JPH0471696A - Method for purifying water - Google Patents
Method for purifying waterInfo
- Publication number
- JPH0471696A JPH0471696A JP18067790A JP18067790A JPH0471696A JP H0471696 A JPH0471696 A JP H0471696A JP 18067790 A JP18067790 A JP 18067790A JP 18067790 A JP18067790 A JP 18067790A JP H0471696 A JPH0471696 A JP H0471696A
- Authority
- JP
- Japan
- Prior art keywords
- water
- light
- region
- purified
- light source
- 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
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims abstract description 76
- 238000000034 method Methods 0.000 title claims abstract description 12
- 238000000746 purification Methods 0.000 claims abstract description 16
- 241000894006 Bacteria Species 0.000 claims abstract description 12
- 230000001678 irradiating effect Effects 0.000 claims abstract description 4
- 239000008213 purified water Substances 0.000 claims description 14
- 230000000243 photosynthetic effect Effects 0.000 claims description 11
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 abstract description 10
- 229910052760 oxygen Inorganic materials 0.000 abstract description 10
- 239000001301 oxygen Substances 0.000 abstract description 10
- 241001148470 aerobic bacillus Species 0.000 abstract description 4
- 230000029553 photosynthesis Effects 0.000 abstract description 4
- 238000010672 photosynthesis Methods 0.000 abstract description 4
- 239000010802 sludge Substances 0.000 description 6
- 230000000052 comparative effect Effects 0.000 description 5
- 230000007423 decrease Effects 0.000 description 5
- 239000000126 substance Substances 0.000 description 4
- 241000251468 Actinopterygii Species 0.000 description 3
- 241000190831 Chromatium Species 0.000 description 3
- 241000233866 Fungi Species 0.000 description 3
- 241000190932 Rhodopseudomonas Species 0.000 description 3
- 239000005416 organic matter Substances 0.000 description 3
- 241000194107 Bacillus megaterium Species 0.000 description 2
- 241000195628 Chlorophyta Species 0.000 description 2
- 241000192700 Cyanobacteria Species 0.000 description 2
- 241000191001 Thiocapsa Species 0.000 description 2
- 238000004140 cleaning Methods 0.000 description 2
- 230000003247 decreasing effect Effects 0.000 description 2
- 238000009434 installation Methods 0.000 description 2
- 230000002503 metabolic effect Effects 0.000 description 2
- 230000007306 turnover Effects 0.000 description 2
- 241000206761 Bacillariophyta Species 0.000 description 1
- 241000459479 Capsula Species 0.000 description 1
- 241001425707 Chlorobiaceae Species 0.000 description 1
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical compound S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 description 1
- 241001134684 Rubrivivax gelatinosus Species 0.000 description 1
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 1
- 239000013043 chemical agent Substances 0.000 description 1
- 238000000354 decomposition reaction Methods 0.000 description 1
- 230000006866 deterioration Effects 0.000 description 1
- 230000002542 deteriorative effect Effects 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 229910000037 hydrogen sulfide Inorganic materials 0.000 description 1
- 230000013011 mating Effects 0.000 description 1
- 230000004060 metabolic process Effects 0.000 description 1
- 244000005700 microbiome Species 0.000 description 1
- 150000007524 organic acids Chemical class 0.000 description 1
- 235000005985 organic acids Nutrition 0.000 description 1
- 231100000719 pollutant Toxicity 0.000 description 1
- 230000001932 seasonal effect Effects 0.000 description 1
- 238000005507 spraying Methods 0.000 description 1
- 229910052717 sulfur Inorganic materials 0.000 description 1
- 239000011593 sulfur Substances 0.000 description 1
- 231100000331 toxic Toxicity 0.000 description 1
- 230000002588 toxic effect Effects 0.000 description 1
- 231100000419 toxicity Toxicity 0.000 description 1
- 230000001988 toxicity Effects 0.000 description 1
- 238000003911 water pollution Methods 0.000 description 1
Landscapes
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
Abstract
Description
【発明の詳細な説明】 [産業上の利用分野] 本発明は溜池、養魚場、湖沼等の水浄化法である。[Detailed description of the invention] [Industrial application field] The present invention is a water purification method for ponds, fish farms, lakes, etc.
[従来の技術]
溜池や養魚場、湖沼等の水の入れ替わりの少ない水域、
特にそれらの深層部では水中の酸素が欠乏し、好気性菌
による有機物の分解能が低下、底泥化が進行して水質が
低下している。[Conventional technology] Water areas with low water turnover, such as reservoir ponds, fish farms, lakes, etc.
Particularly in these deep layers, water quality is decreasing due to a lack of oxygen in the water, a decline in the ability of aerobic bacteria to decompose organic matter, and progress to siltation of the bottom.
上記水質の低下は衛生上問題であり、外観も悪いためこ
れを防止するために、例えば水の入れ替えや清掃、薬剤
等の散布が行われている。The aforementioned deterioration in water quality is a sanitary problem and also causes a poor appearance, so to prevent this, for example, water replacement, cleaning, and spraying of chemicals are carried out.
[発明が解決しようとする課題]
しかしながら水の入れ替えや清掃といった作業は容積の
大きな湖沼などでは人手や費用がかかり定期的に行うに
は経済的に問題がある。[Problems to be Solved by the Invention] However, in large lakes and ponds, operations such as water replacement and cleaning require labor and expense, and are economically problematic to perform on a regular basis.
また化学的な薬剤は毒性等危険性が高く、分解しにくい
ものが多く、最悪の場合には水中の微生物等を死滅させ
、水中の生態系を変えてしまう恐れもある。In addition, many chemical agents are highly dangerous due to their toxicity and are difficult to decompose, and in the worst case scenario, they can kill microorganisms in the water and change the aquatic ecosystem.
以上の様に低コストで簡単な水の浄化法が要望されてい
るのが現状である。As described above, there is currently a demand for a low-cost and simple water purification method.
[課題を解決するための手段]
本発明は、上記の問題を解決し、低コストで簡単な水浄
化法を提供するものである。[Means for Solving the Problems] The present invention solves the above problems and provides a low-cost and simple water purification method.
すなわち本発明は、目的とする浄化水域に光合成菌を添
加し、かつ20m以内に光源を設置し、浄化水域に光を
照射することを特徴とする特許法である。That is, the present invention is a patented method characterized by adding photosynthetic bacteria to a targeted purified water area, installing a light source within 20 m, and irradiating the purified water area with light.
以下、本発明の構成を詳細に説明する。Hereinafter, the configuration of the present invention will be explained in detail.
本発明の水浄化法を利用する浄化水域は溜池、養魚場、
湖沼等であり、例えばBOD(Bi。Purified water areas using the water purification method of the present invention include ponds, fish farms,
Lakes and marshes, for example, BOD (Bi.
chemical Oxigen Demand:
生化学的酸素要求量)やCOD (Chemical
Oxigen Demand:化学的酸素要求量)
の値が高い水域である。Chemical Oxygen Demand:
Biochemical oxygen demand) and COD (Chemical
Oxygen Demand: chemical oxygen demand)
It is a body of water with a high value of
本発明に用いる光合成菌は例えばロドシュードモナス(
Rhodopseudomonas)属のロドスピリラ
ーシエ(rhodospiril 1 aceae)、
クロマチアーシエ(chr。The photosynthetic bacteria used in the present invention are, for example, Rhodopseudomonas (
rhodospiral 1 aceae of the genus Rhodopseudomonas,
Chromatiasis (chr.
matiaceae)、クロロビアーシエ(chlor
obiaceae)+カブシュラータ(capsula
ta)、クロマチウム(chromatium)、ゼオ
チノサ(gelatinosa)や紅色硫黄細菌のチオ
カブサ(thiocapsa)から選択される1種又は
2種以上の混合系であり、好ましくは、カブシュラータ
とクロマチウム、ゼラチノサとチオカブサの組み合わせ
がBOD源となる有機酸と毒性の強い硫化水素を同時に
除去できる点で好ましい。又、光合成菌とそれ以外との
菌との組み合わせも蓄積した有機へどろを分解浄化する
点でさらに好ましく、具体的にはクロマチウムと非光合
成菌のバチラス メガテリウム(Bac i 11 u
smegaterium)の組み合わせを用いることが
望ましい。これら菌類の添加量は菌の種類や浄化水域の
容積、水質の程度により異なるが、好ましくは(菌の乾
燥重量/浄化水域の容積)として10/日/トン以上で
ある。これらをなるべ(偏りのない様に万遍無(浄化水
域に添加する。matiaceae), chlorobiaceae
obiaceae) + capsula
ta), chromatium, gelatinosa, and the purple sulfur bacterium thiocapsa. Preferably, combinations of turnipulata and chromatium, or combinations of gelatinosa and thiocapsa are used. This method is preferable because organic acids, which are BOD sources, and highly toxic hydrogen sulfide can be removed at the same time. Furthermore, a combination of photosynthetic bacteria and other bacteria is more preferable in terms of decomposing and purifying accumulated organic sludge; specifically, a combination of photosynthetic bacteria and non-photosynthetic bacteria Bacillus megaterium (Bacillus megaterium) is preferable.
It is desirable to use a combination of smegaterium. The amount of these fungi added varies depending on the type of fungi, the volume of the purified water area, and the water quality, but is preferably 10/day/ton or more (dry weight of bacteria/volume of the purified water area). Add these to the purified water area as evenly as possible.
次に、本発明に用いる光源は、太陽光線としての働きを
有するため、その波長は300〜900nm、少なくと
も500〜800nmが必要である。Next, since the light source used in the present invention functions as sunlight, its wavelength must be 300 to 900 nm, or at least 500 to 800 nm.
本発明において光源の設置場所は浄化水域から20m以
内であり、ここで言う浄化水域とは浄化を目的とする水
圏全域を示し、従って水質がそれほど低下しておらず水
の透明度の高い場合は水面から6m以内の水上に設置す
れば良(、逆に水質が低く透明度が低い場合には、水面
での光の反射により水中への光の照射量が減少するため
水中即ち浄化水域の中に設置するのが好ましい。In the present invention, the installation location of the light source is within 20 m from the purified water area, and the purified water area here refers to the entire aquatic area for the purpose of purification. (Conversely, if the water quality is low and transparency is low, the amount of light irradiated into the water will decrease due to the reflection of light on the water surface, so install it underwater, that is, in a purified water area.) It is preferable to do so.
光源の強さは浄化水域の水質により異なるが少なくとも
50ルクス以上は必要である。ここで言う50ルクスと
は光源に一番近い位置での照度であり、光源が水中に置
かれた場合は直接水が光源に触れる事になるので光源の
光が放出される部分を覆っている透明部材上の照度を言
う。浄化水域の水の透明度が極端に低い場合には光が全
体、特に内部にまで届きに(いので複数の光源を設置し
、浄化の進行により適宜設置場所を変えれば良い。The intensity of the light source varies depending on the water quality of the purified water area, but it must be at least 50 lux. The 50 lux here refers to the illuminance at the position closest to the light source, and if the light source is placed underwater, the water will come into direct contact with the light source, so cover the part of the light source that emits light. Refers to the illuminance on a transparent member. If the clarity of the water in the purified water area is extremely low, the light will need to reach the entire area, especially the interior (so it is best to install multiple light sources and change the installation locations as appropriate as the purification progresses.
本発明において光の照射時間は、少なくとも太陽光線の
照射しない夜間であるが、悪天候や日没直前等浄化水域
への太陽光線の照度が50ルクス未満の時間にも適宜照
射を行う。照射時間は季節ごとの日照時間の変化や天候
により異なるが、1日に2時間以上は必要であり、好ま
しくは6時間以上照射する。光の照射は連続でも断続的
でも良い。In the present invention, the light irradiation time is at least at night when no sunlight is irradiated, but the irradiation is also carried out appropriately during bad weather or when the illuminance of sunlight on the purified water area is less than 50 lux, such as just before sunset. The irradiation time varies depending on seasonal changes in sunlight hours and the weather, but it is necessary to irradiate for at least 2 hours a day, preferably for 6 hours or more. Irradiation of light may be continuous or intermittent.
[作 用]
水中に棲息する光合成菌等の菌類、あおこ等の単細胞生
物、原生動物、珪藻、緑藻類は、光のある昼間は生活活
動が盛んで、その代謝活動により水の浄化が進行する。[Function] Fungi such as photosynthetic bacteria, single-celled organisms such as blue-green algae, protozoa, diatoms, and green algae that live in water are active during the day when there is light, and their metabolic activities progress in water purification. .
ところが光がなくなる夜間や天候が悪(光の照射量の少
ない昼間は代謝活動が弱まり、浄化が進行しな(なる。However, at night when there is no light or when the weather is bad (daytime when the amount of light irradiation is low), metabolic activity weakens and purification does not proceed.
しかも光合成菌やあおこ等の単細胞、緑藻等が光合成を
行わなくなるために酸素が発生せず、水中の溶存酸素量
が低下する。従って昼間でも光の当たらない水域や水の
入れ替わりの少ない水域ではこの溶存酸素量が極端に低
下し、上記生物系、特に好気性菌による有機物の分解代
謝が進まず汚濁物質として蓄積し、水の浄化を進行させ
ている生物自体も減少している。Moreover, since photosynthetic bacteria, single cells such as blue-green algae, and green algae no longer perform photosynthesis, no oxygen is generated, and the amount of dissolved oxygen in the water decreases. Therefore, in water areas that are not exposed to sunlight even during the day or water areas that have little water turnover, the amount of dissolved oxygen is extremely low, and the above biological systems, especially aerobic bacteria, do not decompose and metabolize organic matter, which accumulates as pollutants and accumulates in water. The organisms that carry out the purification process are also decreasing in number.
本発明はこうした水質の低下した水域に先ず光合成菌を
添加し、さらに夜間や悪天候時に人工的照明により光を
照射することによって光の照射時間を増加させ光合成を
促進させる。その結果水中の溶存酸素量が増加し、好気
性菌やその他の生物による有機物の分解代謝も活発にな
り、水の浄化が進行する。In the present invention, photosynthetic bacteria are first added to water bodies with reduced water quality, and then artificial lighting is applied at night or during bad weather to increase the light irradiation time and promote photosynthesis. As a result, the amount of dissolved oxygen in the water increases, the decomposition and metabolism of organic matter by aerobic bacteria and other organisms becomes active, and water purification progresses.
[実施例]
以下実施例により本発明の具体的な実施態様を示すが本
発明がこれに限定されるものではない。[Examples] Specific embodiments of the present invention will be shown below through Examples, but the present invention is not limited thereto.
比較例1
平均水位時の面積400m2.最深部2m、容積550
にρの池の水底に厚さ10cmの底泥が溜っていた。こ
の池の水面全体に500ルクスの光が照射される様に光
源を9個設置し、1日に6時間ずつ光を照射した。5週
間観察を続けたが水質はほとんど変化しなかった。Comparative Example 1 Area at average water level: 400 m2. Deepest part 2m, volume 550
On the bottom of Rho's pond, there was mud 10 cm thick. Nine light sources were installed so that the entire water surface of this pond was irradiated with 500 lux of light, and the light was irradiated for 6 hours a day. Although observation was continued for 5 weeks, there was almost no change in water quality.
比較例2
比較例1の池の光源を取り除き、光合成菌ロドシュード
モナス ゼラチノサを乾燥重量にして500g水面全体
に散布して水質の変化を観察した。しかしながら、5週
間を経過しても水質に変化が見られなかった。Comparative Example 2 The light source of the pond in Comparative Example 1 was removed, and 500 g of the photosynthetic bacterium Rhodopseudomonas gelatinosa (dry weight) was sprinkled over the entire water surface, and changes in water quality were observed. However, no change in water quality was observed even after 5 weeks had passed.
実施例1
比較例2の池に比較例1と同じ光源を設置し、同様に光
を照射した。その結果3週間後には汚泥が減少し始め、
水の透明度も向上した。さらに観察したところ、10週
間後には汚泥がほとんど無くなったため、光源の数を減
らし、水面上で200ルクスとなる様にして水質の観察
を続けたが、汚泥が発生することもな(、水質は良好に
保たれたままであった。Example 1 The same light source as in Comparative Example 1 was installed in the pond of Comparative Example 2, and light was irradiated in the same manner. As a result, sludge started to decrease after 3 weeks.
Water clarity has also improved. Further observation revealed that the sludge had almost disappeared after 10 weeks, so we continued to observe the water quality by reducing the number of light sources and setting the light to 200 lux above the water surface, but no sludge was generated (and the water quality was It remained in good condition.
実施例2
実施例1とほとんど同じ容積で、しかも水質の汚濁状況
も同様の池に光合成菌ロドシュードモナス 力ブシュラ
ータを乾燥重量にして100gと、クロマチウムを乾燥
重量にして100g水面全体に万遍な(散布した。実施
例1と同様に光を照射したところ、7日後には汚泥が減
り始め、3週間後には全く汚泥が無くなり、水の濁りも
ほとんど無くなった。Example 2 In a pond with almost the same volume as in Example 1 and with similar water pollution conditions, 100 g of the photosynthetic bacterium Rhodopseudomonas bushulata and 100 g of Chromatium (dry weight) were distributed evenly over the entire water surface ( When irradiated with light in the same manner as in Example 1, the sludge began to decrease after 7 days, and after 3 weeks, there was no sludge at all, and the water was almost completely turbid.
[発明の効果]
以上説明した通り、本発明の水浄化法によると、池や湖
沼等の大規模な水域の水の浄化を簡単にしかも安価に行
うことができる。しかも本発明の水浄化法により水を浄
化した後は、適宜光を照射しておくだけで、常に水中の
生物による水の浄化を促進するので以後、水質が悪化す
る心配も無(非常に経済的である。[Effects of the Invention] As explained above, according to the water purification method of the present invention, water in large-scale water bodies such as ponds and lakes can be easily and inexpensively purified. Moreover, after water has been purified using the water purification method of the present invention, simply by irradiating it with light as appropriate, water purification by organisms in the water will be promoted, so there is no need to worry about water quality deteriorating (very economical). It is true.
出願人 株式会社吉田総合研究所Applicant: Yoshida Research Institute Co., Ltd.
Claims (2)
20m以内に少なくとも1個の50ルクス以上の光源を
設置し、少なくとも夜間に2時間/日以上光を照射する
ことを特徴とする水浄化法。(1) Water characterized by adding photosynthetic bacteria to the purified water area, and installing at least one light source of 50 lux or more within 20 m from the purified water area, and irradiating the water with light for at least 2 hours/day at least at night. Purification method.
とを特徴とする請求項(1)記載の水浄化法。(2) The water purification method according to claim (1), wherein the wavelength of the irradiated light is 300 to 900 nm.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP18067790A JPH0471696A (en) | 1990-07-10 | 1990-07-10 | Method for purifying water |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP18067790A JPH0471696A (en) | 1990-07-10 | 1990-07-10 | Method for purifying water |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPH0471696A true JPH0471696A (en) | 1992-03-06 |
Family
ID=16087377
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP18067790A Pending JPH0471696A (en) | 1990-07-10 | 1990-07-10 | Method for purifying water |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH0471696A (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN107868760A (en) * | 2016-12-29 | 2018-04-03 | 广西民族大学 | A kind of cultural method of Rhodopseudomonas palustris |
Citations (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS575889B2 (en) * | 1973-11-27 | 1982-02-02 | ||
| JPS59199099A (en) * | 1983-04-25 | 1984-11-12 | Ichigoro Sekine | Process and apparatus for purifying filthy water utilizing photosynthetic bioslime |
-
1990
- 1990-07-10 JP JP18067790A patent/JPH0471696A/en active Pending
Patent Citations (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS575889B2 (en) * | 1973-11-27 | 1982-02-02 | ||
| JPS59199099A (en) * | 1983-04-25 | 1984-11-12 | Ichigoro Sekine | Process and apparatus for purifying filthy water utilizing photosynthetic bioslime |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN107868760A (en) * | 2016-12-29 | 2018-04-03 | 广西民族大学 | A kind of cultural method of Rhodopseudomonas palustris |
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