JPH0217997A - Photosynthesizing-bacterium immobilized fiber accumulation - Google Patents
Photosynthesizing-bacterium immobilized fiber accumulationInfo
- Publication number
- JPH0217997A JPH0217997A JP63165676A JP16567688A JPH0217997A JP H0217997 A JPH0217997 A JP H0217997A JP 63165676 A JP63165676 A JP 63165676A JP 16567688 A JP16567688 A JP 16567688A JP H0217997 A JPH0217997 A JP H0217997A
- Authority
- JP
- Japan
- Prior art keywords
- fibers
- bacteria
- photosynthetic bacteria
- fiber aggregate
- immobilized
- 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.)
- Pending
Links
- 239000000835 fiber Substances 0.000 title claims abstract description 70
- 238000009825 accumulation Methods 0.000 title description 2
- 241000894006 Bacteria Species 0.000 claims abstract description 37
- 230000000243 photosynthetic effect Effects 0.000 claims description 37
- 244000005700 microbiome Species 0.000 abstract description 8
- 230000003100 immobilizing effect Effects 0.000 abstract 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 26
- 238000001914 filtration Methods 0.000 description 8
- 235000019645 odor Nutrition 0.000 description 8
- 238000004065 wastewater treatment Methods 0.000 description 8
- 239000013535 sea water Substances 0.000 description 6
- 230000000813 microbial effect Effects 0.000 description 4
- 239000002351 wastewater Substances 0.000 description 4
- 230000000052 comparative effect Effects 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- 229920002994 synthetic fiber Polymers 0.000 description 3
- 239000012209 synthetic fiber Substances 0.000 description 3
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 2
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- 230000001580 bacterial effect Effects 0.000 description 2
- 239000011248 coating agent Substances 0.000 description 2
- 238000000576 coating method Methods 0.000 description 2
- 238000000354 decomposition reaction Methods 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 238000002474 experimental method Methods 0.000 description 2
- 238000000034 method Methods 0.000 description 2
- 239000000203 mixture Substances 0.000 description 2
- 235000016709 nutrition Nutrition 0.000 description 2
- 230000035764 nutrition Effects 0.000 description 2
- 229920000728 polyester Polymers 0.000 description 2
- -1 polyethylene Polymers 0.000 description 2
- 241000251468 Actinopterygii Species 0.000 description 1
- 108010003118 Bacteriochlorophylls Proteins 0.000 description 1
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical compound S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 description 1
- 241000238071 Homarus americanus Species 0.000 description 1
- 239000004677 Nylon Substances 0.000 description 1
- 229920002292 Nylon 6 Polymers 0.000 description 1
- 239000004952 Polyamide Substances 0.000 description 1
- 239000004698 Polyethylene Substances 0.000 description 1
- 239000004743 Polypropylene Substances 0.000 description 1
- 241000131970 Rhodospirillaceae Species 0.000 description 1
- 229910021529 ammonia Inorganic materials 0.000 description 1
- 238000009360 aquaculture Methods 0.000 description 1
- 244000144974 aquaculture Species 0.000 description 1
- 239000004760 aramid Substances 0.000 description 1
- 229920003235 aromatic polyamide Polymers 0.000 description 1
- DSJXIQQMORJERS-AGGZHOMASA-M bacteriochlorophyll a Chemical compound C1([C@@H](C(=O)OC)C(=O)C2=C3C)=C2N2C3=CC([C@H](CC)[C@H]3C)=[N+]4C3=CC3=C(C(C)=O)C(C)=C5N3[Mg-2]42[N+]2=C1[C@@H](CCC(=O)OC\C=C(/C)CCC[C@H](C)CCC[C@H](C)CCCC(C)C)[C@H](C)C2=C5 DSJXIQQMORJERS-AGGZHOMASA-M 0.000 description 1
- 235000021466 carotenoid Nutrition 0.000 description 1
- 150000001747 carotenoids Chemical class 0.000 description 1
- 230000029087 digestion Effects 0.000 description 1
- 238000007598 dipping method Methods 0.000 description 1
- 239000006185 dispersion Substances 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 210000003608 fece Anatomy 0.000 description 1
- 239000000706 filtrate Substances 0.000 description 1
- 239000013505 freshwater Substances 0.000 description 1
- 229910000037 hydrogen sulfide Inorganic materials 0.000 description 1
- 239000012784 inorganic fiber Substances 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 230000007774 longterm Effects 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 230000007102 metabolic function Effects 0.000 description 1
- 238000001000 micrograph Methods 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 239000004745 nonwoven fabric Substances 0.000 description 1
- 229920001778 nylon Polymers 0.000 description 1
- 239000003973 paint Substances 0.000 description 1
- 239000000049 pigment Substances 0.000 description 1
- 238000009372 pisciculture Methods 0.000 description 1
- 229920002239 polyacrylonitrile Polymers 0.000 description 1
- 229920002647 polyamide Polymers 0.000 description 1
- 229920000573 polyethylene Polymers 0.000 description 1
- 229920001155 polypropylene Polymers 0.000 description 1
- 230000001737 promoting effect Effects 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 230000000384 rearing effect Effects 0.000 description 1
- 229920005989 resin Polymers 0.000 description 1
- 239000011347 resin Substances 0.000 description 1
- 230000000717 retained effect Effects 0.000 description 1
- 238000007761 roller coating Methods 0.000 description 1
- 238000005507 spraying Methods 0.000 description 1
Classifications
-
- 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
- Y02W10/10—Biological treatment of water, waste water, or sewage
Landscapes
- Biological Treatment Of Waste Water (AREA)
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
- Nonwoven Fabrics (AREA)
Abstract
Description
【発明の詳細な説明】
〔産業上の利用分野〕
本発明は、光合成細菌固定化繊維集積に関し、微生物フ
ィルター等に利用される。DETAILED DESCRIPTION OF THE INVENTION [Industrial Application Field] The present invention relates to a fiber accumulation with immobilized photosynthetic bacteria, and is used for microbial filters and the like.
従来の繊維集積体は、例えば、養魚用循環フィルター又
は生物処理による排水処理材等の排水処理用フィルター
等に用いられている。この繊維集積体には、排水処理時
に所定の微生物が発生し、この微生物が繊維集積体に付
着し、これにより排水を浄化するものが知られている。Conventional fiber aggregates are used, for example, in filters for wastewater treatment such as circulating filters for fish farming or wastewater treatment materials using biological treatment. It is known that certain microorganisms are generated in this fiber aggregate during wastewater treatment, and these microorganisms adhere to the fiber aggregate, thereby purifying the wastewater.
従来の繊維集積体においては、連続又は長期間の使用に
より、発生した微生物が繊維集積体間に付着、累積して
目詰まり又は悪臭が生じたりする。従って従来の濾過方
法では、水質の保全が十分に維持されにくい。そこでこ
の使用によっても目詰まり又は悪臭も、より低減できる
繊維集積体の現出が望まれている。In conventional fiber aggregates, when used continuously or for a long period of time, microorganisms generated adhere and accumulate between the fiber aggregates, resulting in clogging or foul odors. Therefore, with conventional filtration methods, it is difficult to maintain sufficient water quality. Therefore, it is desired to develop a fiber aggregate that can further reduce clogging and bad odor even when used in this manner.
本発明は上記観点に鑑みてなされたものであり、繊維集
積体を構成する繊維上及び繊維間に積極的に光合成細菌
を固定化するという構成をとることにより、目詰まり又
は悪臭を低減させ、排水処理効率を向上させる光合成細
菌固定化繊維集積体を提供することを目的とする。The present invention has been made in view of the above-mentioned viewpoint, and by adopting a configuration in which photosynthetic bacteria are actively immobilized on and between the fibers constituting the fiber aggregate, clogging or bad odor is reduced, The purpose of the present invention is to provide a photosynthetic bacteria-immobilized fiber aggregate that improves wastewater treatment efficiency.
本発明の光合成細菌固定化繊維集積体は、繊維集積体と
、該繊維集積体を構成する繊維上及び該繊維間に固定さ
れた光合成細菌と、から成ることを特徴とする。The photosynthetic bacteria-immobilized fiber aggregate of the present invention is characterized by comprising a fiber aggregate and photosynthetic bacteria immobilized on and between the fibers constituting the fiber aggregate.
上記繊維集積体とは、種々の繊維が集積されたものであ
る。この繊維集積体としては、例えばフエルト、不織布
又は繊維間の一部をゴム又は樹脂等で結合させた集積体
等が用いられる。このフェルトとしては、ニードルパン
チフェルトでも圧縮フェルトでも織りフェルト等でも良
い。この繊維集積体に用いられる繊維としては、有機質
繊維又は無機質繊維、更にはこれらの混毛は問わないが
、有機質繊維が好ましい。この方が光合成細菌の付着性
が良いからである。又、有機質繊維のうち、天然繊維よ
りも合成繊維例えばナイロン、ポリエステル、ポリアク
リロニトリル、ポリエチレン、ポリプロピレン、ポリア
ミド、全芳香族ポリアミド等が好ましい。合成繊維は、
機械的強度、耐水性、耐海水性、耐候性等に優れるから
である。The fiber aggregate is an aggregate of various fibers. As this fiber aggregate, for example, felt, nonwoven fabric, or an aggregate in which fibers are partially bonded with rubber, resin, or the like is used. This felt may be needle punch felt, compressed felt, woven felt, or the like. The fibers used in this fiber assembly may be organic fibers, inorganic fibers, or a mixture thereof, but organic fibers are preferred. This is because photosynthetic bacteria have better adhesion. Among organic fibers, synthetic fibers such as nylon, polyester, polyacrylonitrile, polyethylene, polypropylene, polyamide, wholly aromatic polyamide, etc. are preferable to natural fibers. Synthetic fibers are
This is because it has excellent mechanical strength, water resistance, seawater resistance, weather resistance, etc.
上記光合成細菌とは、光エネルギーを用いて光無機栄養
又は光有機栄養によって成育する細菌の総称をいい、こ
れは、上記繊維上及び繊維間に固定される。The above-mentioned photosynthetic bacteria is a general term for bacteria that grow by photo-inorganic nutrition or photo-organic nutrition using light energy, and is fixed on the fibers and between the fibers.
本発明においては、繊維集積体を用いるので、その表面
積が大きく更に繊維間に適度の空隙を持ち、そのため光
合成細菌が必要とする光エネルギーを吸収し易く、又、
その細菌群が繊維上又は繊維間に着生、保持され易い。In the present invention, since a fiber aggregate is used, its surface area is large and there are appropriate voids between the fibers, so that it is easy to absorb the light energy required by photosynthetic bacteria.
The bacterial group is likely to settle and be retained on or between the fibers.
又、光合成細菌は、種々のバクテリア及び悪臭成分を消
化する性質があるので、水に含まれている一般雑菌等を
食べて化学変化を起こさせて、分解させる。In addition, photosynthetic bacteria have the property of digesting various bacteria and malodorous components, so they eat general bacteria contained in water, causing chemical changes, and decomposing them.
上記作用に述べたように、この繊維集積体は光エネルギ
ーを効率的に吸収し易く、又、光合成細菌、更には排水
処理に用いられる場合の排水種に応じて生成する種々の
微生物の生育が良い。従って光合成細菌の一般雑菌等及
び悪臭成分の消化効率が良く、更に排水中の有機成分の
分解も良いので、目詰まり及び悪臭が少なく、更に排水
の浄化にも優れ、特に、高濃度有機排水処理又は連続、
長期間使用時のフィルターとしては非常に有用である。As mentioned in the above action, this fiber aggregate easily absorbs light energy efficiently, and also supports the growth of photosynthetic bacteria and various microorganisms that are generated depending on the type of wastewater when used for wastewater treatment. good. Therefore, the digestion efficiency of photosynthetic bacteria and other malodorous components is good, and the decomposition of organic components in wastewater is also good, so there is less clogging and bad odors, and it is also excellent in purifying wastewater, especially for high-concentration organic wastewater treatment. or continuous,
Very useful as a filter for long-term use.
また、本発明では、上記繊維集積体を用いるので、光合
成細菌を繊維上及び繊維間に容易に且つ強固に固定でき
る。特にこの胞子形成能がない光合成細菌だけに繊維集
積体を用いるとその着生は有効である。従って、本発明
においては光合成細菌が有効に固定化されるので、その
脱離がしにくく寿命が長い。Further, in the present invention, since the above-mentioned fiber aggregate is used, photosynthetic bacteria can be easily and firmly fixed on the fibers and between the fibers. In particular, when fiber aggregates are used only for photosynthetic bacteria that do not have the ability to form spores, their attachment is effective. Therefore, in the present invention, since photosynthetic bacteria are effectively immobilized, they are difficult to detach and have a long lifespan.
以上より本発明は、高濃度有機排水処理、水産業の養殖
水槽施設のフィルター等の微生物フィルター等に広く用
いることができる。As described above, the present invention can be widely used for high concentration organic wastewater treatment, microbial filters such as filters for aquaculture tank facilities in the fisheries industry, and the like.
以下、実施例により本発明を具体的に説明する。 Hereinafter, the present invention will be specifically explained with reference to Examples.
第１図及び第２図は光合成細菌固定化繊維集積体１を示
す。1 and 2 show a photosynthetic bacteria-immobilized fiber aggregate 1. FIG.
（１）光合成細菌の繊維集積体への固定化まず、約２０
０Ｘ２００Ｘ３ （厚さ）ｍｍのほぼ正方形状の繊維集
積体を準備する。この繊維集積体はニードルフェルトか
らなり、ナイロン６・６、ポリエステル等の各合成繊維
が混毛されてなるものである。なお繊維の太さは約３〜
ｌＯμｍである。(1) Immobilization of photosynthetic bacteria onto fiber aggregates First, about 20
A substantially square fiber aggregate of 0x200x3 (thickness) mm is prepared. This fiber assembly is made of needle felt, and is made of a mixture of synthetic fibers such as nylon 6/6 and polyester. The thickness of the fiber is approximately 3~
It is lOμm.
次に、固定化後の第１図に示すように、この繊維集積体
２のほぼ中央部の約１００〜１５０ｍｍの長方形部分に
、光合成細菌（紅色非硫黄細菌）３の液状水分散液（水
約１ｋｇに対してこの細菌約１ｍｊりの約６ｇをハケを
用いてこの繊維集積体２になるべく均一になるように塗
りつけた。これを１５℃の菌体培養器の冷暗状態で３〜
５日静置させて、光合成細菌３を固定化した。この結果
を第１図及び第２図に示す。なお第１図は写真の一部を
ほぼそのままの大きさでトレースしたもの、第２図は第
１図に示す光合成細菌３を固定化した繊維集積体部分の
顕微鏡写真（５０倍）をそのままトレースしたものであ
る。この光合成細菌３は第１図中の斜線部で示し、これ
が繊維２１の上及び間に着生、成育していることが示さ
れている。なお、この細胞の色は顕微鏡下では見ること
ができないので、第２図では光合成細菌の着生状態を図
示していない。しかし、菌体は細胞内に多量のバクテリ
オクロロフィルとカロチノイド（光合成色素）を含んで
いるので、集積体表面全体としては第１図図示のように
赤色に色づいて見える。Next, as shown in FIG. 1 after immobilization, a liquid aqueous dispersion of photosynthetic bacteria (purple non-sulfur bacteria) 3 (water Approximately 6 g of this bacteria (approximately 1 mj) per approximately 1 kg was applied to the fiber aggregate 2 using a brush so as to be as uniform as possible.
The photosynthetic bacteria 3 were immobilized by allowing the plate to stand for 5 days. The results are shown in FIGS. 1 and 2. Figure 1 is a trace of a part of the photograph at almost the same size, and Figure 2 is a trace of a micrograph (50x magnification) of the fiber aggregate portion with immobilized photosynthetic bacteria 3 shown in Figure 1. This is what I did. This photosynthetic bacterium 3 is shown by the hatched area in FIG. 1, and it is shown that it is attached and growing on and between the fibers 21. Since the color of these cells cannot be seen under a microscope, the epiphytic state of photosynthetic bacteria is not illustrated in FIG. However, since the bacterial cells contain large amounts of bacteriochlorophyll and carotenoids (photosynthetic pigments), the entire surface of the aggregate appears red, as shown in Figure 1.
上記のハケ塗りではほぼ均一に塗布されているか、やや
非塗布部分もあり、これは地色の白色を示している。こ
のように、光合成細菌３が繊維集積体２に容易かつ確実
に固定化されている。In the above brush application, the paint is applied almost uniformly, or there are some areas where it is not applied, which indicates the white background color. In this way, the photosynthetic bacteria 3 are easily and reliably immobilized on the fiber aggregate 2.
（２）フィルターとしての利用実験
次いで、この光合成細菌固定化繊維集積体１を微生物フ
ィルターとして利用した実験を行った。(2) Experiment of use as a filter Next, an experiment was conducted in which this photosynthetic bacteria-immobilized fiber aggregate 1 was used as a microbial filter.
まず、大きさ約１ （巾）×５ （長さ）×１ （高さ
）ｍの水槽４の上部に濾過部８を配置した。この濾過部
８内には上記光合成細菌固定化繊維集積体１を外枠１１
で支持しフィルターとして配置、固定されている。ポン
プ７の作動により、水槽４内に配置された吸水部５及び
これに接続する吸水管６を介して、吐出管９に接続する
ノズル１０から上記繊維集積体ｌの表面に、水槽４内の
水が吐出される。なおポンプ７の吐出量は約６１７分で
ある。そしてこの繊維集積体ｌを濾過された水が水槽４
内に循環される。First, the filtration section 8 was placed on the top of the water tank 4 having a size of approximately 1 (width) x 5 (length) x 1 (height) m. The above-mentioned photosynthetic bacteria-immobilized fiber aggregate 1 is placed in the outer frame 11 in the filter section 8.
It is supported and placed as a filter and fixed. By the operation of the pump 7, the water in the water tank 4 is applied to the surface of the fiber aggregate l from the nozzle 10 connected to the discharge pipe 9 through the water suction part 5 arranged in the water tank 4 and the water suction pipe 6 connected thereto. Water is discharged. Note that the discharge amount of the pump 7 is approximately 617 minutes. The water that has been filtered through this fiber aggregate is then collected in a water tank 4.
circulated within.
この水槽４内に、水約１トン及び大きさ約３００ｍｍの
アメリカンロブスタ−８匹を入れて、飼育した。Approximately 1 ton of water and 8 American lobsters each having a size of approximately 300 mm were placed in this aquarium 4 and raised.
２〜３日使用後のフィルターを観察した所、使用前と比
べて、より均一に広がった赤色を示したので、光合成細
菌が繊維上及び間に着生し、使用によりこのｗｉ菌が脱
離していないことを示している。なお、この濾過面は、
赤色を示すと同時に、残餌等の濾過物を示す黒色又は褐
色を示している。When we observed the filter after 2 to 3 days of use, it showed a more evenly spread red color compared to before use, indicating that photosynthetic bacteria had settled on and between the fibers, and that the wi bacteria had detached from the filter after use. It shows that it is not. In addition, this filtration surface is
At the same time, it shows a red color, and at the same time shows a black or brown color indicating filtrate such as leftover bait.
一方、比較のために光合成細菌が固定化されていない同
形状の繊維集積体を同様の飼育水槽において飼育した。On the other hand, for comparison, fiber aggregates of the same shape without immobilized photosynthetic bacteria were reared in a similar rearing tank.
この両者を比較すると、約２日を経過すると比較例では
目詰まりが起き始め、循環水の流通が良くないが、実施
例ではそのようなことはなかった。また水槽内の水も実
施例と比べると比較例は、濁っている。更に、約３日連
続して飼育すると、比較例の方は実施例と比べて、悪臭
がし始めたが、実施例では悪臭はしなかった。Comparing the two, the Comparative Example started to become clogged after about two days and the circulating water did not flow well, but this did not occur in the Example. Furthermore, the water in the water tank was also cloudy in the comparative example compared to the example. Furthermore, after being kept for about 3 consecutive days, the Comparative Example started to emit a bad odor compared to the Example, but the Example did not emit any bad odor.
また、本実施例では、フィルターを取り替えないでその
まま継続して１２０日間連続使用した所、海水を取り替
えなくても飼育することができた。従来の濾過方法では
、除外物（糞等）や残餌の分解が十分でないので、収容
されている個体数にもよるが上記のように２〜３日で目
詰まりゃ水の濁りや悪臭を発する。従ってフィルターを
頻繁に取り替える必要が生じるし、たとえ頻繁に取り替
えても水質の保全が十分でないので、海水を取り替える
必要がある。しかし本実施例では、除外物等から生じる
有害なアンモニア、硫化水素を取込み水中の窒素分を少
なくし、代謝機能が高まり水質浄化が促進される。従っ
て、そのまま、１２０日間という長期間海水を取り替え
ずに飼育することができたのである。Furthermore, in this example, when the filter was used continuously for 120 days without replacing it, it was possible to raise the fish without replacing the seawater. With conventional filtration methods, the decomposition of excluded substances (feces, etc.) and leftover food is not sufficient, so if the filter becomes clogged within 2 to 3 days as described above, depending on the number of individuals housed, the water becomes cloudy and the odor becomes bad. emanate. Therefore, it becomes necessary to replace the filter frequently, and even if the filter is replaced frequently, the water quality is not sufficiently maintained, so the seawater needs to be replaced. However, in this embodiment, harmful ammonia and hydrogen sulfide generated from excluded substances are taken in to reduce the nitrogen content in the water, thereby increasing metabolic function and promoting water purification. Therefore, it was possible to raise them as they were for a long period of 120 days without changing the seawater.
以上において、本実施例の光合成細菌固定化繊維集積体
を微生物フィルターとして用いると、悪臭がなく又排水
処理も有効且つ確実に行われ、フィルターの目詰まりも
起きなく海水を取り替える必要もない。In the above, when the photosynthetic bacteria-immobilized fiber aggregate of this example is used as a microbial filter, there is no bad odor, wastewater treatment is performed effectively and reliably, the filter is not clogged, and there is no need to replace the seawater.
なお、本発明においては、上記具体的実施例に示すもの
に限られず、目的、用途に応じて本発明の範囲内で種々
変更した実施例とすることができる。即ち、使用する繊
維集積体の形状、大きさ、厚さ、密度更には固定する光
合成細菌の量等は目的及び用途により種々選択できる。Note that the present invention is not limited to what is shown in the above-mentioned specific examples, but can be variously modified within the scope of the present invention depending on the purpose and use. That is, the shape, size, thickness, density, and amount of photosynthetic bacteria to be immobilized of the fiber aggregate to be used can be variously selected depending on the purpose and use.
光合成細菌の塗布方法も、他にスプレー塗り、ローラ申
り、浸漬塗り等を用いることもでき、細菌の濃度によっ
ては、より均一に塗布することもできる。使用する濾過
装置も種々の態様とすることもできる。例えば、水槽の
形状、大きさ、使用水量、真水又は海水の有無又はポン
プの容量等は目的、用途により種々設定する。濾過部も
水槽の一端部に固定させても良いし、水槽の一下端部か
ら使用水を導出してこれをポンプで濾過部まで搬送する
。こともできる。また、フィルターを複数枚重ねても良
いし、フィルターの少なくとも下端部に支持体を配置し
ても良いし、種々のフィルターの配置、固定方法を用い
ることができる。。Other methods for applying the photosynthetic bacteria include spray coating, roller coating, dipping coating, etc., and depending on the concentration of the bacteria, more uniform coating can be achieved. The filtration device used can also be in various forms. For example, the shape and size of the water tank, the amount of water used, the presence or absence of fresh water or seawater, the capacity of the pump, etc. are variously set depending on the purpose and use. The filtration part may also be fixed to one end of the water tank, or the water to be used is drawn out from one lower end of the tank and transported to the filtration part by a pump. You can also do that. Further, a plurality of filters may be stacked, a support body may be arranged at least at the lower end of the filter, and various methods of arranging and fixing the filters can be used. .
第１図は光合成細菌固定化繊維集積体の説明斜視図、第
２図は第１図に示す光合成細菌固定化繊維集積体の一部
拡大説明図、第３図は光合成細菌固定化ＩＪＩ！維集積
体をフィルターとして用いた実験装置の説明断面図であ
る。
１；光合成細菌固定化繊維集積体、２；繊維集積体、２
１；繊維、３；光合成細菌、４；水槽、８；濾過部。Fig. 1 is an explanatory perspective view of a photosynthetic bacteria-immobilized fiber aggregate, Fig. 2 is a partially enlarged explanatory view of the photosynthetic bacteria-immobilized fiber aggregate shown in Fig. 1, and Fig. 3 is a photosynthetic bacteria-immobilized IJI! FIG. 2 is an explanatory cross-sectional view of an experimental device using a fiber aggregate as a filter. 1; Photosynthetic bacteria immobilized fiber aggregate, 2; Fiber aggregate, 2
1; fiber, 3; photosynthetic bacteria, 4; water tank, 8; filtration section.
Claims (1)
び該繊維間に固定された光合成細菌と、から成ることを
特徴とする光合成細菌固定化繊維集積体。(1) A photosynthetic bacteria-immobilized fiber aggregate comprising a fiber aggregate and photosynthetic bacteria immobilized on and between the fibers constituting the fiber aggregate.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP63165676A JPH0217997A (en) | 1988-07-02 | 1988-07-02 | Photosynthesizing-bacterium immobilized fiber accumulation |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP63165676A JPH0217997A (en) | 1988-07-02 | 1988-07-02 | Photosynthesizing-bacterium immobilized fiber accumulation |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPH0217997A true JPH0217997A (en) | 1990-01-22 |
Family
ID=15816918
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP63165676A Pending JPH0217997A (en) | 1988-07-02 | 1988-07-02 | Photosynthesizing-bacterium immobilized fiber accumulation |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH0217997A (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US5711731A (en) * | 1995-09-26 | 1998-01-27 | Shimano, Inc. | Bicycle rear derailleur jockey pulley |
Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS55162394A (en) * | 1979-06-05 | 1980-12-17 | Sumitomo Chem Co Ltd | Treatment of reducible inorg. sulfur containing waste water |
| JPS61220791A (en) * | 1985-03-26 | 1986-10-01 | Toto Ltd | Microbe-immobilizing carrier for waste water treating apparatus |
| JPS62155990A (en) * | 1985-12-27 | 1987-07-10 | Takenaka Komuten Co Ltd | Plate-shaped bioreactor |
-
1988
- 1988-07-02 JP JP63165676A patent/JPH0217997A/en active Pending
Patent Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS55162394A (en) * | 1979-06-05 | 1980-12-17 | Sumitomo Chem Co Ltd | Treatment of reducible inorg. sulfur containing waste water |
| JPS61220791A (en) * | 1985-03-26 | 1986-10-01 | Toto Ltd | Microbe-immobilizing carrier for waste water treating apparatus |
| JPS62155990A (en) * | 1985-12-27 | 1987-07-10 | Takenaka Komuten Co Ltd | Plate-shaped bioreactor |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US5711731A (en) * | 1995-09-26 | 1998-01-27 | Shimano, Inc. | Bicycle rear derailleur jockey pulley |
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