分に要するコストが高くついてしまう。
【0007】
本発明は、以上の技術課題を解決するものであって、浸出水処理水を公共水域などに放流することなく蒸発乾燥させて処分することにより、公共水域などを利用している農作物などが浸出水処理水に含まれる塩化物イオンによる塩害を受けるのを防止し、さらに、浸出水処理水の処分コストを安く抑えることができる処理水の最終処分方法を提供するものである。
【0008】
【課題を解決するための手段】
前記目的を達成するため、本発明の請求項1に係る処理水の最終処分方法は、廃棄物処分場から排出される浸出水を水処理施設で処理し、該水処理施設から排出される処理水を蒸発施設で蒸発させる処理水の最終処分方法であって、前記蒸発施設は、屋根部の少なくとも南面側が透明ガラス屋根に形成され、一側部に吸気用窓部が設けられ、他側部に排気用窓部が設けられる建物と、前記吸気用窓部に設けられて、前記吸気用窓部から前記排気用窓部に向けて送風するファンと、前記建物の内部に設置されるとともに、内部に前記水処理施設から供給される処理水を一時貯留させる浅底容器状の蒸発槽と、該蒸発槽の底面に交換可能に敷設されるとともに、前記処理水の水分蒸発後の固形分を吸着する黒色に着色されたフィルタマットとを備え、前記ファンの駆動によって前記吸気用窓部から前記排気用窓部に向けて送風し、前記蒸発槽の内部に貯留されている処理水を気液接触させることにより、該処理水の水分を蒸発させることを特徴とする。
本発明による処理水の最終処分方法によれば、蒸発槽に貯留した処理水をファンの駆動によって気液接触させて、処理水の水分のみを蒸発させることで、水分蒸発後の固形分を黒色に着色されたフィルタマットに吸着させることができる。また、黒色に着色されたフィルタマットに吸着させた固形分は、固形分ごとフィルタマットを撤去し、フィルタマットを新しいものと交換することで、固形分(塩分)除去の手間を省略することができる。
また、フィルタマットに吸熱性を付与することができるので、処理水の水分を効率良く蒸発させることができる。
【0012】
【発明の実施の形態】
以下、本発明の好ましい実施の形態につき、添付図面を参照して詳細に説明する。図1は本発明方法を適用した最終処分施設を示すものである。
【0013】
図において、処分施設1の建物2内には、浅底容器状の蒸発槽3が設置され、水処理施設4から供給される処理水を蒸発槽3内に一時貯留するようになっている、また屋根部の少なくとも南面側は太陽光線を通す透明ガラス屋根5となっていて、太陽光を蒸発槽3内に取入れ、これの熱によって、蒸発槽3内に一時貯留された処理水を順次蒸発させている。また、建物2の南北両面には窓部6が開口されている。南面側窓部6は吸気用であって送風用ファン7が装備され、常時南面側窓部6から排気用の北面側窓部6に向けて送風がなされ、気化した水分を順次除去している。
【0014】
蒸発槽3の底面部は防錆処理を施した鉄板8で構成され、この鉄板8の下面には補助加熱用のニクロム線ヒータ9が配置されている。また、鉄板8の上面には太陽光を吸熱しやすいように黒色に着色されたフィルタマット10、例えばアスファルトシートなどが交換可能に敷設されている。このマット10は水分蒸発後の固形分を吸着するものであり、蒸発残滓がある程度たまったら、残滓ごと撤去し、新たなマット10に交換することで、塩分除去の手間を省略できるようにしている。なお、撤去したマット10は焼却処分し、マット10にたまった蒸発残滓は回収して適切に処分する。
【0015】
さらに、処分施設1の敷地内には、太陽光発電装置となる太陽電池パネル11および風力発電装置12が1ないし複数設けられ、これらにより得られた電力を切替器14を介して前記ヒータ9およびファン7に接続している。
【0016】
この切替器14は一般の商用電源15にも接続され、太陽電池パネル11および風力発電装置12の発電量の多寡に応じて商用電源15側から電気を取入れたり(買電)、商用電源15側に余剰電力を供給する(売電)ように切替え可能となっている。すなわち切替器14はファン7およびヒータ9駆動用の必要電力を判定し、その判定値より電力不足であるならば、商用電源15を取入れ、電力が十分であるなら商用電源15をカットし、さらに余剰電力が生じたならばその電力を商用電源15側に送る制御を行う。
【0017】
なお、以上の作用の他に、商用電源15は専ら安価な夜間電力を利用し、太陽光がでている日中は専ら太陽電池パネル11および風力発電装置12で得られた自前の電力を利用することによって昼夜を分たず蒸発処理を可能としている。また、夜間電力で得られた熱は温水タンク内に溜め、これを熱媒体として蒸発槽3の加熱に用いてもよい。
【0018】
以上の構成において、水処理施設4で処理された処理水はある一定量蒸発槽3内に蓄えられ、太陽熱、または補助ヒータ9、あるいは温水の循環による加熱により水分をとばされ、蒸発した水分はファン7により建物2外に順次排出される。そして一定時間経過後には、水分は完全に蒸発し、塩分のみがマット10の表面に析出する。
【0019】
なお、以上の動作を自動化する場合には、蒸発の検出は水分計などにより行い、この計測値が設定値になったら、再度水処理施設4より一定量の処理水を供給する制御を繰返せばよい。また、以上の蒸発乾燥処理は間欠的ならざるを得ないが、その一方で水処理施設4が連続的に水処理を行う必要がある場合には、以上の設備を備えた建物2を複数配列しておき、順次乾燥処理が終った建物に処理水を分配する制御を行えばよい。
【0020】
【発明の効果】
以上の説明により明らかなように、本発明による処理水の最終処分方法によれば、水処理施設からの処理水を蒸発乾燥させて処分しているので、公共水域などを利用している農作物などが処理水に含まれる塩化物イオンによる塩害を受けるのを防止することができる。
また、蒸発施設は、屋根部の少なくとも南面側が透明ガラス屋根に形成され、一側部に吸気用窓部が設けられ、他側部に排気用窓部が設けられる建物と、吸気用窓部に設けられて、吸気用窓部から排気用窓部に向けて送風するファンと、建物の内部に設置される蒸発槽と、蒸発槽の底面に交換可能に敷設されるフィルタマットとを備えた簡単な構成のものであるので、施設の設置に要する費用を安く抑えることができ、水処理施設からの処理水の処分に要する費用を低減させることができる。
さらに、蒸発槽の底面にフィルタマットを交換可能に敷設し、このフィルタマットに処理水の水分蒸発後の固形分を吸着させるようにしたので、フィルタマットを新しいものと交換することにより、固形分(塩分)の除去の手間を省略することができ、これによっても処理水の処分に要する費用を低減させることができる。
さらに、黒色に着色されたフィルタマットを使用しているので、フィルタマットに吸熱性を付与することができ、処理水の水分を効率良く蒸発させることができる。
【図面の簡単な説明】
【図1】本発明方法を適用した浸出水処理水の最終処分施設の説明図である。
【符号の説明】
1 蒸発施設
2 建物
3 蒸発槽
4 水処理施設
5 透明パネル
6 窓部
7 ファン
9 ヒータ
11 太陽光発電装置(太陽光発電パネル)
12 風力発電装置
14 切替器
15 商用電源[0001]
BACKGROUND OF THE INVENTION
The present invention relates to a final disposal method for treated water , and more particularly, to a final disposal method for treated water that is disposed by evaporating and drying treated water discharged from a water treatment facility .
[0002]
[Prior art]
The final disposal site used for landfill disposal of waste usually has a water-impervious construction on the bottom and side walls that are connected to its four sides, forming a concave container-shaped waste container with an open top. Waste is landfilled sequentially from the upper side of the housing part.
[0003]
Then, when a predetermined amount of waste is buried in the container, a final cover is provided on the upper part to complete the disposal of the waste, and the leachate generated from the waste is the water installed adjacent to the disposal site. The prescribed wastewater treatment was performed at the treatment facility, and the treated leachate after being treated at the water treatment facility was discharged as it was into a public water area.
[0004]
However, such a final disposal method has the following problems.
[0005]
[Problems to be solved by the invention]
First, leachate treated water from landfills where incinerated ash is landfilled contains chloride ions that are generated during the incineration process. If these ions are released without removing them, salt damage to crops, etc. will occur. Is concerned.
[0006]
For this reason, it is possible to remove the chloride ions from the leachate treated water using membrane treatment and heat dehydration treatment adopted in salt mills, etc., and then discharge the leachate treated water to the public water area. In such a method, although salt damage can be prevented, high power and enormous thermal energy are required to remove chloride ions, so that the cost required for disposal of treated leachate is high .
[0007]
The present invention solves the above technical problem, and by treating the leachate treated water by evaporating and drying it without discharging it into a public water area, etc., agricultural products that use the public water area are leached. It is intended to provide a final disposal method for treated water that can prevent salt damage caused by chloride ions contained in the treated water, and further reduce the disposal cost of the leachate treated water .
[0008]
[Means for Solving the Problems]
In order to achieve the above object, a final disposal method of treated water according to claim 1 of the present invention is a treatment of leachate discharged from a waste disposal site at a water treatment facility, and a treatment discharged from the water treatment facility. A final disposal method of treated water for evaporating water in an evaporation facility, wherein the evaporation facility is formed of a transparent glass roof on at least the south surface side of the roof portion, an intake window portion is provided on one side portion, and the other side portion. And a building that is provided with an exhaust window, a fan that is provided in the intake window and that blows air from the intake window toward the exhaust window, and is installed inside the building, A shallow-bottomed evaporation tank that temporarily stores treated water supplied from the water treatment facility, and a replaceable laying on the bottom surface of the evaporation tank, and the solid content of the treated water after evaporation of water Bei a filter mat which is colored black to adsorb The fan is driven to blow air from the intake window toward the exhaust window, and the treated water stored in the evaporation tank is brought into gas-liquid contact to evaporate the treated water. It is characterized by making it.
According to the final disposal method of treated water according to the present invention, the treated water stored in the evaporation tank is brought into gas-liquid contact by driving a fan to evaporate only the moisture of the treated water, whereby the solid content after moisture evaporation is black. It can be adsorbed on the filter mat colored . In addition, the solid matter adsorbed on the filter mat colored black can be removed by removing the filter mat together with the solid content and replacing the filter mat with a new one, thereby eliminating the trouble of removing the solid content (salt content). it can.
In addition, since heat absorption can be imparted to the filter mat, the moisture of the treated water can be efficiently evaporated.
[0012]
DETAILED DESCRIPTION OF THE INVENTION
Hereinafter, preferred embodiments of the present invention will be described in detail with reference to the accompanying drawings. FIG. 1 shows a final disposal facility to which the method of the present invention is applied.
[0013]
In the figure, in the building 2 of the disposal facility 1, a shallow container-like evaporation tank 3 is installed, and the treated water supplied from the water treatment facility 4 is temporarily stored in the evaporation tank 3. Further, at least the south surface side of the roof portion is a transparent glass roof 5 through which sunlight passes, and sunlight is taken into the evaporating tank 3, and the treated water temporarily stored in the evaporating tank 3 is sequentially evaporated by the heat of this. I am letting. In addition, windows 6 are opened on both the north and south sides of the building 2. The south side window 6 is for intake and is equipped with a blower fan 7, and air is constantly blown from the south side window 6 toward the north side window 6 for exhaust to sequentially remove the evaporated water. .
[0014]
The bottom surface of the evaporation tank 3 is composed of an iron plate 8 subjected to rust prevention treatment, and a
[0015]
Further, in the site of the disposal facility 1, one or a plurality of solar battery panels 11 and wind power generators 12 serving as solar power generators are provided, and the electric power obtained thereby is supplied to the
[0016]
The switch 14 is also connected to a general
[0017]
In addition to the above effects, the
[0018]
In the above configuration, a certain amount of treated water treated in the water treatment facility 4 is stored in the evaporating tank 3, and moisture is removed by heating by circulation of solar heat,
[0019]
When automating the above operation, evaporation is detected by a moisture meter or the like, and when this measured value becomes a set value, the control for supplying a fixed amount of treated water from the water treatment facility 4 is repeated again. That's fine. Moreover, although the above evaporative drying treatment must be intermittent, on the other hand, when the water treatment facility 4 needs to perform water treatment continuously, a plurality of buildings 2 having the above equipment are arranged. A control for distributing the treated water to the buildings that have been sequentially dried may be performed.
[0020]
【The invention's effect】
As is clear from the above description, according to the final disposal method of treated water according to the present invention, the treated water from the water treatment facility is disposed by evaporating and drying, so that crops using public water areas, etc. Can be prevented from being damaged by chloride ions contained in the treated water.
In addition, the evaporation facility has a building in which at least the south surface side of the roof is formed on a transparent glass roof, an intake window is provided on one side, and an exhaust window is provided on the other side, and an intake window provided, easy with a fan for blowing air toward the exhaust window from the intake window portion, an evaporation tank, which is installed inside a building, and a filter mat which is replaceably laid on the bottom of the evaporation tank Since it is a thing of a simple structure, the expense required for installation of a facility can be held down cheaply, and the expense required for disposal of the treated water from a water treatment facility can be reduced.
Furthermore, since the filter mat is installed on the bottom surface of the evaporation tank so that the filter mat can be exchanged, the solid content after evaporation of the water in the treated water is adsorbed to the filter mat. The labor of removing (salin) can be omitted, and this can also reduce the cost required for disposal of treated water.
Furthermore, since the filter mat colored black is used, the filter mat can be endothermic and the water of the treated water can be efficiently evaporated.
[Brief description of the drawings]
FIG. 1 is an explanatory diagram of a final disposal facility for leachate treated water to which the method of the present invention is applied.
[Explanation of symbols]
1 Evaporation Facility 2 Building 3 Evaporation Tank 4 Water Treatment Facility 5 Transparent Panel 6 Window 7
12 Wind power generator 14
Claims (1)
前記蒸発施設は、屋根部の少なくとも南面側が透明ガラス屋根に形成され、一側部に吸気用窓部が設けられ、他側部に排気用窓部が設けられる建物と、
前記吸気用窓部に設けられて、前記吸気用窓部から前記排気用窓部に向けて送風するファンと、
前記建物の内部に設置されるとともに、内部に前記水処理施設から供給される処理水を一時貯留させる浅底容器状の蒸発槽と、
該蒸発槽の底面に交換可能に敷設されるとともに、前記処理水の水分蒸発後の固形分を吸着する黒色に着色されたフィルタマットとを備え、
前記ファンの駆動によって前記吸気用窓部から前記排気用窓部に向けて送風し、前記蒸発槽の内部に貯留されている処理水を気液接触させることにより、該処理水の水分を蒸発させることを特徴とする処理水の最終処分方法。A final disposal method of treated water that treats leachate discharged from a waste disposal site in a water treatment facility and evaporates treated water discharged from the water treatment facility in an evaporation facility,
The evaporation facility is a building in which at least the south surface side of the roof portion is formed on a transparent glass roof, an intake window portion is provided on one side portion, and an exhaust window portion is provided on the other side portion;
A fan that is provided in the intake window and blows air from the intake window toward the exhaust window;
A shallow vessel-shaped evaporation tank that is installed inside the building and temporarily stores treated water supplied from the water treatment facility,
A replacement mat laid on the bottom surface of the evaporation tank, and a filter mat colored in black to adsorb the solid content after water evaporation of the treated water,
When the fan is driven, air is blown from the intake window toward the exhaust window, and the treated water stored in the evaporation tank is brought into gas-liquid contact to evaporate the moisture of the treated water. A method for final disposal of treated water.
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JP2001386671A JP3952768B2 (en) | 2001-12-19 | 2001-12-19 | Final disposal method of treated water |
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JP2001386671A JP3952768B2 (en) | 2001-12-19 | 2001-12-19 | Final disposal method of treated water |
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