JPS593699B2 - Biological treatment sludge discrimination device - Google Patents
Biological treatment sludge discrimination deviceInfo
- Publication number
- JPS593699B2 JPS593699B2 JP5602878A JP5602878A JPS593699B2 JP S593699 B2 JPS593699 B2 JP S593699B2 JP 5602878 A JP5602878 A JP 5602878A JP 5602878 A JP5602878 A JP 5602878A JP S593699 B2 JPS593699 B2 JP S593699B2
- Authority
- JP
- Japan
- Prior art keywords
- piston
- pipe
- water
- sludge
- detector
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired
Links
- 239000010802 sludge Substances 0.000 title claims description 15
- 238000001514 detection method Methods 0.000 claims description 18
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 18
- 244000005700 microbiome Species 0.000 claims description 6
- 230000001678 irradiating effect Effects 0.000 claims description 2
- 230000033001 locomotion Effects 0.000 description 4
- 241000700141 Rotifera Species 0.000 description 3
- 238000004140 cleaning Methods 0.000 description 3
- 230000005284 excitation Effects 0.000 description 3
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- 241000223782 Ciliophora Species 0.000 description 2
- 238000005273 aeration Methods 0.000 description 2
- 238000006243 chemical reaction Methods 0.000 description 2
- 230000007423 decrease Effects 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 238000005086 pumping Methods 0.000 description 2
- 238000005070 sampling Methods 0.000 description 2
- 238000002834 transmittance Methods 0.000 description 2
- 241000233866 Fungi Species 0.000 description 1
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical group [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 1
- 230000005856 abnormality Effects 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 230000001580 bacterial effect Effects 0.000 description 1
- 230000005540 biological transmission Effects 0.000 description 1
- 238000009395 breeding Methods 0.000 description 1
- 230000001488 breeding effect Effects 0.000 description 1
- 230000000052 comparative effect Effects 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 238000005259 measurement Methods 0.000 description 1
- 230000000813 microbial effect Effects 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 235000015097 nutrients Nutrition 0.000 description 1
- 230000003287 optical effect Effects 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 230000002250 progressing effect Effects 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 239000010865 sewage Substances 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 239000012780 transparent material Substances 0.000 description 1
Landscapes
- Investigating Materials By The Use Of Optical Means Adapted For Particular Applications (AREA)
- Treatment Of Biological Wastes In General (AREA)
Description
【発明の詳細な説明】
本発明は汚水の生物処理による浄化処理を効率を高め能
率的に行なうために汚泥状態を判別する装置に関する。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to an apparatus for determining the state of sludge in order to improve the efficiency and perform biological purification treatment of sewage.
生物処理槽において、過曝気が行なわれると活性汚泥の
微細化、窒素の酸化によるPH低下があり、沈澱汚泥の
まき上げなどの現象が生じ正常運転を阻害する。In a biological treatment tank, if excessive aeration is performed, the activated sludge becomes finer, the pH decreases due to nitrogen oxidation, and phenomena such as settling sludge being thrown up occur, which impedes normal operation.
また糸状菌が増殖すると活性汚泥が沈澱せずにバルキン
グ現象が起る。このような異常を防ぐには薬剤を投入し
たサ曝気量を制御する。活性汚泥力徘常に少ない時、あ
るいは一般的に高負荷になつたとき、空気量を減少させ
たク5BOD源の投入などが行われる。このような生物
処理においては、生物の状態、活性状態等を常に監視し
ながら制御することが必要となる。本発明はこのような
目的のために提案されたもので、生物処理槽内処理水が
流通するパイプと、10該パイプ内に嵌合して水を汲み
上げ且つ内壁面をクリーニングするピストンと、該ピス
トンを往復駆動する装置と、前記ピストンが往復する部
分のパイプの一部分を検出部として一方にレーザーまた
はソフトX線の照射装置、他方の検出器とから15成り
、ピストンのポンプ作用によつて汲み取わクリーニング
されたパイプ部分に貯えられた水中に光照射し、透過光
もしくは反射光を検出器で、検出すること、また検出器
を所定の角度移動させながら散乱光を検出することによ
り汚泥状態を判別20することを特徴とする。Furthermore, when filamentous fungi multiply, the activated sludge does not settle and a bulking phenomenon occurs. To prevent such abnormalities, the amount of aeration of the chemical-injected sample should be controlled. When the amount of activated sludge is constantly low, or when the load is generally high, a BOD source with a reduced amount of air is introduced. In such biological treatment, it is necessary to constantly monitor and control the condition, activity state, etc. of the organisms. The present invention was proposed for this purpose, and includes: a pipe through which treated water in a biological treatment tank flows; a piston that fits into the pipe to draw up water and clean the inner wall surface; It consists of a device for reciprocating a piston, a part of the pipe where the piston reciprocates as a detection part, a laser or soft X-ray irradiation device on one side, and a detector on the other side, and the pump is pumped by the pumping action of the piston. The state of the sludge is determined by irradiating light into the water stored in the pipe section that has been removed and cleaned, and detecting the transmitted or reflected light with a detector, and by detecting the scattered light while moving the detector at a predetermined angle. It is characterized by determining 20.
以下図面の一実施例により本発明を説明すると、第1図
において、1は活性汚泥処理槽の処理水をサンプリング
して流通させるパイプ、2はこのパイプ1内に嵌合する
ピストンで往復運動すること25によつて水を汲み取わ
、且つパイプ内壁面を摺動摩擦してクリーニングをする
。The present invention will be explained below with reference to an embodiment of the drawings. In Fig. 1, 1 is a pipe for sampling and distributing treated water in an activated sludge treatment tank, and 2 is a piston fitted in this pipe 1 for reciprocating motion. In step 25, the water is pumped out and the inner wall surface of the pipe is cleaned by sliding friction.
3は弁でピストンが上昇するときは弁を開き下降すると
き弁を閉じて水をポンプする。3 is a valve which opens the valve when the piston goes up and closes the valve when it goes down to pump water.
4はピストン2に連結する磁気鉄心で外部コイル5の励
磁によつて吸引移動L30励磁を解除するとバネ6によ
つて戻るよう、これがコイル5の間歇励磁によつて繰返
されピストン2が往復するようになる。Reference numeral 4 denotes a magnetic iron core connected to the piston 2. When the external coil 5 is energized, the magnetic core 4 attracts and moves L30, and when the excitation is released, it returns by the spring 6. This is repeated by the intermittent energization of the coil 5, so that the piston 2 reciprocates. become.
Tはピストン2が移動する部分のパイプ、即ち光透過性
透明材で構成された検出部9に一方からレーザーまたは
ソフトX35線を照射する装置、8は照射散乱光を検出
する検出器で、所定の角度0〜1800移動しながら角
度に対応する受光検出をする。即ち検出器8の移44q
−動は第2図のように照射装置8に照射される光線のパ
ィブ9内光点を中心にして円弧を画いて移動レ受光角度
に対して光度を検出し水中汚泥状態を判別できるように
してある。T is a device that irradiates a laser or soft X35 ray from one side to the pipe where the piston 2 moves, that is, a detection part 9 made of a light-transmitting transparent material; 8 is a detector that detects the irradiated scattered light; While moving through an angle of 0 to 1800, light reception corresponding to the angle is detected. That is, the movement 44q of the detector 8
- As shown in Fig. 2, the movement is made by drawing an arc around the light point in the pipe 9 of the light beam irradiated to the irradiation device 8, and detecting the luminous intensity with respect to the receiving angle, so that the state of underwater sludge can be determined. There is.
以上の装置によりピストン2を往復運動させる .,こ
とによつて水はバイブ1内を矢印の方向に汲み上げ移動
する。The above device causes the piston 2 to reciprocate. , the water is pumped up and moved inside the vibrator 1 in the direction of the arrow.
励磁コイル5を励磁したま\にするとピストン2は図示
状態を保ち、汲み上げた水は検出部9を満すから、こ\
に照射装置7からレーザーを照射すると、光は水中微生
物に当つて反,射し散乱し透過する。散乱光は微生物の
量とか微生物の種類、繊毛虫類、吸管虫類、鞭毛虫類、
根足虫類、輪虫類等色々の種類が混つているが、各各に
よつて反射散乱状態は異なv、散乱光を角度によつて検
出することによジ容易に量、種類の判1別ができる。検
出器8は検出部9を中心に0−180程度の回動移動が
でき、検出器8を移動させながら検出操作をすることに
よつて角度に対応する散乱光度を検出することができる
。検出信号は図示しないX,Yレコーダによつて記録す
れば水中の2汚泥状態が容易に判別できる。第3図は検
出角度に対する散乱光の強度をグラフすることによつて
微生物の繁殖状態を判別したもので、バクテリア量で2
x106/mlが5×105/mlよジもいずれの角度
に訃いても散乱光度が高2くなつている。If the excitation coil 5 is kept energized, the piston 2 will remain in the state shown in the figure, and the pumped water will fill the detection part 9.
When a laser is irradiated from the irradiation device 7, the light hits the microorganisms in the water and is reflected, scattered, and transmitted. Scattered light is determined by the amount of microorganisms, the types of microorganisms, ciliates, haustoria, flagellates,
There are various types of rhizopods, rotifers, etc., but the reflection and scattering state is different for each type.By detecting the scattered light at different angles, it is easy to determine the amount and type. 1. I can differentiate. The detector 8 can be rotated about 0 to 180 degrees around the detection part 9, and by performing a detection operation while moving the detector 8, it is possible to detect the scattered light intensity corresponding to the angle. If the detection signal is recorded by an X, Y recorder (not shown), the two states of sludge in the water can be easily distinguished. Figure 3 shows the state of microbial growth determined by graphing the intensity of scattered light against the detection angle.
When x106/ml is 5 x 105/ml, the scattered light intensity becomes high at any angle.
第4図はいずれも100μg/WLIの輪虫類と繊毛虫
類の散乱光度の分布状態を示L第5図はスボア一を含ん
だ水とバクテリア水との比較測定グラフである。このよ
うな各種グラフを予じめ用意しておくことによシ、これ
と運転中の3,処理水を検出した値と比較検討すること
によつて微生物の種類、混合状態、量等を検出すること
ができる。繁殖状態の判定には一番大きいサイズの輪虫
類を判別すれば、汚泥全体の増減状態を大凡判定でき、
これにもとずいて制御することにより安定した処理をす
ることができる。な訃勿論光検出は透過光を利用して透
過状態の変化によつて判定してもよい。しかして以上の
ようにして汚泥状態の検出判別を繰返すうち水中微生物
はサンプリング流通路のパイプ1壁面に付着し繁殖して
くる。FIG. 4 shows the distribution of scattered luminosity of rotifers and ciliates at 100 μg/WLI, and FIG. 5 is a comparative measurement graph of water containing Sboa and bacterial water. By preparing such various graphs in advance, the type, mixing state, amount, etc. of microorganisms can be detected by comparing these with the values detected in the treated water during operation. can do. To determine the breeding status, if you identify the largest rotifer, you can roughly determine the increase/decrease status of the sludge as a whole.
By controlling based on this, stable processing can be performed. Of course, optical detection may also be performed using transmitted light to determine a change in the transmission state. However, as the detection and determination of the sludge state is repeated as described above, the microorganisms in the water adhere to the wall surface of the pipe 1 of the sampling flow path and multiply.
多量に繁殖すれば検出部9の透光性も遮断され光による
検出ができなくなるが、前記ポンプ作用を働せるピスト
ン2はその往復運動を行ないながら検出部9の壁面を常
に摺動摩擦してクリーニングし光透過性を常に最良状態
に維持する。即ち検出部は特にピストン2が摺動する部
分に設けてあるからピストンは検出部のクリーニング作
用も兼用するわけで、これによう前記の検出判別を安定
に維持できることになる。If they grow in large numbers, the light transmittance of the detection part 9 will be blocked and detection by light will no longer be possible, but the piston 2, which performs the pumping action, constantly slides and rubs against the wall surface of the detection part 9 while performing its reciprocating motion, thereby cleaning the detection part 9. and always maintain the best light transmittance. That is, since the detecting section is particularly provided in the area where the piston 2 slides, the piston also serves as a cleaning function for the detecting section, and thus the above-mentioned detection discrimination can be stably maintained.
このように本発明は検出部をポンプのピストンによつて
クリーニングしながら汲み上げた水にレーザー、ンフト
X線を照射して反射、透過光を検出Lまた散乱光を検出
方向角度を変えながら検出し生物状態を判別するように
したから安定した判別が続けられ、目的の如理反応が目
的に進んでいるか、はずれているかを素早く検出し対応
制御u酸素量、反応栄養素の量、PH値、温度等を最適
条件に制御することができる。In this way, the present invention irradiates pumped water with a laser or an FT X-ray while cleaning the detection part with the piston of the pump, detects reflected and transmitted light, and detects scattered light while changing the detection direction angle. Since the biological state is determined, stable determination can be continued, and it can be quickly detected whether the desired reaction is progressing to the target or not, and the corresponding control u Oxygen amount, reaction nutrient amount, PH value, temperature etc. can be controlled to optimal conditions.
第1図は本発明の一実施例構成図、第2図はその一部の
詳細図、第3図乃至第5図は判別グラフ図である。
1はパイプ、2はピストン、3は弁、4は磁気鉄心、5
は励磁コイル、6はバネ、7は照射装置、8は検出器、
9は検出部である。FIG. 1 is a configuration diagram of an embodiment of the present invention, FIG. 2 is a detailed diagram of a part thereof, and FIGS. 3 to 5 are discrimination graphs. 1 is a pipe, 2 is a piston, 3 is a valve, 4 is a magnetic core, 5
is an excitation coil, 6 is a spring, 7 is an irradiation device, 8 is a detector,
9 is a detection section.
Claims (1)
プ内に嵌合して水を汲み上げ、且つ内壁面をクリーニン
グするピストンと、該ピストンを往復駆動する装置と、
前記ピストンが往復する部分のパイプの一部を検出部と
して一方にレーザーまたはソフトX線の照射装置、他方
の検出器とから成り、ピストンのポンプ作用によつて汲
み上げクリーニングされたパイプ部分に貯れられた水中
に光照射し検出器で検出することにより汚泥状態を判別
することを特徴とする生物処理汚泥判別装置。 2 検出器を所定の角度移動させながら水中微生物から
の散乱光を検出することを特徴とする特許請求の範囲第
1項に記載の生物処理汚泥判別装置。[Scope of Claims] 1. A pipe through which treated water in a biological treatment tank flows, a piston that fits into the pipe to draw up water and clean the inner wall surface, and a device for reciprocating the piston.
A part of the pipe where the piston reciprocates is used as a detection part, and consists of a laser or soft X-ray irradiation device on one side and a detector on the other. A biological treatment sludge discrimination device characterized by discriminating the state of sludge by irradiating light into water and detecting it with a detector. 2. The biologically treated sludge discrimination device according to claim 1, which detects scattered light from underwater microorganisms while moving a detector at a predetermined angle.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP5602878A JPS593699B2 (en) | 1978-05-11 | 1978-05-11 | Biological treatment sludge discrimination device |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP5602878A JPS593699B2 (en) | 1978-05-11 | 1978-05-11 | Biological treatment sludge discrimination device |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS54147093A JPS54147093A (en) | 1979-11-16 |
| JPS593699B2 true JPS593699B2 (en) | 1984-01-25 |
Family
ID=13015602
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP5602878A Expired JPS593699B2 (en) | 1978-05-11 | 1978-05-11 | Biological treatment sludge discrimination device |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS593699B2 (en) |
Families Citing this family (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS57106847A (en) * | 1980-12-24 | 1982-07-02 | Hitachi Ltd | Apparatus for detecting minute foreign matter |
-
1978
- 1978-05-11 JP JP5602878A patent/JPS593699B2/en not_active Expired
Also Published As
| Publication number | Publication date |
|---|---|
| JPS54147093A (en) | 1979-11-16 |
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