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JP4969817B2 - Microbial carrier assembly for water treatment - Google Patents
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JP4969817B2 - Microbial carrier assembly for water treatment - Google Patents

Microbial carrier assembly for water treatment Download PDF

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JP4969817B2
JP4969817B2 JP2005245351A JP2005245351A JP4969817B2 JP 4969817 B2 JP4969817 B2 JP 4969817B2 JP 2005245351 A JP2005245351 A JP 2005245351A JP 2005245351 A JP2005245351 A JP 2005245351A JP 4969817 B2 JP4969817 B2 JP 4969817B2
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water treatment
microbial carrier
water
binder
carrier assembly
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JP2006334588A (en
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卓弘 笹尾
武則 日下部
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Inoac Corp
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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)

Description

本発明は、水処理用微生物担体集合体に関し、特には浄水槽に投入されることにより集合が解除されて水処理用微生物担体に分離する水処理用微生物担体集合体に関する。   The present invention relates to a microbial carrier aggregate for water treatment, and more particularly to a microbial carrier aggregate for water treatment that is released into a water purification tank and separated into a microbial carrier for water treatment.

従来、軟質ポリウレタン発泡体をキュービック形状のチップとした水処理用微生物担体が、微生物による汚水処理用に広く知られている。   Conventionally, a microbial carrier for water treatment using a soft polyurethane foam as a cubic chip is widely known for treating sewage by microorganisms.

しかし、軟質ポリウレタン発泡体は、そのままでは吸水し難いことから、水処理用微生物担体が処理水中に分散し難くなって、汚水処理効率が低くなる問題がある。そこで、吸水性を高める処理を軟質ポリウレタン発泡体の表面に施すことが行われている。ところが、水処理用微生物担体と処理水との接触効率を高めるために水処理用微生物担体を小さくすると、吸水性を高める処理を施す表面が小さくなって、処理が難しくなり、処理作業に手間取るようになる。   However, since the soft polyurethane foam is difficult to absorb water as it is, there is a problem that the microbial carrier for water treatment is difficult to disperse in the treated water and the sewage treatment efficiency is lowered. Therefore, a treatment for increasing water absorption is performed on the surface of the flexible polyurethane foam. However, if the microbial carrier for water treatment is made small in order to increase the contact efficiency between the microbial carrier for water treatment and the treated water, the surface subjected to the treatment for increasing the water absorption becomes small, the treatment becomes difficult, and it takes time for the treatment work. become.

また、軟質ポリウレタン発泡体のチップからなる水処理用微生物担体は、浄水槽に投入する際に周囲に飛散し易く、周囲を汚す問題がある。さらに、軟質ポリウレタン発泡体チップからなる水処理用微生物担体は嵩張るため、梱包容積が大きくなり、輸送や保管に場所を取る問題がある。そこで、水溶性合成樹脂を一部または全部に用いた収容袋に、軟質ポリウレタン発泡体チップからなる水処理用微生物担体を圧縮して収容し、袋ごと浄水槽に投入することが提案されている。これによれば、浄水槽へ投入する際に水処理用微生物担体が飛散するのを防止でき、しかも梱包容積を小さくすることが可能である。しかし、軟質ポリウレタンフォームからなる水処理用微生物担体自体が吸水し難いことに変わりないため、水処理用微生物担体が完全に吸水するまでに、かなりの時間を必要とし、水面に浮かんだ状態がしばらく続き、本来の水処理効率を得るのに時間がかかる問題がある。   In addition, a microbial carrier for water treatment composed of a chip of a flexible polyurethane foam is likely to be scattered around when it is put into a water purification tank, and there is a problem of soiling the surroundings. Furthermore, since the microbial carrier for water treatment made of a flexible polyurethane foam chip is bulky, there is a problem that a packaging volume becomes large and a space is taken for transportation and storage. Therefore, it has been proposed to compress and store a microbial carrier for water treatment made of a soft polyurethane foam chip in a storage bag using a part or all of a water-soluble synthetic resin, and put the bag together into a water purification tank. . According to this, when throwing into the water purification tank, it is possible to prevent the microbial carrier for water treatment from being scattered and to reduce the packing volume. However, since the microbial carrier for water treatment made of flexible polyurethane foam itself is difficult to absorb water, it takes a considerable time for the microbial carrier for water treatment to completely absorb water, and the state of floating on the water surface for a while. There is a problem that it takes time to obtain the original water treatment efficiency.

特開2004−89803号公報JP 2004-89803 A

本発明は前記の点に鑑みなされたものであって、浄水槽への投入時に水処理用微生物担体が飛散することなく、作業性が良好で、さらには梱包容積を小さくすることができ、しかも水処理用微生物担体の吸水性が高く、水処理用微生物担体が処理水内に速やかに水没することのできる水処理用微生物担体集合体の提供を目的とする。   The present invention has been made in view of the above-mentioned points, and the microbial carrier for water treatment is not scattered when thrown into the water purification tank, the workability is good, and the packaging volume can be further reduced. An object of the present invention is to provide a water treatment microbial carrier assembly in which the water treatment microbial carrier has high water absorption, and the water treatment microbial carrier can be quickly submerged in the treated water.

請求項1の発明は、連通気泡構造を有する軟質合成樹脂発泡体からなる水処理用微生物担体が圧縮された状態で集合し、前記圧縮及び集合状態がバインダーにより固定されていると共に、前記バインダーが水の付与により前記圧縮及び集合状態を解除するものからなることを特徴とする水処理用微生物担体集合体に係る。   In the invention of claim 1, the microbial carriers for water treatment made of a soft synthetic resin foam having an open cell structure are assembled in a compressed state, and the compressed and assembled state is fixed by a binder, and the binder is The present invention relates to a microbial carrier assembly for water treatment, which comprises releasing the compressed and aggregated state by application of water.

請求項2の発明は、請求項1において、前記水処理用微生物担体集合体が水に投入されることにより、前記バインダーによる前記圧縮及び集合状態が水分で解除されて、前記水処理用微生物担体が分離復元可能とされていることを特徴とする。   The invention according to claim 2 is the microbial carrier for water treatment according to claim 1, wherein the compressed and aggregated state by the binder is released by moisture when the microbial carrier aggregate for water treatment is put into water. Is characterized in that it can be separated and restored.

請求項3の発明は、請求項1または2において、前記水処理用微生物担体のセル内に前記バインダーが付着していることを特徴とする。   The invention of claim 3 is characterized in that, in claim 1 or 2, the binder is attached in a cell of the microbial carrier for water treatment.

請求項4の発明は、請求項1から3の何れか一項において、前記バインダーが、カルボキシメチルセルロースであることを特徴とする。   The invention of claim 4 is characterized in that, in any one of claims 1 to 3, the binder is carboxymethyl cellulose.

請求項5の発明は、請求項1から3の何れか一項において、前記バインダーが、常温で固体、軟化点または融点が80℃以上の酸の金属塩であることを特徴とする。 The invention of claim 5 is characterized in that, in any one of claims 1 to 3, the binder is a metal salt of an acid having a solid at room temperature, a softening point or a melting point of 80 ° C. or higher .

請求項6の発明は、請求項1から5の何れか一項において、前記連通気泡構造を有する軟質合成樹脂発泡体が、軟質ポリウレタン発泡体であることを特徴とする。   A sixth aspect of the present invention is characterized in that, in any one of the first to fifth aspects, the soft synthetic resin foam having the open cell structure is a soft polyurethane foam.

請求項7の発明は、請求項1から6の何れか一項において、前記連通気泡構造を有する軟質合成樹脂発泡体が、発泡体のセル膜が除膜されたものであることを特徴とする。
A seventh aspect of the present invention is the soft synthetic resin foam having the open cell structure according to any one of the first to sixth aspects, wherein a cell membrane of the foam is removed. .

本発明によれば、水処理用微生物担体集合体は、水処理用微生物担体が圧縮された状態で集合し前記圧縮及び集合状態がバインダーにより固定され、前記バインダーが水の付与により前記圧縮及び集合状態を解除するものからなるため、非圧縮の水処理用微生物担体を梱包するのと比べて梱包容積を小さくすることができる。また、前記背景技術の項で説明した収容袋に水処理用微生物担体を収容する場合は、袋内の水処理用微生物担体間に隙間を生じやすいのに対し、本発明の水処理用微生物担体集合体は水処理用微生物担体間に隙間を生じにくいため、収容袋に水処理用微生物担体を収容するのと比べて梱包容積を小さくすることができる。そのため、輸送や保管に場所を取らず、非圧縮の場合と同一のスペースでより多くの数量を輸送及び保管できるので、輸送費用及び保管費用を減らすことができる。さらに、水処理用微生物担体集合体は、浄水槽へ投入されると、バインダーが浄水槽の水と接触して溶解し、それにより前記水処理用微生物担体の圧縮及び集合状態が解除され、前記水処理用微生物担体が分離して復元し、浄水槽に分散する。そのため、浄水槽へ水処理用微生物担体集合体を投入する際には水処理用微生物担体が飛散することがなく、作業性がよい。   According to the present invention, the microbial carrier assembly for water treatment is assembled in a state where the microbial carrier for water treatment is compressed, and the compression and assembly state are fixed by the binder, and the binder is compressed and assembled by application of water. Since it consists of what cancels | releases a state, a packing volume can be made small compared with packing the microorganism carrier for non-compressed water treatment. Further, when the microbial carrier for water treatment is accommodated in the accommodation bag described in the section of the background art, a gap is easily generated between the microbial carriers for water treatment in the bag, whereas the microbial carrier for water treatment of the present invention is used. Since the aggregate hardly forms a gap between the water treatment microorganism carriers, the packing volume can be reduced as compared with the case where the water treatment microorganism carriers are housed in the housing bag. For this reason, it is possible to transport and store a larger quantity in the same space as in the case of non-compression without taking up space for transportation and storage, thereby reducing transportation costs and storage costs. Further, when the microbial carrier assembly for water treatment is put into the water purification tank, the binder comes into contact with the water in the water purification tank and dissolves, thereby releasing the compressed and aggregated state of the microbial carrier for water treatment, The microorganism carrier for water treatment is separated and restored, and dispersed in the water purification tank. Therefore, when the microbial carrier assembly for water treatment is introduced into the water purification tank, the microbial carrier for water treatment does not scatter and the workability is good.

しかも、本発明によれば、連通気泡構造を有する軟質合成樹脂発泡体からなる水処理用微生物担体の表面及びセル内にバインダーが付着して水処理用微生物担体の圧縮及び集合状態が固定されているため、水処理用微生物担体が水に投入されるまで前記圧縮及び集合状態を確実に維持することができる。さらに、連通気泡構造を有する軟質合成樹脂発泡体からなる水処理用微生物担体の表面及びセル内にカルボキシメチルセルロースが付着して水処理用微生物担体の圧縮及び集合状態が固定されている場合には、カルボキシメチルセルロースが水溶性であるため、カルボキシメチルセルロースの存在により水処理用微生物担体の吸水性を向上させることができる。この吸水性向上により、浄水槽に水処理用微生物担体集合体が投入された際に、水処理用微生物担体が水面下に沈むまでの時間を短くすることができる。   Moreover, according to the present invention, the binder is attached to the surface and the cell of the water treatment microorganism carrier made of the soft synthetic resin foam having the open cell structure, and the compression and aggregation state of the water treatment microorganism carrier is fixed. Therefore, the compressed and assembled state can be reliably maintained until the water treatment microorganism carrier is introduced into water. Furthermore, when the carboxymethyl cellulose adheres to the surface and the cell of the microbial carrier for water treatment composed of a soft synthetic resin foam having an open cell structure, and the compressed and assembled state of the microbial carrier for water treatment is fixed, Since carboxymethyl cellulose is water-soluble, the presence of carboxymethyl cellulose can improve the water absorption of the microbial carrier for water treatment. By this water absorption improvement, when the microbial carrier assembly for water treatment is introduced into the water purification tank, the time until the microbial carrier for water treatment sinks below the water surface can be shortened.

以下本発明の実施形態を詳細に説明する。図1は本発明の一実施形態に係る水処理用微生物担体集合体を示す図、図2は浄水槽への投入による水処理用微生物担体集合体の分解を示す模式図である。   Hereinafter, embodiments of the present invention will be described in detail. FIG. 1 is a diagram showing a microbial carrier assembly for water treatment according to an embodiment of the present invention, and FIG. 2 is a schematic diagram showing decomposition of the microbial carrier assembly for water treatment by charging into a water purification tank.

図1に示す水処理用微生物担体集合体10は、複数の水処理用微生物担体11が圧縮された状態で集合し前記圧縮及び集合状態がバインダーにより固定されたものであって、前記バインダーが水の付与(水との接触)により前記圧縮及び集合状態を解除するものからなり、図2のように、浄水槽21に投入されて水22と接触すると、バインダーによる圧縮及び集合状態の固定が解除されて水処理用微生物担体11が分離し、復元するものである。   A water treatment microorganism carrier assembly 10 shown in FIG. 1 is a collection of a plurality of water treatment microorganism carriers 11 in a compressed state, and the compression and the assembly state are fixed by a binder. 2 (contact with water) to release the compression and aggregation state, as shown in FIG. 2, when it is put into the water purification tank 21 and contacted with water 22, the compression and aggregation state fixation by the binder is released. Thus, the microbial carrier 11 for water treatment is separated and restored.

水処理用微生物担体11は、連通気泡構造を有する軟質合成樹脂発泡体を、所用のサイズのチップとしたものからなる。前記連通気泡構造を有する軟質合成樹脂発泡体としては、特に限定されず、例えば軟質ポリウレタン発泡体やポリオレフィン系樹脂発泡体を挙げることができる。特に軟質ポリウレタン発泡体は、耐摩耗性に優れ、安価で入手が容易なことから好ましい。さらに、連通気泡構造を有する軟質合成樹脂発泡体は、除膜されたものが好ましい。除膜されたものは、セル膜が公知の爆破法や溶解法などで除去されて、三次元網状骨格となっているため、水が内部に浸透し易く、水処理用微生物担体が水中に分散するまでの時間を短縮することができる。また、連通気泡構造を有する軟質合成樹脂発泡体は、嵩密度が20〜70kg/mであるのが好ましい。嵩密度が低くなると水処理用微生物担体11の耐久性が低下し、一方、嵩密度が高くなると水処理用微生物担体11のセルサイズ(気孔)が小さくなって、吸水性が低下するようになると共に、水処理用微生物担体集合体10の製造時に、水処理用微生物担体11の圧縮が難しくなる。水処理用微生物担体11のサイズは、適宜とされるが、通常2mm〜25mmとされる。また、水処理用微生物担体11の形状は適宜の立体とされるが、通常は立方体とされることが多い。 The microbial carrier 11 for water treatment is made of a soft synthetic resin foam having an open cell structure as a chip of a desired size. The soft synthetic resin foam having the open cell structure is not particularly limited, and examples thereof include a soft polyurethane foam and a polyolefin resin foam. In particular, a flexible polyurethane foam is preferable because it is excellent in wear resistance, inexpensive and easily available. Furthermore, it is preferable that the soft synthetic resin foam having the open cell structure has been removed. In the case of the film removal, the cell membrane is removed by a known blasting method or dissolution method to form a three-dimensional network skeleton, so that water easily penetrates into the inside and the microbial carrier for water treatment is dispersed in water. The time until it can be shortened. In addition, the soft synthetic resin foam having an open cell structure preferably has a bulk density of 20 to 70 kg / m 3 . When the bulk density is lowered, the durability of the water treatment microorganism carrier 11 is lowered. On the other hand, when the bulk density is raised, the cell size (pores) of the water treatment microorganism carrier 11 is reduced and the water absorption is lowered. At the same time, it becomes difficult to compress the microbial carrier 11 for water treatment during the production of the microbial carrier aggregate 10 for water treatment. Although the size of the microorganism carrier 11 for water treatment is set appropriately, it is usually 2 mm to 25 mm. Further, the shape of the water treatment microorganism carrier 11 is an appropriate three-dimensional shape, but is usually a cube in many cases.

水処理用微生物担体集合体10における水処理用微生物担体11は、非圧縮状態の体積の10〜70%に圧縮されているのが好ましい。圧縮程度が低いと水処理用微生物担体集合体10が嵩張るため、水処理用微生物担体集合体10の輸送や保管に多くのスペースが必要になり、一方、圧縮程度が高いと水処理用微生物担体集合体10の製造時における圧縮が困難となる。   It is preferable that the microbial carrier 11 for water treatment in the microbial carrier assembly 10 for water treatment is compressed to 10 to 70% of the uncompressed volume. If the degree of compression is low, the microbial carrier assembly 10 for water treatment becomes bulky, so that a large amount of space is required for transporting and storing the microbial carrier assembly 10 for water treatment. It becomes difficult to compress the assembly 10 during manufacture.

バインダーは、乾燥によって接着し、水の付与(水との接触)により接着を解除するものであれば、制限なく使用することができる。前記バインダーとしては、水溶性バインダー、低分子の酸の金属塩、非イオン界面活性剤を挙げることができる。前記低分子の酸の金属塩及び非イオン界面活性剤としては、常温で固体、軟化点または融点が80℃以上のものが好ましい。前記バインダーの具体例として、ポリビニルアルコール(PVA)、ポリN−ビニルアセトアミド(PNVA)、メチルセルロース(MC)、グアパック(GP)、ガラクトース、マンノース、ガムロジン系不均化ロジンカリウム塩及びガムロジン系不均化ロジンナトリウム塩、合成ガムであるアラビアゴム、アルギン酸塩、カラゲーナン、ペクチン及び植物性ガム類、中国産ガムロジン(脂松香)やガムテレピン油及び、これらの誘導体(重合ロジン、水添ロジン、不均化ロジン)、さらにこれらのエステル等を挙げることができる。   Any binder can be used without limitation as long as it adheres by drying and releases the adhesion by application of water (contact with water). Examples of the binder include a water-soluble binder, a metal salt of a low molecular acid, and a nonionic surfactant. As the low-molecular acid metal salt and nonionic surfactant, those having a solid, softening point or melting point of 80 ° C. or higher at room temperature are preferable. Specific examples of the binder include polyvinyl alcohol (PVA), poly N-vinylacetamide (PNVA), methylcellulose (MC), guapac (GP), galactose, mannose, gum rosin disproportionated rosin potassium salt and gum rosin disproportionation. Sodium rosin, synthetic gum arabic, alginate, carrageenan, pectin and vegetable gum, Chinese gum rosin (gum pine incense), gum turpentine oil and their derivatives (polymerized rosin, hydrogenated rosin, disproportionated rosin) ), And esters thereof.

特には、常温でゲル化し、水処理用微生物担体集合体10の製造時における乾燥に際して、耐熱及び耐久性のあるカルボキシメチルセルロース(CMC)や、常温で固体、融点が80℃以上の低分子の酸の金属塩、例えば前記ガムロジン系不均化ロジンカリウム塩及びガムロジン系不均化ロジンナトリウム塩等が好ましい。前記カルボキシメチルセルロースは生分解するため、水処理用微生物担体11のセル内に残った場合に、汚泥分解する微生物がカルボキシメチルセルロースを分解することによってさらに活性化し、汚泥処理能力の増大を期待することができる。一方、常温で固体、軟化点または融点が80℃以上の低分子の酸の金属塩は、取り扱い、保管、輸送などの環境条件を考慮して選択されている。80℃より低い場合、環境条件によってはバインダーの融解が生じ、水処理用微生物担体集合体の崩壊がおこるおそれがある。なお、乾燥に際して耐熱及び耐久性を備えていないバインダーでは、乾燥時に変質して不溶性となり、浄水槽に水処理用微生物担体集合体10を投入した際にバインダーが分解(接着解除)しなかったり、水処理用微生物担体集合体10の輸送時に接着強度が低下して水処理用微生物担体11が水処理用微生物担体集合体10から脱落したりする。また、コーンスターチや澱粉糊をバインダーとして使用した場合、乾燥時の加熱によってコーンスターチや澱粉糊がグルテンに変質して不溶性となるため、バインダーが水に溶けず、水処理用微生物担体集合体10の水処理用微生物担体11が分解、分散することがなかった。   In particular, carboxymethylcellulose (CMC) that is gelled at room temperature and dried at the time of production of the microbial support assembly 10 for water treatment, or a low molecular acid that is solid at room temperature and has a melting point of 80 ° C. or higher. These metal salts are preferred, such as the above-mentioned gum rosin-based disproportionated rosin potassium salt and gum rosin-based disproportionated rosin sodium salt. Since the carboxymethyl cellulose is biodegraded, if it remains in the cell of the water treatment microorganism carrier 11, the microorganisms that decompose sludge are further activated by decomposing carboxymethyl cellulose, and an increase in sludge treatment capacity can be expected. it can. On the other hand, a metal salt of a low molecular acid that is solid at room temperature, has a softening point, or a melting point of 80 ° C. or higher is selected in consideration of environmental conditions such as handling, storage, and transportation. When the temperature is lower than 80 ° C., the binder may be melted depending on the environmental conditions, and the microbial carrier aggregate for water treatment may collapse. In addition, in the binder that does not have heat resistance and durability at the time of drying, it is altered and becomes insoluble at the time of drying, and when the microbial carrier assembly 10 for water treatment is put into the water purification tank, the binder does not decompose (adhesion release), When the water treatment microbial carrier assembly 10 is transported, the adhesive strength is lowered, and the water treatment microbial carrier 11 is dropped from the water treatment microbial carrier assembly 10. In addition, when corn starch or starch paste is used as a binder, corn starch or starch paste is transformed into gluten by heating during drying and becomes insoluble, so the binder does not dissolve in water, and the water in the microbial carrier assembly 10 for water treatment The processing microorganism carrier 11 was not decomposed or dispersed.

バインダーとしてカルボキシメチルセルロースを用いる場合、カルボキシメチルセルロースは、メチル化率が0.6〜1.4、より好ましくは水による良好な分解性を得るため0.6〜0.8のものである。また、水処理用微生物担体集合体10を製造する際のカルボキシメチルセルロースは、2%濃度の水溶液の粘度が10Pas〜1000Pasのものが好ましく、より好ましくは浄水槽内の水に残留した場合の影響を考慮すると10Pas〜100Pasのものである。さらに、水処理用微生物担体集合体10を製造する際のバインダー水溶液の濃度は、0.5%〜5%が好ましい。濃度が低いと水処理用微生物担体集合体10が取り扱い時に崩れ易くなり、一方、濃度が高いと、水処理用微生物担体集合体10が水により分解し難くなることから、濃度は0.5%〜3%がより好ましい。   When carboxymethyl cellulose is used as the binder, the carboxymethyl cellulose has a methylation rate of 0.6 to 1.4, more preferably 0.6 to 0.8 in order to obtain good decomposability with water. In addition, the carboxymethyl cellulose used in the production of the microbial carrier assembly 10 for water treatment preferably has a 2% strength aqueous solution having a viscosity of 10 Pas to 1000 Pas, and more preferably the effect of remaining in the water in the water purification tank. Considering 10 Pas to 100 Pas. Furthermore, the concentration of the aqueous binder solution when producing the microbial carrier assembly 10 for water treatment is preferably 0.5% to 5%. If the concentration is low, the water treatment microbial carrier assembly 10 is liable to collapse during handling. On the other hand, if the concentration is high, the water treatment microbial carrier assembly 10 is difficult to be decomposed by water. ~ 3% is more preferred.

前記水処理用微生物担体集合体10の製造方法は、圧縮工程、浸漬工程、圧縮繰り返し工程、乾燥工程からなる。   The method for producing the water treatment microorganism carrier assembly 10 includes a compression step, an immersion step, a compression repetition step, and a drying step.

圧縮工程では、前記連通気泡構造を有する軟質合成樹脂発泡体チップからなる水処理用微生物担体11の所要量を圧縮する。その際の圧縮は、非圧縮状態における体積の10〜70%の体積に圧縮するのが好ましい。その際の圧縮が大の場合には圧縮を行うために加える圧力が大きくなりすぎて圧縮が困難となり、一方圧縮が少なすぎる場合には、その後の圧縮繰り返し工程でバインダー水溶液を、水処理用微生物担体11の内部まで含浸させにくくなる。前記圧縮方法の具体的な一例として、図3に示すように一方(図では上方)が開口した網かご31に所要量の水処理用微生物担体11を収容し、前記網かご31の開口部に蓋体33をはめて蓋体33をプレス装置等により網かご31内に押し込むことによって網かご31内の水処理用微生物担体11を圧縮する方法を挙げる。前記蓋体33は、網状のものや小孔を形成した板状体でもよい。なお、前記網目や小孔は前記水処理用微生物担体11が圧縮時に通り抜けない大きさとされる。また圧縮状態で蓋体33を固定するには、図4に示すように、トグルクランプ40を用いて行うことができる。   In the compression step, a required amount of the water treatment microorganism carrier 11 made of the soft synthetic resin foam chip having the open cell structure is compressed. The compression at that time is preferably compressed to a volume of 10 to 70% of the volume in an uncompressed state. If the compression at that time is large, the pressure applied to perform the compression becomes too large and the compression becomes difficult. On the other hand, if the compression is too small, the aqueous binder solution is converted into a microorganism for water treatment in the subsequent compression repeating step. It becomes difficult to impregnate the inside of the carrier 11. As a specific example of the compression method, as shown in FIG. 3, as shown in FIG. 3, a required amount of the microbial carrier 11 for water treatment is accommodated in a mesh cage 31 that is open at one side (upper side in the figure). A method of compressing the water treatment microorganism carrier 11 in the net cage 31 by inserting the lid body 33 and pushing the lid body 33 into the net cage 31 by a press device or the like will be described. The lid 33 may be a net-like member or a plate-like member having a small hole. In addition, the said mesh | network and a small hole are made into the magnitude | size which the said microorganisms carrier 11 for water treatment does not pass through at the time of compression. In addition, the lid 33 can be fixed in a compressed state by using a toggle clamp 40 as shown in FIG.

浸漬工程では、前記水処理用微生物担体11を圧縮した状態の網かご31を、前記バインダー水溶液に浸漬する。このとき、前記網かご11内の水処理用微生物担体11が、完全にバインダー水溶液の液面より下方位置となるようにされる。なお、バインダー水溶液充填前の容器内に前記網かご31を配置して前記圧縮工程を行い、その状態で前記容器内にバインダー水溶液を充填して、この浸漬工程を行ってもよい。例えば、前記網かご31を容器の内底面に配置し、上方に位置するプレス装置の昇降部材に前記蓋体33を係止し、前記蓋体33をプレス装置で網かご31内の所要位置に押し込むことにより前記水処理用微生物担体11を圧縮して前記圧縮工程を行い、次いで前記容器内にバインダー水溶液を充填して前記浸漬工程を行ってもよい。   In the dipping step, the mesh basket 31 in a state where the water treatment microorganism carrier 11 is compressed is dipped in the binder aqueous solution. At this time, the microbial carrier 11 for water treatment in the mesh basket 11 is completely positioned below the liquid surface of the aqueous binder solution. Alternatively, the mesh basket 31 may be placed in a container before filling with the binder aqueous solution to perform the compression step, and in this state, the container may be filled with the aqueous binder solution to perform this dipping step. For example, the mesh basket 31 is disposed on the inner bottom surface of the container, the lid 33 is locked to an elevating member of the press device located above, and the lid 33 is moved to a required position in the mesh cage 31 by the press device. The water treatment microorganism carrier 11 may be compressed by pushing to perform the compression step, and then the dipping step may be performed by filling the container with an aqueous binder solution.

圧縮繰り返し工程では、前記水処理用微生物担体11の圧縮を一旦緩和し、その後再び圧縮する圧縮緩和と圧縮の繰り返しを所要回数行い、これによって水処理用微生物担体11内に強制的にバインダー水溶液を含浸させてセル内に付着させる。そして最終的に非圧縮状態における体積の10〜70%に圧縮した状態とする。なお、前記圧縮緩和状態は、前記水処理用微生物担体11を、非圧縮状態における体積の40〜80%にするのが好ましい。圧縮を緩和する程度が少ないと、バインダー水溶液が水処理用微生物担体11内に含浸し難く、一方、圧縮を緩和する程度が大きいとその後の圧縮量が大になるため、水処理用微生物担体11に強度低下を生じるおそれがある。この際の圧縮及び圧縮緩和は、前記蓋体33を網かご31内で前進後退させることにより行うことができる。具体的な方法として、前記網かご31をバインダー水溶液収容容器内の底面に位置させ、網かご31の上方に配置したプレス装置の昇降部材に前記蓋体33を係止し、プレス装置の昇降部材を上下させることにより行う方法を挙げることができる。   In the compression repetition process, the compression of the water treatment microorganism carrier 11 is temporarily relaxed, and then the compression relaxation and compression are repeated again as many times as necessary, thereby forcing the aqueous binder solution into the water treatment microorganism carrier 11. Impregnate and adhere in the cell. And finally, it is set as the state compressed to 10 to 70% of the volume in an uncompressed state. In the compression relaxation state, the water treatment microorganism carrier 11 is preferably 40 to 80% of the volume in the uncompressed state. If the degree of relaxation is small, the aqueous binder solution is difficult to impregnate the microbial carrier 11 for water treatment. On the other hand, if the degree of relaxation is large, the subsequent amount of compression becomes large. There is a risk that strength will be reduced. In this case, compression and compression relaxation can be performed by moving the lid 33 forward and backward in the net cage 31. As a specific method, the mesh basket 31 is positioned on the bottom surface in the binder aqueous solution container, the lid 33 is locked to the lifting member of the press device disposed above the mesh cage 31, and the lifting member of the press device is secured. The method performed by raising / lowering can be mentioned.

乾燥工程では、前記圧縮状態のまま前記バインダー水溶液から前記水処理用微生物担体11を取り出し、乾燥させることにより前記バインダーの接着力で水処理用微生物担体11の圧縮状態と集合状態を固定し、前記水処理用微生物担体集合体10を得る。前記網かご31を使用する場合には、前記圧縮繰り返し工程終了時の圧縮状態で前記蓋体33の位置を前記トグルクランプ40により固定し、その状態で前記バインダー水溶液から網かご31ごと取り出して乾燥装置で加熱することにより水処理用微生物担体集合体10を形成し、その後に前記網かご31から水処理用微生物担体集合体10を取り出す。なお、前記圧縮繰り返し工程後に、バインダー水溶液を容器から排出し、次いで加熱装置の熱風を前記容器内の網かご31に吹きつけて乾燥を行い、その後網かご31から水処理用微生物担体集合体10を取り出すようにしてもよい。前記乾燥時の温度は、水分を加熱蒸散させることのできる温度とされ、通常は70〜110℃とされる。   In the drying step, the water treatment microorganism carrier 11 is taken out from the aqueous binder solution in the compressed state and dried to fix the compressed state and the aggregated state of the water treatment microorganism carrier 11 with the adhesive force of the binder, A microbial carrier assembly 10 for water treatment is obtained. When the mesh basket 31 is used, the position of the lid 33 is fixed by the toggle clamp 40 in the compressed state at the end of the compression repetition process, and the entire mesh cage 31 is taken out from the aqueous binder solution in that state and dried. The microbial carrier assembly 10 for water treatment is formed by heating with an apparatus, and then the microbial carrier assembly 10 for water treatment is taken out from the net cage 31. After the compression repetition step, the aqueous binder solution is discharged from the container, and then the hot air from the heating device is blown onto the mesh basket 31 in the container for drying, and then the microbial carrier assembly 10 for water treatment is sent from the mesh basket 31. You may make it take out. The temperature at the time of drying is a temperature at which moisture can be evaporated by heating, and is usually 70 to 110 ° C.

・実施例1
縦×横×高さ=3×3×3mmに粉砕された軟質ポリウレタン発泡体からなる水処理用微生物担体(株式会社イノアックコーポレーション製、品番;AQ−3、除膜品、嵩密度;50kg/m)の0.02kgを、図5に示すような円筒形状(内径100mm、高さ100mm)からなる0.785リットル容積のステンレス製網かご45の底部に配置された網状底板49上に投入した。前記網かご45内への水処理用微生物担体の投入により、網かご45は上端まで水処理用微生物担体で一杯になった。次に、網かご45の上方の開口部に網状蓋体51を被せ、プレス装置53により網状蓋体51を網かご45内に押し込んで網状蓋体51を網状底板49から20mmの高さにし、前記水処理用微生物担体を網状底板49と網状蓋体51間で圧縮した。これにより、水処理用微生物担体は、非圧縮状態の体積に対して20%の体積に圧縮され、その状態で維持される。なお、前記網かご45や前記網状底板49及び網状蓋体51の網目は2mmである。また、前記プレス装置53は、前記網かご45の上端に突設された係合部47に解除可能に係合する被係合部54が形成されたプレート55と、前記プレート55の中央に該プレート55を貫通して螺着され、回転により昇降可能とされたねじ部材57と、前記ねじ部材57の下端に設けられた蓋体押圧部59と、ねじ部材57の上端に設けられた回転用把持部61とよりなる。前記プレス装置53は、前記プレート55の被係合部54を網状かご45の係合部47に係合させて網状かご45に取り付け、その状態で前記ねじ部材57を一方向へ回転させて下降させることにより、前記蓋体押圧部59が網状蓋体51を下方へ押して前記水処理用微生物担体を前記網状底板49と網状蓋体51間で圧縮し、一方、前記ねじ部材57を逆方向へ回転させることにより前記蓋体押圧部59を上昇させ、前記水処理用微生物担体の圧縮を緩和あるいは解除することができる。
Example 1
Microorganism carrier for water treatment made of soft polyurethane foam pulverized to length x width x height = 3 x 3 x 3 mm (manufactured by Inoac Corporation, product number; AQ-3, film removal product, bulk density; 50 kg / m 3 ) 0.02 kg was put on a net-like bottom plate 49 arranged at the bottom of a 0.785 liter stainless steel net cage 45 having a cylindrical shape (inner diameter 100 mm, height 100 mm) as shown in FIG. . With the introduction of the water treatment microorganism carrier into the mesh basket 45, the mesh basket 45 was filled with the water treatment microorganism carrier to the upper end. Next, the mesh lid 51 is put on the opening above the mesh basket 45, and the mesh lid 51 is pushed into the mesh basket 45 by the pressing device 53 so that the mesh lid 51 has a height of 20 mm from the mesh bottom plate 49. The microbial carrier for water treatment was compressed between the mesh bottom plate 49 and the mesh lid 51. As a result, the microbial carrier for water treatment is compressed to a volume of 20% with respect to the volume in the non-compressed state and maintained in that state. The mesh of the mesh basket 45, the mesh bottom plate 49, and the mesh lid 51 is 2 mm. The pressing device 53 includes a plate 55 on which an engaged portion 54 that is releasably engaged with an engaging portion 47 projecting from the upper end of the mesh cage 45 is formed, and a plate 55 at the center of the plate 55. A screw member 57 that is screwed through the plate 55 and can be moved up and down by rotation, a lid pressing portion 59 provided at the lower end of the screw member 57, and a rotation member provided at the upper end of the screw member 57 It consists of a gripping part 61. The pressing device 53 engages the engaged portion 54 of the plate 55 with the engaging portion 47 of the mesh cage 45 and attaches it to the mesh cage 45, and in this state, rotates the screw member 57 in one direction and descends. By doing so, the lid pressing part 59 pushes the mesh lid 51 downward to compress the water treatment microorganism carrier between the mesh bottom plate 49 and the mesh lid 51, while the screw member 57 is reversed. By rotating, the lid pressing part 59 is raised, and the compression of the water treatment microorganism carrier can be relaxed or released.

次に、前記水処理用微生物担体を圧縮している網かごを、容積3リットルの容器に予め充填した濃度2%のカルボキシメチルセルロース水溶液(メチル化率;0.6〜0.8、2%濃度の粘度が100〜200Pas)に完全に浸漬させた。   Next, a 2% concentration carboxymethylcellulose aqueous solution (methylation rate: 0.6 to 0.8, 2% concentration) in which a mesh basket in which the above-mentioned microbial carrier for water treatment is compressed is preliminarily filled in a 3 liter container. Was completely immersed in 100-200 Pas).

前記網かごをカルボキシメチルセルロース水溶液に浸漬した状態で、前記プレス装置53のねじ部材57を前記下降時とは反対方向へ回転させて、前記水処理用微生物担体が非圧縮状態時の体積の50%となるように前記網状底板49からの距離が50mmの位置まで網状蓋体51を上昇させ、その後、再び前記ねじ部材57を下降させる方向へ回転させて前記水処理用微生物担体が非圧縮状態の体積の20%となるように、前記網状蓋体51を前記網状底板49から20mmの位置まで下降させた。その状態で、網かご45をカルボキシメチルセルロース水溶液から取り出し、乾燥庫に保管して90℃で24時間加熱乾燥し、その後、水処理用微生物担体の圧縮状態及び集合状態が固定された実施例の水処理用微生物担体集合体を、網かご45から取り出した。   While the mesh cage is immersed in the carboxymethyl cellulose aqueous solution, the screw member 57 of the press device 53 is rotated in the direction opposite to the descending direction so that the microbial carrier for water treatment is 50% of the volume in the uncompressed state. Then, the mesh lid 51 is raised to a position where the distance from the mesh bottom plate 49 is 50 mm, and then the screw member 57 is rotated again in the direction of lowering so that the water treatment microorganism carrier is in an uncompressed state. The mesh lid 51 was lowered from the mesh bottom plate 49 to a position of 20 mm so as to be 20% of the volume. In this state, the net basket 45 is taken out from the carboxymethyl cellulose aqueous solution, stored in a drying cabinet, dried by heating at 90 ° C. for 24 hours, and then the compressed water and the assembled state of the water treatment microorganism carrier are fixed. The microbial carrier assembly for treatment was taken out from the mesh basket 45.

このようにして得られた実施例1の水処理用微生物担体集合体は、直径100mm、高さ20mm、体積157cmであり、梱包容積は0.2リットルであった。この水処理用微生物担体集合体を水槽に投入したところ、20〜45分で完全に水処理用微生物担体に分離し、しかも分離した水処理用微生物担体は全て水面下にあった。 The water treatment microorganism carrier assembly of Example 1 obtained in this way had a diameter of 100 mm, a height of 20 mm, a volume of 157 cm 3 , and a packing volume of 0.2 liters. When this water treatment microbial carrier assembly was put into a water tank, it was completely separated into a water treatment microbial carrier in 20 to 45 minutes, and all the separated water treatment microbial carriers were under the surface of the water.

・実施例2
実施例1における濃度2%のカルボキシメチルセルロース水溶液に代えて、ガムロジン系不均化ロジンカリウム塩の3%水溶液を用い、前記水処理用微生物担体を圧縮している網かごを、容積3リットルの容器に予め充填した前記ガムロジン系不均化ロジンカリウム塩の3%水溶液に完全に浸漬させた。また、前記網かごをガムロジン系不均化ロジンカリウム塩の3%水溶液に浸漬した状態で、前記プレス装置53のねじ部材57を前記下降時とは反対方向へ回転させて、前記水処理用微生物担体が非圧縮状態時の体積の50%となるように前記網状底板49からの距離が50mmの位置まで網状蓋体51を上昇させ、その後、再び前記ねじ部材57を下降させる方向へ回転させて前記水処理用微生物担体が非圧縮状態の体積の20%となるように、前記網状蓋体51を前記網状底板49から20mmの位置まで下降させた。その状態で、網かご45を前記ガムロジン系不均化ロジンカリウム塩の3%水溶液から取り出し、乾燥庫に保管して100℃で20分加熱乾燥した。その後、水処理用微生物担体の圧縮状態及び集合状態が固定された実施例2の水処理用微生物担体集合体を、網かご45から取り出した。このようにして得られた実施例2の水処理用微生物担体集合体は、直径100mm、高さ20mm、体積157cmであり、梱包容積は0.2リットルであった。この水処理用微生物担体集合体を水槽に投入したところ、20〜45分で完全に水処理用微生物担体に分離し、しかも分離した水処理用微生物担体は全て水面下にあった。
Example 2
Instead of the carboxymethylcellulose aqueous solution having a concentration of 2% in Example 1, a 3% aqueous solution of gum rosin-based disproportionated rosin potassium salt was used, and a mesh basket in which the microbial carrier for water treatment was compressed was placed in a container having a volume of 3 liters. Were completely immersed in a 3% aqueous solution of the above-mentioned gum rosin-based disproportionated rosin potassium salt. Further, in the state in which the mesh cage is immersed in a 3% aqueous solution of gum rosin-based disproportionated rosin potassium salt, the screw member 57 of the pressing device 53 is rotated in the direction opposite to that when the descent is performed, thereby The mesh lid 51 is raised to a position where the distance from the mesh bottom plate 49 is 50 mm so that the carrier is 50% of the volume in an uncompressed state, and then the screw member 57 is rotated again in the direction of lowering. The reticulated lid 51 was lowered from the reticulated bottom plate 49 to a position of 20 mm so that the water treatment microorganism carrier was 20% of the uncompressed volume. In this state, the net basket 45 was taken out from the 3% aqueous solution of the gum rosin-based disproportionated rosin potassium salt, stored in a drying cabinet, and dried by heating at 100 ° C. for 20 minutes. Thereafter, the water treatment microorganism carrier aggregate of Example 2 in which the compressed state and the aggregation state of the water treatment microorganism carrier were fixed was taken out of the net cage 45. The water treatment microorganism carrier assembly of Example 2 obtained in this way had a diameter of 100 mm, a height of 20 mm, a volume of 157 cm 3 , and a packing volume of 0.2 liters. When this water treatment microbial carrier assembly was put into a water tank, it was completely separated into a water treatment microbial carrier in 20 to 45 minutes, and all the separated water treatment microbial carriers were under the surface of the water.

また前記実施例と同量の水処理用微生物担体を、バインダーによる圧縮及び集合状態固定を行うことなく、樹脂製シートに包んで段ボール箱で梱包する従来の梱包と比較したところ、本実施例の水処理用微生物担体集合体は従来の40%の梱包容積であった。   In addition, the same amount of the microbial carrier for water treatment as in the above example was compared with the conventional packaging in which it was wrapped in a resin sheet and packed in a cardboard box without performing compression and assembly state fixation with a binder. The microbial carrier aggregate for water treatment has a conventional packing volume of 40%.

さらに、バインダーによる圧縮及び集合状態固定が行われていない水処理用微生物担体を水槽に投入したところ水面下に水没するのに6時間45分必要であった。このことから、本実施例では、従来と比べて水面下に水没するのに必要な時間を5〜12%に短縮することができたのがわかる。   Further, when a microbial carrier for water treatment that was not compressed and aggregated by the binder was put into a water tank, it took 6 hours and 45 minutes to submerge under the surface of the water. From this, it can be seen that in this example, the time required to be submerged under the water surface can be shortened to 5 to 12% compared to the conventional case.

本発明の一実施形態に係る水処理用微生物担体集合体を示す図である。It is a figure which shows the microorganisms carrier assembly for water treatment which concerns on one Embodiment of this invention. 浄水槽への投入による水処理用微生物担体集合体の分解を示す模式図である。It is a schematic diagram which shows decomposition | disassembly of the microorganisms carrier assembly for water treatment by throwing into a water purification tank. 水処理用微生物担体の圧縮時の例を示す概略図である。It is the schematic which shows the example at the time of compression of the microorganisms carrier for water treatment. 網かご内の水処理用微生物単体を圧縮状態にして蓋体を網かごに固定するトグルクランプの例を示す図である。It is a figure which shows the example of the toggle clamp which fixes the cover body to a net cage | basket by making the microorganisms for water treatment in a net cage | basket compressed. 実施例において使用した網かご及びプレス装置等の概略図である。It is the schematic of the net cage | basket and press apparatus etc. which were used in the Example.

符号の説明Explanation of symbols

10 水処理用微生物担体集合体
11 水処理用微生物担体
31,45 網かご
33,51 蓋体
10 Microorganism carrier assembly for water treatment 11 Microbe carrier for water treatment 31, 45 Net basket 33, 51 Lid

Claims (7)

連通気泡構造を有する軟質合成樹脂発泡体からなる水処理用微生物担体が圧縮された状態で集合し、前記圧縮及び集合状態がバインダーにより固定されていると共に、前記バインダーが水の付与により前記圧縮及び集合状態を解除するものからなることを特徴とする水処理用微生物担体集合体。   Microorganism carriers for water treatment composed of a soft synthetic resin foam having an open cell structure are assembled in a compressed state, the compressed and assembled state is fixed by a binder, and the binder is compressed and formed by application of water. A microbial carrier assembly for water treatment, characterized in that it comprises a substance that releases the aggregated state. 前記水処理用微生物担体集合体が水に投入されることにより、前記バインダーによる前記圧縮及び集合状態が水分で解除されて、前記水処理用微生物担体が分離復元可能とされていることを特徴とする請求項1に記載の水処理用微生物担体集合体。   The water treatment microbial carrier aggregate is released into water, so that the compressed and aggregated state by the binder is released with moisture, and the water treatment microbial carrier can be separated and restored. The microbial carrier assembly for water treatment according to claim 1. 前記水処理用微生物担体のセル内に前記バインダーが付着していることを特徴とする請求項1または2に記載の水処理用微生物担体集合体。   The microbial carrier assembly for water treatment according to claim 1 or 2, wherein the binder is attached in a cell of the microbial carrier for water treatment. 前記バインダーが、カルボキシメチルセルロースであることを特徴とする請求項1から3の何れか一項に記載の水処理用微生物担体集合体。   The microbial carrier assembly for water treatment according to any one of claims 1 to 3, wherein the binder is carboxymethylcellulose. 前記バインダーが、常温で固体、軟化点または融点が80℃以上の酸の金属塩であることを特徴とする請求項1から3の何れか一項に記載の水処理用微生物担体集合体。 The microbial carrier assembly for water treatment according to any one of claims 1 to 3, wherein the binder is a solid at normal temperature, a metal salt of an acid having a softening point or a melting point of 80 ° C or higher . 前記連通気泡構造を有する軟質合成樹脂発泡体が、軟質ポリウレタン発泡体であることを特徴とする請求項1から5の何れか一項に記載の水処理用微生物担体集合体。   The microbial carrier assembly for water treatment according to any one of claims 1 to 5, wherein the soft synthetic resin foam having the open cell structure is a soft polyurethane foam. 前記連通気泡構造を有する軟質合成樹脂発泡体が、発泡体のセル膜が除膜されたものであることを特徴とする請求項1から6の何れか一項に記載の水処理用微生物担体集合体。 The microbial carrier assembly for water treatment according to any one of claims 1 to 6, wherein the soft synthetic resin foam having the open cell structure is obtained by removing the cell membrane of the foam. body.
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