JPH0648899U - Anaerobic treatment filter material - Google Patents

Anaerobic treatment filter material

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Publication number
JPH0648899U
JPH0648899U JP405292U JP405292U JPH0648899U JP H0648899 U JPH0648899 U JP H0648899U JP 405292 U JP405292 U JP 405292U JP 405292 U JP405292 U JP 405292U JP H0648899 U JPH0648899 U JP H0648899U
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Prior art keywords
anaerobic
anaerobic treatment
filter medium
filter
treatment
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JP405292U
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JPH0711840Y2 (en
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弘 指吸
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ベスト工業株式会社
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    • 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

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  • Biological Treatment Of Waste Water (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)

Abstract

(57)【要約】 【目的】 嫌気処理用濾材の固形物補捉性等を向上さ
せ、嫌気処理部の処理性能を向上させる。 【構成】 嫌気性微生物による汚水の処理装置の内部へ
不規則状に充填する嫌気処理用濾材に於いて、当該嫌気
処理用濾材の形状を円筒形とし且つその側壁を外形0.
5〜2.5mmの熱可塑性樹脂の糸状体から成る所定厚
さの網状体とする。
(57) [Summary] [Purpose] To improve the solid matter trapping property of the filter for anaerobic treatment and to improve the treatment performance of the anaerobic treatment section. [Constitution] In a filter medium for anaerobic treatment which irregularly fills the inside of an apparatus for treating sewage by anaerobic microorganisms, the filter medium for anaerobic treatment has a cylindrical shape and its side wall has an outer shape of 0.
A net-like body having a predetermined thickness is formed of a thread-like body of a thermoplastic resin having a thickness of 5 to 2.5 mm.

Description

【考案の詳細な説明】[Detailed description of the device]

【0001】[0001]

【産業上の利用分野】[Industrial applications]

本考案は、主として汚水浄化装置の嫌気性処理部に於いて利用されるものであ り、目詰まりが生せず、しかも固形物の捕捉性に優れた嫌気処理用濾材に関する ものである。 The present invention is mainly used in an anaerobic treatment section of a sewage purification device, and relates to an anaerobic treatment filter that does not cause clogging and has excellent solid matter trapping ability.

【0002】[0002]

【従来の技術】[Prior art]

所謂嫌気性微生物による汚水の浄化処理は、従来から各種の浄化装置に於いて 広く利用されている。図5は、当該嫌気性微生物を利用した汚水処理装置の一例 を示すものであり、所謂嫌気濾床接触曝気型合併処理浄化槽の断面概要図である 。 即ち、流入口1から第1嫌気濾床槽2a内へ流入した汚水(屎尿や生活雑排水 )3は、移流管4を通して第2嫌気濾床槽2b内へ入り、先ず両嫌気濾床槽2a ,2b内に於いて、嫌気性微生物による嫌気処理を受ける。嫌気濾床槽2内で嫌 気処理された汚水3aは、引き続き連通孔5を通して接触曝気槽6内へ入り、曝 気処理によって浄化されたあと、沈澱槽7及び消毒槽8を経て、放流口9から外 部へ排出されて行く。 BACKGROUND ART So-called anaerobic microorganism purification treatment of sewage has been widely used in various purification apparatuses. FIG. 5 shows an example of a sewage treatment apparatus using the anaerobic microorganism, and is a schematic sectional view of a so-called anaerobic filter bed contact aeration type combined treatment septic tank. That is, the sewage (human waste or household wastewater) 3 that has flowed into the first anaerobic filter bed tank 2a from the inflow port 1 enters the second anaerobic filter bed tank 2b through the advection pipe 4, and first, both anaerobic filter bed tanks 2a. , 2b, undergoes anaerobic treatment by anaerobic microorganisms. The sewage water 3a that has been anaerobically treated in the anaerobic filter bed tank 2 continuously enters the contact aeration tank 6 through the communication hole 5, is purified by aeration treatment, and then passes through the settling tank 7 and the disinfection tank 8 and then the discharge port. It is discharged from 9 to the outside.

【0003】 而して、前記嫌気濾床槽2の内部には、汚水3内の固形物を捕捉して、接触曝 気槽6内への固形物の流入の防止や嫌気性微生物の繁殖を促進せしめて嫌気処理 能力を高めるために、適宜の厚さの嫌気処理用濾材10が充填されている。 ところが、この嫌気処理用濾材10には、固形物の捕捉性に優れていること 及び目詰まりを起こし難いこと、と云う相反する性能を同時に充足しなければ ならないと云う不可欠の要件があり、現在利用に供されている各種の嫌気処理用 濾材には、夫々一長一短が存在する。Therefore, the solid matter in the wastewater 3 is trapped inside the anaerobic filter bed tank 2 to prevent the solid matter from flowing into the contact aeration tank 6 and to propagate the anaerobic microorganisms. The anaerobic treatment filter medium 10 having an appropriate thickness is filled in order to promote the anaerobic treatment performance. However, the anaerobic treatment filter medium 10 has an essential requirement that it has to satisfy simultaneously the contradictory performances that it is excellent in capturing solids and is unlikely to cause clogging. There are advantages and disadvantages to each type of anaerobic filter material that is used.

【0004】 例えば、従来から使用されているこの種の嫌気処理用濾材には、ポリ塩化ビ ニール等により、外径が150mmφ程度の骨格様のボール体Aに成形されたも の(比表面約64m2/m3)、ポリ塩化ビニール等により、ピッチ約80mm 、高さ約60mmの波形に形成された薄波板体Bのもの(比表面積約55m2/ m3)、ポリプロピレン等から形成した網状の厚さ約60mmの厚板をピッチ 100〜300mm、高さ150〜350mmの波形に折り曲げた網状厚波板体 Cのもの(比表面積約45m2/m3)及びポリエチレン等により外径60mm φ、長さ80mmのかご様の円筒体Dに成形されたもの(比表面積40m2/m3 )等が存在する。For example, a conventional anaerobic filter material of this type is formed into a skeleton-like ball body A having an outer diameter of about 150 mmφ by using polyvinyl chloride or the like. 64 m 2 / m 3 ), a thin corrugated sheet B having a corrugation of about 80 mm 2 and a height of about 60 mm made of polyvinyl chloride (specific surface area of about 55 m 2 / m 3 ), a mesh formed of polypropylene, etc. Of 60 mm thick thick plate with a pitch of 100-300 mm and a height of 150-350 mm bent into a corrugated thick corrugated plate C (specific surface area of about 45 m 2 / m 3 ) and polyethylene etc. , Which is molded into a cage-like cylindrical body D having a length of 80 mm (specific surface area 40 m 2 / m 3 ) and the like.

【0005】 しかし、前記骨格様ボール体Aや薄波板体B、網状厚波板体C及びかご様円筒 体Dの嫌気処理用濾材では、汚泥保持能力や汚泥捕捉性、汚泥の分散性、ガス抜 き性及び濾床内の圧密性等の点に夫々一長一短があり、結果として嫌気濾床槽2 内に於ける処理が不十分となり、嫌気濾床槽2から接触曝気槽6へ流入する汚水 内のBOD値を充分に低下させることが出来なかったり、浄化装置全体の槽容積 を減少し得ないと云う難点がある。However, in the anaerobic treatment filter material of the skeleton-like ball body A, the thin corrugated plate body B, the reticulated thick corrugated plate body C and the basket-like cylindrical body D, sludge retention ability, sludge trapping ability, sludge dispersibility, gas There are merits and demerits in terms of ease of removal and compaction within the filter bed, and as a result, the treatment in the anaerobic filter bed tank 2 becomes insufficient and sewage flowing from the anaerobic filter bed tank 2 into the contact aeration tank 6 is discharged. However, there is a problem that the BOD value in the inside cannot be reduced sufficiently and the tank volume of the entire purification device cannot be reduced.

【0006】[0006]

【考案が解決しようとする課題】[Problems to be solved by the device]

本考案は従前の嫌気処理用濾材に於ける上述の如き問題、即ち嫌気処理用濾材 の汚泥保持能力や汚泥捕捉性が比較的低く、十分な嫌気処理が困難で処理装置の 大幅な小型化が計れないと云う問題を解決せんとするものであり、汚泥捕捉性や 汚泥保持能力が高く、しかも目詰まり等を生じることなしに汚水を高度に嫌気処 理できると共にガス抜きや清掃等も容易に行え、更に比較的安価に製造できるよ うにした嫌気処理用濾材を提供するものである。 The present invention has the above-mentioned problems in the conventional anaerobic treatment filter medium, that is, the sludge retention ability and sludge capturing ability of the anaerobic treatment filter medium are relatively low, sufficient anaerobic treatment is difficult, and the size of the treatment apparatus is significantly reduced. It aims to solve the problem of being unmeasurable, has high sludge trapping ability and sludge holding capacity, and is capable of highly anaerobic treatment of sewage without causing clogging, and easy degassing and cleaning. It is intended to provide a filter medium for anaerobic treatment which can be manufactured at a relatively low cost.

【0007】[0007]

【課題を解決するための手段】[Means for Solving the Problems]

本件考案は、嫌気性微生物による汚水の処理装置の内部へ不規則状に充填する 嫌気処理用濾材に於いて、当該嫌気処理用濾材の形状を円筒形とし且つその側壁 を外形0.5〜2.5mmの熱可塑性樹脂の糸状体から成る所定厚さの網状体とし たことを考案の基本構成とするものである。 The present invention relates to a filter medium for anaerobic treatment that irregularly fills the inside of a device for treating sewage by anaerobic microorganisms. The filter medium for anaerobic treatment has a cylindrical shape and its side wall has an outer shape of 0.5-2. The basic structure of the invention is to form a mesh body of a predetermined thickness made of a thread-shaped body of thermoplastic resin of 0.5 mm.

【0008】[0008]

【作用】[Action]

嫌気処理部へ流入した汚水は、嫌気処理用濾材から成る濾床を通過する間にそ の内部に含まれる固形物が濾材によって捕捉され、所謂濾過処理が行われる。 また、汚泥を含んだ固形物が嫌気処理用濾材に捕捉・保持されることにより、 汚泥内の嫌気性微生物が十分に繁殖し、当該嫌気性微生物による汚水の分解処理 が増進される。 The solid matter contained in the sewage flowing into the anaerobic treatment section is trapped by the filter medium while passing through the filter bed made of the anaerobic treatment filter medium, and so-called filtration treatment is performed. Further, by capturing and retaining the solid matter containing sludge in the anaerobic treatment filter medium, the anaerobic microorganisms in the sludge are sufficiently propagated, and the decomposition treatment of the wastewater by the anaerobic microorganisms is promoted.

【0009】[0009]

【実施例】【Example】

以下、図面に基づいて本考案の実施例を説明する。 図1は本考案に係る嫌気処理用濾材Sの斜面図であり、図2は図1のイーイ視 断面図である。当該嫌気処理用濾材Sは後述する如き方法により、ポリプロピレ ンやポリエチレン等の熱可塑性樹脂の糸状体から成る網状の側壁Saを備えた円 筒体に形成されており、且つその形状寸法は、外径Dが50mm〜300mm、 長さLが外径Dの20%〜300%、網状側壁Saの厚さtが外径Dの10〜3 5%程度に夫々選定されている。 また、前記網状側壁Saを形成する熱可塑性樹脂の糸状体は、その外径が約0 .5〜2mmφ程度に選定されており、且つ直径5〜30mm程度の多数のカー ル体が相互に固着した状態となっている。 An embodiment of the present invention will be described below with reference to the drawings. FIG. 1 is a perspective view of a filter medium S for anaerobic treatment according to the present invention, and FIG. 2 is a cross-sectional view of FIG. The anaerobic treatment filter medium S is formed into a cylindrical body having a mesh-like side wall Sa made of a filamentous material of a thermoplastic resin such as polypropylene or polyethylene by a method described later, and its shape and dimension are The diameter D is selected to be 50 mm to 300 mm, the length L is selected to be 20% to 300% of the outer diameter D, and the thickness t of the mesh side wall Sa is selected to be about 10 to 35% of the outer diameter D. The thermoplastic resin filaments forming the mesh side walls Sa are selected to have an outer diameter of about 0.5 to 2 mmφ, and a large number of curls having a diameter of about 5 to 30 mm are fixed to each other. It is in the state of doing.

【0010】 前記濾材Sの外形寸法は、主としてこれを適用する嫌気濾床槽の容量、汚水の 性質、嫌気処理性能(汚泥捕捉性・汚泥保持率等)及び濾材Sの製造方法等から 決定されるものである。例えば、濾材Sの外径Dが50mmφ以下及び300m mφ以上になると、その製造が難かしくなり、この点から外径Dは50〜300 mmφ程度に限定される。 また、濾材壁体の厚さは、主として目詰まりや汚泥の捕捉性等の点から決定さ れ、濾材Sの外径Dが50の場合には、t=5mm〜17.5mm位が、また、 外径Dが300mmφの場合には、t=30〜105mm位が最適であることが 、実機試験により確認されている。 更に、前記濾材Sの長さLは、主として嫌気濾床部の容量(外形寸法)によっ て決定され、外径Dが50mmφの場合にはL=10〜150mm位に、また、 外径Dが300mmφの場合にはL=300〜600mm位に選定するのが、濾 材Sの充填性や補修(清掃)等の点で好都合であることが、前記実機試験により 確認されている。The outer dimensions of the filter medium S are mainly determined by the capacity of the anaerobic filter bed tank to which the filter medium S is applied, the characteristics of sewage, the anaerobic treatment performance (sludge trapping ability, sludge retention rate, etc.), the method for producing the filter medium S, and the like. It is something. For example, if the outer diameter D of the filter medium S is 50 mmφ or less and 300 mmφ or more, the manufacturing thereof becomes difficult, and from this point, the outer diameter D is limited to about 50 to 300 mmφ. The thickness of the filter medium wall is determined mainly from the viewpoints of clogging and sludge trapping ability. When the outer diameter D of the filter medium S is 50, t = 5 mm to 17.5 mm, and It has been confirmed by an actual machine test that t = 30 to 105 mm is optimal when the outer diameter D is 300 mmφ. Further, the length L of the filter medium S is mainly determined by the capacity (outer dimensions) of the anaerobic filter bed. When the outer diameter D is 50 mmφ, L = 10 to 150 mm, and the outer diameter D It has been confirmed by the above-mentioned actual machine test that it is convenient to select L = 300 to 600 mm when L is 300 mmφ in terms of the filling property and repair (cleaning) of the filter medium S.

【0011】 図3は、本考案に係る濾材Sの製造方法の一例を示すものであり、図4は図3 のローロ視断面図である。 図に於いて、11は合成樹脂供給装置、12はノズル、12aはノズル孔、1 3は糸状体、14は冷却水槽、15は冷却水、16は引き込みローラ、17は送 風機、18は送り出しローラである。 前記合成樹脂供給装置11は、ヒータ11aにより加熱溶融せしめた熱可塑性 合成樹脂材を攪拌羽根11bにより混練すると共に、適当な粘度に混練した合成 樹脂材をスクリューコンベア11cによりひねりを加えた状態で、ノズル12内 へ圧送するものである。 ノズル12内へ圧送された合成樹脂材はノズル孔12aより紡出され、糸状体 13となって下降する。このとき、ノズル孔12aへ供給される熱可塑性合成樹 脂材には、前記スクリューコンベア11cにより所謂ひねりが加えられているた め、ノズル孔12aから紡出された糸状体13は直線状にならず、よじれを生じ た状態となって順次下降する。FIG. 3 shows an example of a method for manufacturing the filter medium S according to the present invention, and FIG. 4 is a cross-sectional view of the filter medium of FIG. In the figure, 11 is a synthetic resin supply device, 12 is a nozzle, 12a is a nozzle hole, 13 is a filament, 14 is a cooling water tank, 15 is cooling water, 16 is a drawing roller, 17 is a blower, and 18 is a delivery. It's Laura. In the synthetic resin supply device 11, the thermoplastic synthetic resin material heated and melted by the heater 11a is kneaded by the stirring blade 11b, and the synthetic resin material kneaded to have an appropriate viscosity is twisted by the screw conveyor 11c. The pressure is fed into the nozzle 12. The synthetic resin material pressure-fed into the nozzle 12 is spun out from the nozzle hole 12a and becomes a filament 13 and descends. At this time, since the so-called twist is applied to the thermoplastic synthetic resin material supplied to the nozzle hole 12a by the screw conveyor 11c, the filament 13 spun from the nozzle hole 12a is not linear. Instead, it twists and gradually descends.

【0012】 よじれを生じた状態で下降してきた糸状体13は、冷却水槽14内の冷却水1 5に触れることにより急冷される。また、急冷により固化力が作用して、糸状体 13の下端部が所謂カール状に変形していく。また、冷却水面の上方近傍で形成 された複数のカール体13aは、相互に接触融着した状態で冷却水15内へ入り 、接触部が硬化することにより相互に強固に固着された状態となる。尚、前記冷 却水槽14の水面近傍へは送風機17により適当な風速で温風が送られており、 この温風により冷却水面上方で形成された複数のカール体13aが強制的に接触 融着されることになる。The filament 13 that has descended in a twisted state is rapidly cooled by touching the cooling water 15 in the cooling water tank 14. Further, the solidification force is applied by the rapid cooling, and the lower end portion of the filamentous body 13 is deformed into a so-called curl shape. Further, the plurality of curls 13a formed in the vicinity of the upper surface of the cooling water enter the cooling water 15 in a state of being in contact with each other and fused, and are hardened to each other by hardening the contact portion. . In addition, warm air is sent to the vicinity of the water surface of the cooling water tank 14 by a blower 17 at an appropriate wind speed, and the plurality of curls 13a formed above the cooling water surface are forcibly brought into contact fusion by the hot air. Will be done.

【0013】 冷却水15内へ引き下げられて硬化した複数のカール体13aの結合物、即ち 、厚さtの網状の側壁Saからなる筒体A´は、冷却水面より僅かに下方に配設 された引き込みローラ16により冷却水15内へ引き込まれ、送り出しローラ1 8を介して機外へ連続的に引き出されていく。尚、本実施例に於いては、図4に 示す如くノズル12のノズル孔12a(直径約0.5〜2.0mmφ)を5〜50 mm間隔でリング状に配列することにより、断面が円形状の筒状体A´を形成す るようにしており、当該筒状体A´を適宜の長さ寸法に切断することにより、嫌 気処理用濾材Sとされる。 また、前記糸状体13のよじれによるカールの直径は、合成樹脂材の粘性やス クリューコンベア11cによるひねり力、ノズル径等を調整することにより変え られ、通常は5〜30mmφに選定されている。A combination of a plurality of curls 13a that have been pulled down into the cooling water 15 and hardened, that is, a cylinder A ′ composed of a net-like side wall Sa having a thickness t is disposed slightly below the cooling water surface. Further, it is drawn into the cooling water 15 by the drawing-in roller 16 and continuously drawn out of the machine through the sending-out roller 18. In this embodiment, as shown in FIG. 4, the nozzle holes 12a (diameter of about 0.5 to 2.0 mmφ) of the nozzle 12 are arranged in a ring shape at intervals of 5 to 50 mm so that the cross section is circular. A tubular body A ′ having a shape is formed, and the tubular body A ′ is cut into an appropriate length dimension to obtain the anaerobic treatment filter medium S. The diameter of the curl due to the twist of the filament 13 can be changed by adjusting the viscosity of the synthetic resin material, the twisting force by the screw conveyor 11c, the nozzle diameter, etc., and is usually selected to be 5 to 30 mmφ.

【0014】 上述の様にして製造された嫌気処理用濾材Sは、嫌気処理部の内部に一定の間 隔を置いて水平に配設した濾材受けと濾材押えとの間の空間部へ約30〜150 0個/m3位の割合で不規則状に充填され、所謂嫌気処理用濾材が形成される。The anaerobic treatment filter medium S manufactured as described above is placed in the anaerobic treatment section in a space between the filter medium receiver and the filter medium retainer, which are horizontally arranged with a certain space therebetween, to the space of about 30 minutes. It is filled irregularly at a rate of about 1500 pieces / m 3 and a so-called anaerobic treatment filter medium is formed.

【0015】 表1は、本考案に係る嫌気処理用濾材の捕捉性と従前のこの種嫌気処理用濾材 の捕捉性との対比を示すものであり、後述する模擬汚泥を使用して実測したもの である。Table 1 shows a comparison between the trapping property of the filter for anaerobic treatment according to the present invention and the trapping property of this type of conventional filter for anaerobic treatment, which was actually measured using a simulated sludge described later. Is.

【0016】[0016]

【表1】 [Table 1]

【0017】 即ち、容量約1.3m3を有する嫌気濾床槽の内部に1m×1m×0.5m(高 さ)の嫌気濾床を形成し、流入口から当該嫌気濾床槽内へSS濃度が3200p pmの人工汚泥を、流量が20l/minの割合で連続的に供給すると共に、そ の放流口から排出される流出水内のSS濃度を連続的に測定し、その平均値を算 定したものである。 尚、当該試験に於いては、各嫌気濾床の全濾材表面積がほぼ同一値に揃えられ ることは勿論である。 表1からも明らかなように、本考案の濾材Sでは約75%[(3200−80 0)/3200]の汚泥が捕捉されることになり、従前の骨格様ボール形濾材A の捕捉率63%[(3200−1200)/3200]に比較して、汚泥捕捉率 が大幅に向上する。That is, an anaerobic filter bed of 1 m × 1 m × 0.5 m (height) is formed inside the anaerobic filter bed tank having a volume of about 1.3 m 3 , and SS is introduced into the anaerobic filter bed tank from the inlet. The artificial sludge with a concentration of 3200 ppm was continuously supplied at a flow rate of 20 l / min, and the SS concentration in the outflow water discharged from the discharge port was continuously measured and the average value was calculated. It is a fixed one. In this test, it goes without saying that the total surface area of the filter media of each anaerobic filter bed is set to the same value. As is clear from Table 1, about 75% [(3200-800) / 3200] of sludge is captured by the filter medium S of the present invention, and the capture rate of the conventional skeleton-like ball filter medium A 63 % [(3200-1200) / 3200], the sludge capture rate is significantly improved.

【0018】[0018]

【考案の効果】[Effect of device]

上述の通り、本考案では濾材Sを、多数のカール状に彎曲せしめたプラスチッ ク糸状体を寄せ集め、これを相互に固着せしめることにより、所定の厚さの網状 側壁を備えた円筒形としている。その結果、従前の嫌気処理用濾材に比較して、 濾材の目詰まりを生ずることなしに汚泥の捕捉率を大幅に向上させることができ 、嫌気処理部に於ける処理能力が大幅に向上する。 また、本考案の嫌気処理用濾材は、所望の外形寸法のものを簡単に且つ連続的 に多量製造することが出来、濾材の製造コストの引き下げが可能になる。 本考案は上述の通り、優れた実用的効用を奏するものである。 As described above, in the present invention, the filter medium S is formed into a cylindrical shape having a net-like side wall of a predetermined thickness by gathering a plurality of plastic filaments curved in a curl shape and fixing them together. . As a result, as compared with the conventional anaerobic treatment filter medium, the sludge capture rate can be greatly improved without causing the filter medium to be clogged, and the treatment capacity in the anaerobic treatment unit is significantly improved. Further, the anaerobic treatment filter medium of the present invention can easily and continuously produce a large amount of a filter having a desired external dimension, and the production cost of the filter medium can be reduced. As described above, the present invention has excellent practical utility.

【図面の簡単な説明】[Brief description of drawings]

【図1】本考案係る嫌気処理用濾材の斜面図である。1 is a perspective view of a filter medium for anaerobic treatment according to the present invention.

【図2】図1のイーイ視断面図である。FIG. 2 is a sectional view taken along the line E-I of FIG.

【図3】嫌気処理用濾材の製造方法の説明図である。FIG. 3 is an explanatory diagram of a method for producing a filter medium for anaerobic treatment.

【図4】図3のローロ視拡大断面図である。FIG. 4 is an enlarged cross-sectional view of the roller of FIG.

【図5】嫌気処理用濾材を利用した合併処理浄化槽の一
例を示すものである。
FIG. 5 shows an example of a combined treatment septic tank using a filter material for anaerobic treatment.

【符号の説明】[Explanation of symbols]

1は 流入口 2は 嫌気濾床槽 3は 汚水 4は 移流管 5は 連通孔 6は 接触曝気槽 7は 沈澱槽 8は 消毒槽 9は 放流口 10は 嫌気処理用濾材 Sは 本考案の嫌気処理用濾材 Saは 網状の側壁 13は 糸状体 1 is inlet 2 is anaerobic filter bed 3 is sewage 4 is advection pipe 5 is communication hole 6 is contact aeration tank 7 is precipitation tank 8 is disinfection tank 9 is discharge port 10 is anaerobic filter S is anaerobic Filter material for treatment Sa is a mesh side wall 13 is a filamentous body

Claims (3)

【実用新案登録請求の範囲】[Scope of utility model registration request] 【請求項1】 嫌気性微生物による汚水の処理装置の内
部へ不規則状に充填する嫌気処理用濾材に於いて、当該
嫌気処理用濾材の形状を円筒形とし且つその側壁を外形
0.5mm〜2.5mmの熱可塑性樹脂の糸状体から成る
所定厚さの網状体としたことを特徴とする嫌気処理用濾
材。
1. A filter medium for anaerobic treatment, which is irregularly filled into a treatment apparatus for wastewater by anaerobic microorganisms, wherein the filter medium for anaerobic treatment has a cylindrical shape and its side wall has an outer shape of 0.5 mm to. A filter material for anaerobic treatment, which is a net-like body having a predetermined thickness and made of a filamentous material of a thermoplastic resin of 2.5 mm.
【請求項2】 形状寸法を、外径が50mm〜300m
m、長さが前記外径の20%〜300%の長さ、側壁厚
さを前記外径の10%〜35%の厚さの円筒形とした請
求項1に記載の嫌気処理用濾材。
2. The shape and the outer diameter are 50 mm to 300 m.
The filter medium for anaerobic treatment according to claim 1, wherein m is a cylindrical shape having a length of 20% to 300% of the outer diameter and a side wall thickness of 10% to 35% of the outer diameter.
【請求項3】 側壁を、糸状体から成る直径が5〜30
mmφの多数のループ体を相互に固着することにより形
成した請求項1又は請求項2に記載の嫌気処理用濾材。
3. The side wall has a diameter of 5 to 30 made of filaments.
The filter medium for anaerobic treatment according to claim 1 or 2, which is formed by fixing a large number of mmφ loop bodies to each other.
JP405292U 1992-02-06 1992-02-06 Anaerobic treatment filter material Expired - Lifetime JPH0711840Y2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP405292U JPH0711840Y2 (en) 1992-02-06 1992-02-06 Anaerobic treatment filter material

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP405292U JPH0711840Y2 (en) 1992-02-06 1992-02-06 Anaerobic treatment filter material

Publications (2)

Publication Number Publication Date
JPH0648899U true JPH0648899U (en) 1994-07-05
JPH0711840Y2 JPH0711840Y2 (en) 1995-03-22

Family

ID=11574125

Family Applications (1)

Application Number Title Priority Date Filing Date
JP405292U Expired - Lifetime JPH0711840Y2 (en) 1992-02-06 1992-02-06 Anaerobic treatment filter material

Country Status (1)

Country Link
JP (1) JPH0711840Y2 (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2004136243A (en) * 2002-10-21 2004-05-13 Geo Front:Kk Water cleaning method
JP2016083642A (en) * 2014-10-29 2016-05-19 フジクリーン工業株式会社 Holding material and wastewater treatment device

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS63119400U (en) * 1987-01-28 1988-08-02
JP3128498U (en) * 2006-08-16 2007-01-18 株式会社兼古製作所 Ball point wrench

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS63119400U (en) * 1987-01-28 1988-08-02
JP3128498U (en) * 2006-08-16 2007-01-18 株式会社兼古製作所 Ball point wrench

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2004136243A (en) * 2002-10-21 2004-05-13 Geo Front:Kk Water cleaning method
JP4620323B2 (en) * 2002-10-21 2011-01-26 株式会社ジオフロント Water purification method
JP2016083642A (en) * 2014-10-29 2016-05-19 フジクリーン工業株式会社 Holding material and wastewater treatment device

Also Published As

Publication number Publication date
JPH0711840Y2 (en) 1995-03-22

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