JPS6244798Y2 - - Google Patents

Info

Publication number
JPS6244798Y2
JPS6244798Y2 JP1982167032U JP16703282U JPS6244798Y2 JP S6244798 Y2 JPS6244798 Y2 JP S6244798Y2 JP 1982167032 U JP1982167032 U JP 1982167032U JP 16703282 U JP16703282 U JP 16703282U JP S6244798 Y2 JPS6244798 Y2 JP S6244798Y2
Authority
JP
Japan
Prior art keywords
granular
water
material layer
particle size
bed
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired
Application number
JP1982167032U
Other languages
Japanese (ja)
Other versions
JPS5970797U (en
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 filed Critical
Priority to JP1982167032U priority Critical patent/JPS5970797U/en
Publication of JPS5970797U publication Critical patent/JPS5970797U/en
Application granted granted Critical
Publication of JPS6244798Y2 publication Critical patent/JPS6244798Y2/ja
Granted legal-status Critical Current

Links

Classifications

    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

Description

【考案の詳細な説明】 本考案は、散水床装置の改善に関するもので
ある。
[Detailed Description of the Invention] The present invention relates to an improvement in a sprinkler bed device.

散水床法は、活性汚泥法のような曝気操作が
不要であるため著しく省エネルギー的であるが、
活性汚泥法に比べ処理水質が劣るという致命的欠
点があり、最近の下水処理場では全く散水床法
が採用されなくなつている。
The sprinkled bed method is extremely energy efficient as it does not require aeration operations like the activated sludge method.
It has a fatal disadvantage of inferior quality of treated water compared to the activated sludge method, and the trickling bed method is no longer being used at all in recent sewage treatment plants.

処理水質が悪いのは、従来の砕石型散水床法
では粒径5〜8cmという大粒径の材が使用され
ているため、表面積が小さく床微生物量が少な
いからである。しかし、小粒径の材を使用する
と空隙径が小さくなるので目詰まりしやすく、こ
のため通気も不良になるという重大な欠点があ
る。すなわち、小粒径の材を用いれば理論的に
は表面積が増大し、処理水質が向上するのである
が、床の閉塞現象を不可避的に招くため、従来
は実用化が不可能とされていた。
The quality of the treated water is poor because the conventional crushed stone sprinkler bed method uses materials with large particle diameters of 5 to 8 cm, resulting in a small surface area and a low amount of bed microorganisms. However, when a material with a small particle size is used, the pore size becomes small, which causes clogging, which leads to poor ventilation, which is a serious drawback. In other words, using a material with a small particle size could theoretically increase the surface area and improve the quality of treated water, but it was previously thought to be impossible to put into practical use because it would inevitably lead to bed clogging. .

本考案は、新規な発想に基づいて、このような
矛盾を完全に克服した散水床装置を提供するも
のである。
The present invention is based on a novel idea and provides a sprinkler bed device that completely overcomes such contradictions.

すなわち本考案は、図面に一実施例を示したよ
うに、散水床槽1内に網などの多孔透水体2を
多段状に設け、該多孔透水体2の各々の上部に比
重1.0未満の粒状固体3を空間部4が形成される
ように充填すると共に、これら各空間部4に空気
流通口5を配備したことを特徴とする散水床装
置である。
That is, in the present invention, as shown in an embodiment in the drawings, porous water-permeable bodies 2 such as nets are provided in multiple stages in a watering floor tank 1, and granules with a specific gravity of less than 1.0 are placed on the upper part of each of the porous water-permeable bodies 2. This sprinkler bed apparatus is characterized in that solids 3 are filled so as to form spaces 4, and air circulation ports 5 are provided in each of these spaces 4.

なお、粒状固体3の形状は任意でよく、独立し
た動きが可能なものであればよい。
Note that the shape of the granular solid 3 may be arbitrary, as long as it is capable of independent movement.

以下、上記実施例について詳細に説明すると、
散水床槽1内には網,多孔板などの多孔透水体
2が多段状に配置されている。多孔透水体2の上
には木材チツプ,発泡スチロール,ポリプロピレ
ンなどの水に浮く粒状固体3が充填されている。
Hereinafter, the above embodiment will be explained in detail.
In the sprinkler floor tank 1, porous water-permeable bodies 2 such as nets and perforated plates are arranged in multiple stages. The porous water-permeable body 2 is filled with granular solids 3 that float on water, such as wood chips, styrofoam, and polypropylene.

粒状固体3の粒径は0.1〜1cm程度とし、従来
の散水床装置に用いられている材の粒径5〜
8cmよりも大幅に小さくすることが重要ポイント
の一つであり、これによつて、材の表面積が増
大し、床内微生物濃度が大幅に向上する結果、
活性汚泥法と同等の良好な処理水質が得られるう
え、原水中のSSの過も可能となる(従来の散
水床装置では、材が大きいため原水中のSS
の過は不可能である)。
The particle size of the granular solid 3 is about 0.1 to 1 cm, and the particle size of the material used in conventional sprinkler bed equipment is 5 to 1 cm.
One of the important points is to make the material much smaller than 8 cm, which increases the surface area of the material and significantly increases the microbial concentration in the floor.
Good treated water quality equivalent to the activated sludge method can be obtained, and it is also possible to remove SS in the raw water (with conventional sprinkler bed equipment, the material is large, so SS in the raw water can be removed).
).

本考案では粒状固体3は空間部4が残るように
充填しておくことが必須要件であるが、粒状固体
3から成る粒状材層の厚みについては、自然通
風によつて該材層内の微生物に酸素供給を行な
うためには10〜20cm程度とすることが好ましく、
50cm以上にすると自然通風が困難となる。このこ
とから、好ましい態様として上記粒状固体として
小粒径のものを用いる本考案は、前記粒状材層
を空間部4を介して多段状に配置した構成にして
ある。
In the present invention, it is an essential requirement that the granular solids 3 be filled so that a space 4 remains, but the thickness of the granular material layer made of the granular solids 3 is determined by the microorganisms in the material layer due to natural ventilation. In order to supply oxygen to the
If the height is more than 50 cm, natural ventilation will be difficult. In view of this, in a preferred embodiment of the present invention in which the granular solid is of small particle size, the granular material layer is arranged in multiple stages with the space 4 interposed therebetween.

次に、本考案装置を用いた廃水の処理態様につ
いて説明すると、下水などの有機性廃水8は散水
床槽1上部の散水部6から散水され、小粒径の
粒状材層内を流れ落ちたのち空間部4の空気中
を滴下し、さらに下段の粒状材層中を流下して
ゆくというサイクルを何回か繰り返したのち、
BODが除去された処理水9が処理水流出口7か
ら流出してゆく。
Next, to explain the manner in which wastewater is treated using the device of the present invention, organic wastewater 8 such as sewage is sprinkled from the water sprinkling section 6 at the top of the water sprinkling bed tank 1, and after flowing down in the layer of granular material with small particle size. After repeating several times the cycle of dripping into the air in the space 4 and further flowing down into the lower granular material layer,
The treated water 9 from which BOD has been removed flows out from the treated water outlet 7.

粒状固体3の表面に生息している微生物に必要
な酸素は、空気流通口5から流入する空気が粒状
材層の厚みが10cm程度と浅く通気抵抗が小さい
ため、容易に粒状材層に侵入することによつて
供給されるため、何ら動力(ブロワー,フアンな
どの)を必要としない。
The oxygen necessary for the microorganisms living on the surface of the granular solid 3 easily enters the granular material layer because the air flowing in through the air flow opening 5 has a shallow thickness of about 10 cm and has low ventilation resistance. It does not require any power (such as a blower or fan).

しかして、処理を継続するに従つて有機性廃水
8中のSSおよび増殖微生物によつて最上段の粒
状材層の通水抵抗が増大してくるが、本考案で
は粒状固体3が水に浮く性質をもつているので、
粒状材層が通水抵抗の増加により浸水し始める
と粒状固体3が浮上し、この結果、それまで捕捉
されていたSSおよび過剰の増殖微生物がはく離
され、下段の粒状材層に水とともに落下してゆ
く。この段でも同様な現象が生起し順次、次の下
段に移つてゆく。このようにして、原水中の
SS,BODがいかに高濃度であつても本考案では
決して粒状材層は目詰まりすることがなく、極
めて円滑に良好な処理を続行することができる。
なお、上段の材層は下段の材層よりもBOD
負荷およびSS負荷が高くなるが、粒状固体3の
粒径を上段ほど大きくしておくことによつて材
層の通水抵抗の増大を軽減できるので極めて好都
合である。
However, as the treatment continues, the water flow resistance of the uppermost granular material layer increases due to the SS and proliferating microorganisms in the organic wastewater 8, but in the present invention, the granular solids 3 float on the water. Because it has the characteristics
When the granular material layer begins to be submerged in water due to an increase in water flow resistance, the granular solids 3 rise to the surface, and as a result, the SS and excessively proliferating microorganisms that had been captured until then are separated and fall to the granular material layer below with water. I'm going to go. A similar phenomenon occurs in this stage, and the stage sequentially moves to the next lower stage. In this way,
No matter how high the concentration of SS and BOD is, in the present invention, the granular material layer will never be clogged, and the processing can continue extremely smoothly and efficiently.
Note that the upper material layer has a lower BOD than the lower material layer.
Although the load and the SS load become higher, increasing the particle size of the granular solid 3 toward the upper stage makes it possible to reduce the increase in water flow resistance of the material layer, which is extremely convenient.

しかして、材層内に捕捉されたSSおよび増
殖微生物は、処理水流出口7に後続して設けられ
た沈殿池,過機などの固液分離工程10にて分
離される。
Thus, the SS and proliferating microorganisms captured in the material layer are separated in a solid-liquid separation step 10, such as a settling tank or a filter, which is provided subsequent to the treated water outlet 7.

以上のような本考案によれば次のような重要な
効果を得ることができ、従来の散水床装置の問
題点を完全に解決できる。
According to the present invention as described above, the following important effects can be obtained, and the problems of conventional sprinkler bed devices can be completely solved.

粒状固体を空間部を介して多段状に配置した
ので、小粒径の粒状固体を用いても通気抵抗が
小さく、自然通風で容易に酸素供給ができ、し
たがつて処理水質の大幅な向上が可能となる。
Since the granular solids are arranged in multiple stages with spaces between them, ventilation resistance is low even when using granular solids with small particle diameters, and oxygen can be easily supplied through natural ventilation, resulting in a significant improvement in the quality of treated water. It becomes possible.

材に浮上性粒子を用いたので、何ら動力も
必要とせずに自動的に材の自己洗浄が行なわ
れ、閉塞のトラブルは起こり得ない。
Since floating particles are used in the material, the material self-cleans automatically without requiring any power, and troubles such as clogging do not occur.

非常に軽い粒子を材とし、しかも、これを
空気中に露出させたため床を支持する多孔透
水体の強度は小さなものですむため、装置の製
作価格を大幅に削減できる。また、床壁は鉄
板などを用いる必要がなく単なるシート状のも
のでよいため、従来から知られている生物処理
装置のすべてと比較して、建設費を最も安価な
ものとすることができる。
Since the material is made of extremely light particles and these are exposed to the air, the strength of the porous water-permeable body that supports the floor can be reduced, resulting in a significant reduction in the manufacturing cost of the device. In addition, the floor and walls do not need to be made of iron plates or the like and can be simply sheet-shaped, so the construction cost can be the lowest compared to all conventionally known biological treatment equipment.

【図面の簡単な説明】[Brief explanation of the drawing]

図面は本考案の一実施例の縦断面図である。 1……散水床槽、2……多孔透水体、3……
粒状固体、4……空間部、5……空気流通口、6
……散水部、7……処理水流出口、8……有機性
廃水、9……処理水、10……固液分離工程。
The drawing is a longitudinal sectional view of an embodiment of the present invention. 1... Watering bed tank, 2... Porous water permeable body, 3...
Granular solid, 4... Space, 5... Air flow opening, 6
... Water sprinkling section, 7 ... Treated water outlet, 8 ... Organic wastewater, 9 ... Treated water, 10 ... Solid-liquid separation step.

Claims (1)

【実用新案登録請求の範囲】 1 槽内に多段状に多孔透水体を配設し、該各々
の多孔透水体上に比重1.0未満の粒状固体から
成る粒状材層ならびにその上方に空間部を形
成せしめると共に該各空間部に空気流通口を配
備した散水床装置。 2 前記粒状固体の粒径を上段から下段に向つて
順次小さくした実用新案登録請求の範囲第1項
記載の装置。 3 前記粒状固体の粒径を0.1〜1cmとした実用
新案登録請求の範囲第1項又は第2項記載の装
置。 4 前記粒状材層の層厚を10〜20cmとした実用
新案登録請求の範囲第1項,第2項又は第3項
記載の装置。
[Claims for Utility Model Registration] 1. Porous water-permeable bodies are arranged in multiple stages in a tank, and a granular material layer consisting of granular solids with a specific gravity of less than 1.0 is formed on each of the porous water-permeable bodies, as well as a space above the layer. A water sprinkling floor device in which air circulation ports are provided in each space. 2. The device according to claim 1, wherein the particle size of the granular solid is gradually decreased from the upper stage to the lower stage. 3. The device according to claim 1 or 2, wherein the particle size of the granular solid is 0.1 to 1 cm. 4. The device according to claim 1, 2, or 3 of the utility model registration claim, wherein the layer thickness of the granular material layer is 10 to 20 cm.
JP1982167032U 1982-11-05 1982-11-05 Trickling filter device Granted JPS5970797U (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP1982167032U JPS5970797U (en) 1982-11-05 1982-11-05 Trickling filter device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP1982167032U JPS5970797U (en) 1982-11-05 1982-11-05 Trickling filter device

Publications (2)

Publication Number Publication Date
JPS5970797U JPS5970797U (en) 1984-05-14
JPS6244798Y2 true JPS6244798Y2 (en) 1987-11-27

Family

ID=30365533

Family Applications (1)

Application Number Title Priority Date Filing Date
JP1982167032U Granted JPS5970797U (en) 1982-11-05 1982-11-05 Trickling filter device

Country Status (1)

Country Link
JP (1) JPS5970797U (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20020072897A (en) * 2001-03-13 2002-09-19 김두성 Onsite wastewater treatment equi pment of biological tower type non-aeration
JP5748206B2 (en) * 2011-03-31 2015-07-15 みつる 高崎 Water purification system and water purification method
JP6112604B2 (en) * 2013-05-29 2017-04-12 学校法人日本大学 Constructed wetland for water quality improvement

Also Published As

Publication number Publication date
JPS5970797U (en) 1984-05-14

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