JP2012098066A - Water quality monitoring device - Google Patents

Water quality monitoring device Download PDF

Info

Publication number
JP2012098066A
JP2012098066A JP2010243846A JP2010243846A JP2012098066A JP 2012098066 A JP2012098066 A JP 2012098066A JP 2010243846 A JP2010243846 A JP 2010243846A JP 2010243846 A JP2010243846 A JP 2010243846A JP 2012098066 A JP2012098066 A JP 2012098066A
Authority
JP
Japan
Prior art keywords
light
water
water quality
abnormality
predetermined time
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.)
Granted
Application number
JP2010243846A
Other languages
Japanese (ja)
Other versions
JP5643055B2 (en
Inventor
Makoto Hosaka
誠 保坂
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
MEIKYO DENKI KK
Original Assignee
MEIKYO DENKI KK
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by MEIKYO DENKI KK filed Critical MEIKYO DENKI KK
Priority to JP2010243846A priority Critical patent/JP5643055B2/en
Publication of JP2012098066A publication Critical patent/JP2012098066A/en
Application granted granted Critical
Publication of JP5643055B2 publication Critical patent/JP5643055B2/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Classifications

    • 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
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A20/00Water conservation; Efficient water supply; Efficient water use
    • Y02A20/20Controlling water pollution; Waste water treatment

Abstract

PROBLEM TO BE SOLVED: To give an alarm by detecting abnormal water quality of raw water for water supply when the water is taken while avoiding an erroneous detection of abnormal water quality in response to a normal fish behavior.SOLUTION: A water quality monitoring device 1 includes: a water tank 2 in which a fish 10 swims under a condition where the raw water for water supply is supplied, whose quality to be monitored; a plurality of light-emitting/receiving devices 3 for irradiating a liquid phase in the water tank 2 with light and receiving light reflected from a reflector arranged across the water tank 2; and a determination section 41 for determining abnormal water quality in the water tank 2 based on an interception of the receiving light by the fish 10. Pairs of light-emitting/receiving devices 3a and 3b vertically arranged in the plurality of light-emitting/receiving devices 3 are provided so as to irradiate an underwater area close to the water surface in the water tank 2 with light. If the determination section 41 detects a plurality of interceptions of receiving light at any one pair of the pairs of light-emitting/receiving devices 3a and 3b within a predetermined time, it is determined that the interceptions occur by breathing of the fish 10 due to abnormal water quality in the water tank 2.

Description

本発明は毒性に敏感な魚類の挙動に基づき上水道の原水の水質を監視する監視装置に関する。   The present invention relates to a monitoring device for monitoring the quality of raw water in waterworks based on the behavior of fish sensitive to toxicity.

近時、水道水源の汚染が、廃棄物の不法投棄などの環境悪化で拡がりつつあるとともに、テロリズム対策としての水源防備も怠ってもならない。一方、ユーザーニーズとしては、「安心して飲めるおいしい水」の要望も、近年、強くなって来ている。   Recently, pollution of tap water sources is spreading due to environmental deterioration such as illegal dumping of waste, and water source defense as a countermeasure against terrorism must be neglected. On the other hand, as user needs, the demand for “delicious water to drink with confidence” has been increasing in recent years.

このため、上水道の水源の汚染を早期に検知するには河川から採取した水を計器により水質の検査を行う手段が採られている他に前記採取した水を魚の飼育に供してその魚の異常行動を検出することにより水質の異常状態を検知する手段も採られている。   For this reason, in order to detect the contamination of the water source of the water supply at an early stage, there is a means for inspecting the water quality of the water collected from the river with a meter. Means for detecting an abnormal state of the water quality by detecting the above are also employed.

例えば、特許文献1に開示された水質監視装置は、原水が供給されると共に魚を遊泳させる水槽と、この水槽内の水質異常による魚の狂乱状態の挙動を検出する狂乱状態検出部を備える。本装置の制御部は前記狂乱状態検出部が魚の狂乱状態の挙動が予め設定された時間継続したことを出力した場合に水質異常であると判定する。したがって、本装置によれば、水質の検知に最も敏感にして、即応性ある魚を利用することにより、安価にして、簡単な機構で正確に水質を検知できる。   For example, a water quality monitoring device disclosed in Patent Document 1 includes a water tank that is supplied with raw water and that swims fish, and a frenzy state detection unit that detects the behavior of a frenzy state of a fish due to a water quality abnormality in the water tank. The control unit of the present apparatus determines that the water state is abnormal when the frenzy state detection unit outputs that the behavior of the frenzy state of the fish has continued for a preset time. Therefore, according to the present apparatus, it is possible to detect the water quality accurately with a simple mechanism at a low cost by using a fish that is most sensitive to water quality detection and is responsive.

特開2009−63333号公報JP 2009-63333 A

しかしながら、従来の水質監視装置では水槽の水質が異常でないにもかかわらず正常な魚の挙動によっても水質異常が検知されてしまうことがある。例えば、摂取行動、闘争行動、生殖行動、逃避行動、睡眠行動の際に水質異常が誤検出されることがある。   However, in the conventional water quality monitoring device, water quality abnormality may be detected by normal fish behavior even though the water quality of the aquarium is not abnormal. For example, water quality abnormalities may be erroneously detected during intake behavior, struggle behavior, reproductive behavior, escape behavior, and sleep behavior.

毒物の混入により水中の溶存酸素濃度が低下すると酸素の補給のために魚は水面に近くに浮上して口を水面に向けて身体を略垂直に起こす行動を採る。この鼻上げ行動は餌の捕食時にも採られるので、餌の摂取行動の場合には水質異常が誤検出されることがある。また、水槽内での縄張り争いや餌の奪いあい等に起因する闘争行動は毒物の混入による魚の狂乱状態にも似ているので水質異常が誤検出されることがある。生殖行動も魚の狂乱状態に似ているので狂乱状態の検出回数のみで水質異常を判断しようとすると誤検出もあり得る。また、水槽の周辺の異常があって驚いた場合の逃避行動も狂乱状態に似ており誤検出されることがある。そして、睡眠状態の魚は毒物による致死状態と似ており水槽の越流堰付近に漂うこともあるので水質異常の誤検出が起こることが懸念される。   When the dissolved oxygen concentration in the water drops due to poisoning, the fish rises close to the surface of the water to replenish the oxygen, and takes action to raise the body almost vertically with the mouth facing the surface. Since this nose raising action is also taken at the time of food predation, in the case of food intake behavior, a water quality abnormality may be erroneously detected. In addition, the struggle behavior caused by turf wars and bait in the aquarium is similar to the frenzy state of fish due to the mixing of poisonous substances, so water quality abnormalities may be erroneously detected. The reproductive behavior is similar to the frenzy state of the fish, so there is a possibility of false detection when trying to judge a water quality abnormality only by the number of frenzy state detections. Moreover, the escape behavior when there is an abnormality around the aquarium and is surprised is similar to the frenzy state and may be erroneously detected. And the sleeping fish resembles a deadly state caused by poisonous substances and may drift near the overflow weir in the aquarium.

本発明はかかる事情に鑑みなされたものでその目的は正常な魚の挙動による水質異常の誤検知を回避しながら上水道の原水の取水時に原水の水質異常を検知して警報を促すことができる水質監視装置の提供にある。   The present invention has been made in view of such circumstances, and its purpose is water quality monitoring capable of detecting an abnormality in the quality of raw water and prompting an alarm at the time of intake of the raw water of the water supply while avoiding false detection of abnormal water quality due to normal fish behavior. In providing equipment.

そこで、本発明の請求項1の水質監視装置は、上水道の原水が供される環境のもとで魚を遊泳させる水槽と、この水槽の液相に対して光を照射すると共に当該水槽を隔てて配置された反射体から反射された光を受光する複数の発光受光器と、前記魚による前記受光の遮断に基づき前記水槽の水質異常を判定する判定手段とを備え、前記複数の発光受光器のうちで上下に配置される一対の発光受光器が前記水槽の水面付近の水面下に光を照射するように複数備えられ、前記判定手段は所定時間内に前記いずれかの一対の発光受光器の受光遮断を複数検出した場合に前記原水の水質の異常に基づく魚の鼻上げ行動であると判定することを特徴とする。   Therefore, a water quality monitoring device according to claim 1 of the present invention separates a water tank for swimming fish under an environment where raw water for water supply is provided, and irradiates the liquid phase of the water tank with light. A plurality of light-emitting receivers that receive light reflected from the reflectors arranged in the manner described above, and a determination means that determines a water quality abnormality of the aquarium based on the blocking of the light reception by the fish, the plurality of light-emitting receivers A plurality of light emitting receivers disposed above and below are provided so as to irradiate light below the water surface near the water surface of the aquarium, and the determination means includes any one of the pair of light emitting receivers within a predetermined time. When a plurality of light reception interruptions are detected, it is determined that it is a fish nose raising action based on an abnormality in the quality of the raw water.

請求項2の水質監視装置は、請求項1の水質監視装置において、前記一対の発光受光器以外の複数の発光受光器が前記水槽の水位未満の位置にて上下方向に配置され、前記判定手段は、所定時間内における前記いずれかの発光受光器の単位時間当たりの受光遮断の回数を所定回数以上検出した場合に前記魚の狂乱と判断して前記水質に異常があると判定することを特徴とする。   The water quality monitoring apparatus according to claim 2 is the water quality monitoring apparatus according to claim 1, wherein a plurality of light emitting receivers other than the pair of light emitting receivers are arranged in a vertical direction at a position below the water level of the water tank, Is characterized in that when the number of light reception interruptions per unit time of any one of the light emitting and receiving devices within a predetermined time is detected a predetermined number of times or more, it is determined that the fish is furious and the water quality is abnormal. To do.

請求項3の水質監視装置は、請求項2の水質監視装置において、前記判定手段は、所定時間内における前記いずれかの発光受光器の単位時間当たりの受光遮断の回数を所定回数以上検出した後、さらに所定時間内における前記いずれかの発光受光器の単位時間当たりの受光遮断の回数を所定回数以上検出した場合に前記魚の異常狂乱と判断して前記異常よりも重度な水質異常があると判定することを特徴とする。   The water quality monitoring device according to claim 3 is the water quality monitoring device according to claim 2, wherein the determination means detects the number of light reception interruptions per unit time of any one of the light emitting receivers within a predetermined time after a predetermined number of times. Further, when the number of times of light reception interruption per unit time of any one of the light emitting and receiving devices within a predetermined time is detected a predetermined number of times or more, it is determined that the fish is abnormally abnormal and it is determined that there is a water quality abnormality that is more severe than the abnormality It is characterized by doing.

請求項4の水質監視装置は、請求項2の水質監視装置において、一つの発光受光器が前記水槽の越流堰付近の水面下に光を照射するように配置され、前記判定手段は、所定時間内における前記いずれかの発光受光器の単位時間当たりの受光遮断の回数を所定回数以上検出した後、さらに前記越流堰付近の発光受光器の受光遮断時間を所定時間以上検出した場合に前記魚の異常狂乱と判断して前記異常よりも重度な水質異常があると判定することを特徴とする。   The water quality monitoring device according to claim 4 is the water quality monitoring device according to claim 2, wherein one light-emitting receiver is disposed so as to irradiate light below the surface of the water near the overflow weir of the water tank, After detecting the number of light reception interruptions per unit time of any one of the light emitting receivers in time within a predetermined number of times, and further detecting the light reception interruption time of the light emission receivers near the overflow weir above a predetermined time It is determined that there is a water quality abnormality that is more severe than the abnormality by judging that the fish is abnormal.

請求項5の水質監視装置は、請求項1の水質監視装置において、一つの発光受光器が前記水槽の越流堰付近の水面下に光を照射するように配置され、前記判定手段は所定の時間帯において当該発光受光器の所定時間の受光遮断を少なくとも一回検出した場合に前記魚の仮死状態と判断して前記水質に異常があると判定することを特徴とする。   The water quality monitoring device according to claim 5 is the water quality monitoring device according to claim 1, wherein one light emitting receiver is disposed so as to irradiate light below the surface of the water near the overflow weir of the water tank, It is characterized in that the water quality is determined to be abnormal by determining that the fish is in a dead state when at least one light reception interruption of the light emitting / receiving device is detected at least once in a time zone.

請求項6の水質監視装置は、請求項5の水質監視装置において、前記判定手段は前記所定の時間帯において当該発光受光器の所定時間の受光遮断を少なくとも一回検出した後にさらに当該発光受光器の所定時間の受光遮断を少なくとも二回検出した場合に前記魚の致死状態と判断して前記異常よりも重度な水質異常があると判定することを特徴とする。   The water quality monitoring device according to claim 6 is the water quality monitoring device according to claim 5, wherein the determination means further detects the light reception interruption of the light emission receiver for a predetermined time in the predetermined time zone, and then further detects the light emission receiver. When the light reception interruption for a predetermined time is detected at least twice, it is determined that the fish is dead and it is determined that there is a water quality abnormality more severe than the abnormality.

請求項7の水質監視装置は、請求項2の水質監視装置において、一つの発光受光器が前記水槽の越流堰付近の水面下に光を照射するように配置され、前記判定手段は所定の時間帯において当該発光受光器の所定時間の受光遮断を検出した場合に前記水質に異常があると判定することを特徴とする。   The water quality monitoring device according to claim 7 is the water quality monitoring device according to claim 2, wherein one light-emitting receiver is arranged to irradiate light below the surface of the water near the overflow weir, and It is determined that there is an abnormality in the water quality when the light-receiving / blocking of the light-emitting / receiving device for a predetermined time is detected in a time zone.

請求項8の水質監視装置は、請求項7の水質監視装置において、前記判定手段は、前記越流堰付近の発光受光器の所定時間の受光遮断が検出された後に所定時間内における前記いずれかの発光受光器の単位時間当たりの受光遮断の回数を所定回数以上検出した場合に前記異常よりも重度な水質異常があると判定することを特徴とする。   The water quality monitoring device according to claim 8 is the water quality monitoring device according to claim 7, wherein the determination means is any one of the predetermined time within a predetermined time after detection of light reception interruption of the light emitting receiver near the overflow weir is detected. It is determined that there is a water quality abnormality that is more severe than the abnormality when the number of light reception interruptions per unit time of the light emitting / receiving device is detected a predetermined number of times or more.

以上の発明によれば正常な魚の挙動による水質異常の誤検知を回避しながら上水道の原水の取水時に原水の水質異常を検知して警報を促すことができる。   According to the above invention, it is possible to detect an abnormality in the quality of the raw water during the intake of the raw water in the water supply and to prompt an alarm while avoiding erroneous detection of the abnormal water quality due to the normal behavior of the fish.

発明の実施形態に係る水質監視装置の概略構成図。The schematic block diagram of the water quality monitoring apparatus which concerns on embodiment of invention. 発明の実施形態に係る水質監視装置の正面図。The front view of the water quality monitoring apparatus which concerns on embodiment of invention. 発明の実施形態に係る水質監視装置の上面図。The top view of the water quality monitoring device concerning the embodiment of the invention. 発明の実施形態に係る水質監視装置の左面図。The left view of the water quality monitoring apparatus which concerns on embodiment of invention. 発明の実施形態に係る発光受光系の概略構成図。1 is a schematic configuration diagram of a light emitting and receiving system according to an embodiment of the invention. 発明の実施形態に係る発光受光器の配置例(a)〜(c)を示した配置図。The layout which showed the example (a)-(c) of arrangement | positioning of the light-emitting / receiving device which concerns on embodiment of invention. 発明の実施形態に係る第一の監視,第二の監視の手順を示したシーケンス図。The sequence diagram which showed the procedure of the 1st monitoring and 2nd monitoring which concern on embodiment of invention. 発明の実施形態に係る第三の監視,組み合わせの監視,第四の監視,濁度監視の手順を示したシーケンス図。The sequence diagram which showed the procedure of the 3rd monitoring which concerns on embodiment of invention, the monitoring of a combination, the 4th monitoring, and turbidity monitoring.

以下、図面を参照しながら本発明の実施の形態について説明する。   Hereinafter, embodiments of the present invention will be described with reference to the drawings.

図1に例示された本発明の実施形態に係る水質監視装置1は水槽2と発光受光器3と制御盤4を備える。   A water quality monitoring apparatus 1 according to the embodiment of the present invention illustrated in FIG. 1 includes a water tank 2, a light emitting / receiving device 3, and a control panel 4.

水槽2は水質が監視される水として上水道の原水が供されると共にこの水環境のもとで魚10を遊泳させるための槽である。水槽2は図2〜図4に示された架台6上に設置されている。   The aquarium 2 is a tank for swimming the fish 10 in this water environment while the raw water of the water supply is provided as the water whose quality is monitored. The water tank 2 is installed on the mount 6 shown in FIGS.

水槽2の短辺側の端面には原水供給管11が接続されている。水槽2内に導入された原水供給管11の一端には図5に示したようにT字型パイプ12が接続、配置され、このパイプ12には複数の水噴出孔が穿設されている。T字型パイプ12の横方向のパイプ両端は閉塞され、縦方向のパイプの下端には、複数の水噴出孔が穿設された水噴出パイプ13が接続されている。水噴出パイプ13は図2,図4に示されたように水槽2の底辺に沿って配設されている。このような水噴出パイプ13の構成及び配置よって水槽2内の水流を一斉に整流させることができる。また、図1に示されたように原水供給管11には原水ストップ弁14,電磁弁15,減圧弁16,流量計17,調整弁18を介して供給され、これらの弁などにより水槽2内に供される原水は常時一定流量(一定圧力)に制御される。   A raw water supply pipe 11 is connected to the end surface on the short side of the water tank 2. As shown in FIG. 5, a T-shaped pipe 12 is connected to one end of the raw water supply pipe 11 introduced into the water tank 2, and a plurality of water ejection holes are formed in the pipe 12. Both ends of the T-shaped pipe 12 in the horizontal direction are closed, and a water ejection pipe 13 having a plurality of water ejection holes is connected to the lower end of the vertical pipe. The water ejection pipe 13 is disposed along the bottom side of the water tank 2 as shown in FIGS. The water flow in the water tank 2 can be rectified all at once by such a configuration and arrangement of the water ejection pipe 13. Further, as shown in FIG. 1, the raw water supply pipe 11 is supplied via a raw water stop valve 14, a solenoid valve 15, a pressure reducing valve 16, a flow meter 17, and an adjusting valve 18, and these valves and the like are used in the water tank 2. The raw water supplied to is always controlled at a constant flow rate (constant pressure).

水槽2内の越流堰20を越流した水は排水管19を介して主排水管21に移行して外部に放流されるようになっている。主排水管21は水槽2の底部の排水口22に接続されている。また、主排水管21にはストップ弁24が具備されており、水槽2内を清掃した際の廃水を系外排出できるようになっている。   The water that overflows the overflow weir 20 in the water tank 2 is transferred to the main drain pipe 21 via the drain pipe 19 and discharged to the outside. The main drain pipe 21 is connected to the drain port 22 at the bottom of the water tank 2. Further, the main drain pipe 21 is provided with a stop valve 24 so that waste water when the water tank 2 is cleaned can be discharged out of the system.

発光受光器3は図2〜図4に示したように水槽2の長辺側外側面から所定間隔隔てた位置にて設置位置が変更可能に複数備えられている。発光受光器3は図5に示したように発光素子と受光素子の機能を有する発光受光部31を備えており、水槽2の液相に対して光を照射すると共に水槽2を隔てて配置された反射体5から反射された前記光を受光する。魚10が前記光を遮ると、発光受光部31の受光素子が受ける光の量が減少するので、これをとらえることで魚10の検出が行える。   As shown in FIGS. 2 to 4, a plurality of light emitting / receiving devices 3 are provided so that the installation position can be changed at a position spaced from the outer surface of the long side of the water tank 2 by a predetermined distance. As shown in FIG. 5, the light emitting / receiving device 3 includes a light emitting element and a light emitting / receiving part 31 having a function of a light receiving element, which irradiates the liquid phase of the water tank 2 with light and is disposed across the water tank 2. The light reflected from the reflector 5 is received. When the fish 10 blocks the light, the amount of light received by the light receiving element of the light emitting / receiving unit 31 is reduced, and the fish 10 can be detected by capturing this.

図1に例示した態様では複数の発光受光器3のうちで一対の発光受光器3a,3bが水槽2の水面付近の水面下に光を照射するように複数備えられることで、水質異常に起因する魚10の鼻上げ行動を検出できるようになっている。また、複数の発光受光器3cが水槽2の長辺側外側面の中央付近の水位未満で且つ発光受光器3a,3bよりも下位の位置にて上下方向に配置されるように具備されることで、水質異常に起因する魚10の狂乱行動を検出できるようになっている。さらに、発光受光器3dが水槽2の越流堰20付近の水面下に光を照射するように配置されることで、水質異常に起因する魚10の狂乱行動や致死状態を検出できるようになっている。尚、このような発光受光器3a〜3dの配置に対応するように水槽2には図3に示したような略T型板状の反射体5が具備されている。   In the embodiment illustrated in FIG. 1, among the plurality of light-emitting receivers 3, a pair of light-emitting receivers 3 a and 3 b are provided so as to irradiate light below the water surface near the water surface of the water tank 2. The nose raising action of the fish 10 to be detected can be detected. Also, a plurality of light emitting / receiving devices 3c are provided so as to be arranged vertically below the water level near the center of the outer side of the long side of the water tank 2 and at positions lower than the light emitting / receiving devices 3a and 3b. Thus, it is possible to detect the frenzy behavior of the fish 10 caused by the water quality abnormality. Further, the light emitting / receiving device 3d is arranged so as to irradiate light below the surface of the overflow dam 20 in the water tank 2, so that it is possible to detect the furious behavior and the lethal state of the fish 10 caused by the water quality abnormality. ing. The water tank 2 is provided with a substantially T-shaped reflector 5 as shown in FIG. 3 so as to correspond to the arrangement of the light emitting / receiving devices 3a to 3d.

発光受光器3a,3bの配置態様は図6(a)に示した形態に限定されず図6(b)(c)に例示されたような態様を採ってもよい。図6(a)に例示された態様に係る一対の発光受光器3a,3bは上流側から下流側の方向に並ぶように配置されていると共に発光受光器3aは発光受光器3bよりも上流側且つ高位に配置されている。図6(b)に例示された態様では上流側の一対の発光受光器3a,3bに係る発光受光器3aは発光受光器3bよりも下流側且つ高位に配置されている。図6(b)(c)に例示された態様では中央側の発光受光器3a,3bが上下方向に配置されている。   The arrangement of the light emitting / receiving devices 3a and 3b is not limited to the configuration shown in FIG. 6A, and may adopt the configuration illustrated in FIGS. 6B and 6C. The pair of light-emitting receivers 3a and 3b according to the embodiment illustrated in FIG. 6A are arranged in the direction from the upstream side to the downstream side, and the light-emitting receiver 3a is upstream of the light-emitting receiver 3b. And it is arranged at a high level. In the embodiment illustrated in FIG. 6B, the light emitting / receiving device 3a related to the pair of light emitting / receiving devices 3a and 3b on the upstream side is disposed downstream and higher than the light emitting / receiving device 3b. In the embodiment illustrated in FIGS. 6B and 6C, the light emitting receivers 3a and 3b on the center side are arranged in the vertical direction.

制御盤4は図1に示したように水槽2内の魚10による発光受光器3の受光遮断に基づき水槽2の水質異常を判定する判定部41を備える。また、制御盤4は警報表示部42,警報ブザー43,シーケンサ44を備える。警報表示部42は判定部4によって判定された警報事項を点灯表示するようになっている。警報ブザー43は前記警報事項の点灯表示と連動して鳴動するようになっている。警報表示部42,警報ブザー43は図2に示したように制御盤4の扉部40に設けられている。シーケンサ44は判定部41を動作制御するための制御アルゴリズムを格納している。後述の判定部41の監視動作に係るパラメータ(検出時間、閾値等)はシーケンサ44によって任意に設定できるようになっている。   As shown in FIG. 1, the control panel 4 includes a determination unit 41 that determines a water quality abnormality in the aquarium 2 based on light reception blocking of the light emitting / receiving device 3 by the fish 10 in the aquarium 2. The control panel 4 includes an alarm display unit 42, an alarm buzzer 43, and a sequencer 44. The alarm display unit 42 lights up and displays the alarm items determined by the determination unit 4. The alarm buzzer 43 sounds in conjunction with the lighting display of the alarm items. The alarm display part 42 and the alarm buzzer 43 are provided on the door part 40 of the control panel 4 as shown in FIG. The sequencer 44 stores a control algorithm for controlling the operation of the determination unit 41. Parameters (detection time, threshold value, etc.) relating to the monitoring operation of the determination unit 41 described later can be arbitrarily set by the sequencer 44.

図7及び図8を参照しながら水質監視装置1の具体的な監視動作例について説明する。   A specific monitoring operation example of the water quality monitoring device 1 will be described with reference to FIGS. 7 and 8.

[第一の監視]
図7(a)に例示された第一の監視は水質異常に起因する魚10の鼻上げ行動を検出する。魚類はその生息系への毒物の混入により水面近くに浮上し、水面に対して鼻上げ行動をとる。そこで、判定部41は所定時間内に上流側、中央部、下流側のいずれかの一対の発光受光器3a,3bの受光遮断を複数検出した場合に水槽2の水質に異常があると判定する。
[First monitoring]
The first monitoring illustrated in FIG. 7A detects the nose raising behavior of the fish 10 due to the water quality abnormality. Fish rise near the surface of the water due to the entry of poisons into their habitats, and act to raise the nose against the surface of the water. Therefore, the determination unit 41 determines that there is an abnormality in the water quality of the aquarium 2 when a plurality of light reception interruptions of the pair of light emitting receivers 3a, 3b on the upstream side, the central part, or the downstream side are detected within a predetermined time. .

本監視では、判定部41は、上流側,中央側,下流側のいずれかの発光受光器3a,3bが同時に受光遮断及びその解除があったことを検出した場合にこれを1カウントと判断する。その後、所定時間内(例えば1分以内)におけるいずれかの発光受光器3a,3bの受光遮断とその解除のカウント数を所定回(例えば2回、計3回)検出した場合に水質異常に基づく魚10の鼻上げ行動であると判定する。この水質異常は「重故障」として制御盤4の警報表示部42に表示され、これと連動して警報ブザー43が鳴動する。そして、監視対象の水を供給する設備が停止される。尚、前記所定時間及びカウント数の閾値は制御盤4内に具備されたシーケンサ44によって任意に設定される。   In this monitoring, the determination unit 41 determines that this is one count when any one of the upstream, central, and downstream light-emitting receivers 3a and 3b detects that light reception has been blocked and released at the same time. . Thereafter, when the number of counts of light-blocking and release of any of the light-emitting receivers 3a and 3b within a predetermined time (for example, within 1 minute) is detected a predetermined number of times (for example, 2 times, a total of 3 times) It is determined that the fish 10 is raising the nose. This water quality abnormality is displayed on the alarm display unit 42 of the control panel 4 as a “serious failure”, and the alarm buzzer 43 sounds in conjunction with this. And the facility which supplies the water to be monitored is stopped. The predetermined time and the threshold value of the count number are arbitrarily set by a sequencer 44 provided in the control panel 4.

したがって、以上の第一の監視によれば誤検出を起こすことなく水質異常に起因する魚10の鼻上げ行動を検知でき、警報を促すことができる。   Therefore, according to the first monitoring described above, it is possible to detect the nose-lifting behavior of the fish 10 caused by the water quality abnormality without causing erroneous detection, and to prompt an alarm.

[第二の監視]
図7(b)に例示された第二の監視は水質異常に起因する魚10の狂乱行動を検出する。
[Second monitoring]
The second monitoring illustrated in FIG. 7B detects the mad behavior of the fish 10 caused by the water quality abnormality.

(正常時)
水質が「正常」である場合、水温や時の状況により狂乱に似た挙動をとることがあるが、その挙動の回数が少ない(魚10匹飼育の場合、受光遮断回数約100回/3分以内)。
(Normal)
When the water quality is “normal”, it may behave like a frenzy depending on the water temperature and time, but the number of times of the behavior is small (in the case of 10 fish breeding, the number of times of light interception is about 100 times / 3 minutes) Within).

(異常時当初または驚愕時の第一次挙動把握)
そして、水質異常や外部の気配が変わったときの場合には、魚10の挙動に平常と比べ変化が起こる(魚10匹飼育の場合、受光遮断約120回/分)。この「第一次挙動」の場合は軽故障と捉えて警戒態勢を促すことのみとしている。この場合、警戒態勢のまま次の挙動変化やこの挙動が所定時間継続しなければ、以上の作動を誤作動と認識して解除する。尚、図7(b)に記載の検出時間及び受光遮断(狂乱)の回数の閾値はシーケンサ44によって任意に設定される。
(Understand the primary behavior at the time of abnormality or startle)
When the water quality is abnormal or when the external signs change, the behavior of the fish 10 changes compared to normal (when 10 fish are raised, light interception is about 120 times / minute). In the case of this “primary behavior”, it is assumed that it is a minor failure and only a warning posture is promoted. In this case, if the next behavior change or this behavior does not continue for a predetermined time in the alert state, the above operation is recognized as a malfunction and released. Note that the threshold of the detection time and the number of times of light reception interruption (frenzy) shown in FIG. 7B is arbitrarily set by the sequencer 44.

図7(b)に例示された監視では、判定部41は所定時間(例えば3分間)内においていずれかの発光受光器3cの単位時間当たりの受光遮断の回数を所定回数以上検出した場合(例えば120回以上/分)に魚10の狂乱と判断して水槽2の水質に軽度な異常があると判定する。この異常は「軽故障」として制御盤4の警報表示部42に表示される。   In the monitoring illustrated in FIG. 7B, when the determination unit 41 detects the number of light reception interruptions per unit time of any one of the light-emitting receivers 3c within a predetermined time (for example, 3 minutes) (for example, It is determined that there is a slight abnormality in the water quality of the aquarium 2 by judging that the fish 10 is frenzy at 120 times / min). This abnormality is displayed on the alarm display unit 42 of the control panel 4 as “minor failure”.

(本格的な異常狂乱状態の第二次挙動把握)
「第一次挙動」に引き続き所定時間内に本格的な異常狂乱状態すなわち「第二次挙動」の事態が発生した場合には(例えば魚10匹飼育時に受光遮断回数約60回以上/分である場合、または発光受光器3dの受光遮断時間が15秒以上である場合)、前記異常よりも重度な異常を警告する。尚、図7(b)に記載の検出時間及び受光遮断(狂乱)の回数の閾値、間合い時間、及び発光受光器3dの受光遮断時間はシーケンサ44によって任意に設定される。
(Understanding the secondary behavior of full-scale abnormal frenzy)
If a full-fledged abnormal state of turbulence or “secondary behavior” occurs within a predetermined time after “primary behavior” (for example, when the number of light interception is about 60 times or more per minute when raising 10 fish) If there is a case, or if the light reception interruption time of the light emitting / receiving device 3d is 15 seconds or more), an abnormality that is more severe than the abnormality is warned. It should be noted that the detection time, the threshold of the number of times of light reception interruption (frenzy), the waiting time, and the light reception interruption time of the light emitting receiver 3d shown in FIG.

図7(b)に例示された監視では、判定部41は、所定時間(例えば3分間)内におけるいずれかの発光受光器3cの単位時間当たりの受光遮断の回数が所定回数以上(例えば120回以上/分)であることを検出する。   In the monitoring illustrated in FIG. 7B, the determination unit 41 determines that the number of light reception interruptions per unit time of any one of the light emitting / receiving devices 3c within a predetermined time (for example, 3 minutes) is equal to or more than the predetermined number (for example, 120 times). Or more).

さらに、所定の間合い時間(例えば10分)の後、所定時間内(例えば3分間)における前記いずれかの発光受光器3cの単位時間当たりの受光遮断の回数を所定回数以上(例えば60回以上/分)検出した場合に魚10の異常狂乱と判断して前記異常よりも重度な水質異常があると判定する。   Further, after a predetermined waiting time (for example, 10 minutes), the number of light reception interruptions per unit time of any one of the light-emitting receivers 3c within a predetermined time (for example, 3 minutes) is a predetermined number of times or more (for example, 60 times / Min) If detected, it is determined that there is an abnormal frenzy of the fish 10, and it is determined that there is a water quality abnormality that is more severe than the abnormality.

または、水槽2の越流堰20付近の発光受光器3dの受光遮断時間が所定時間以上(例えば15秒以上)であることを検出した場合に魚10の異常狂乱と判断して前記異常よりも重度な水質異常があると判定する。   Alternatively, when it is detected that the light reception interruption time of the light emitting / receiving device 3d in the vicinity of the overflow weir 20 of the water tank 2 is longer than a predetermined time (for example, 15 seconds or more), it is determined that the fish 10 is abnormally abnormal and the above abnormality is detected. It is determined that there is a severe water quality abnormality.

この第二次挙動把握によって検出されたいずれの異常も「重故障」として制御盤4の警報表示部42に表示され、これと連動して警報ブザー43が鳴動する。そして、監視対象の水を供給する設備が停止される。   Any abnormality detected by this secondary behavior grasp is displayed as a “serious failure” on the alarm display unit 42 of the control panel 4, and the alarm buzzer 43 sounds in conjunction with this. And the facility which supplies the water to be monitored is stopped.

したがって、以上の第二の監視によれば誤検出を起こすことなく水質異常に起因する魚10の狂乱行動を検知でき、警報を促すことができる。   Therefore, according to the second monitoring described above, it is possible to detect the mad behavior of the fish 10 caused by the water quality abnormality without causing erroneous detection, and to prompt an alarm.

[第三の監視]
魚10はその生息水域への毒物の混入により前段階の狂乱状態から仮死状態に移行するものや、致死状態で水槽2の底部に静止するものもある。また、正常時でも特に環境が平穏である場合は休憩や睡眠等の仮死状態と同様な状態となる。そこで、本監視では以下の第一次〜第三次の挙動の把握をもって水質異常を判定する。尚、以下に述べる図8(a)に記載の検出時間及び受光遮断の回数の閾値及び間合い時間はシーケンサ44によって任意に設定される。
[Third monitoring]
Some fish 10 shift from a frenzy state in a previous stage to a pseudo-dead state due to the mixing of poisons in their habitat waters, and some fish 10 remain stationary at the bottom of the aquarium 2 in a lethal state. In addition, even when normal, particularly when the environment is calm, it becomes a state similar to a temporary death state such as a break or sleep. Therefore, in this monitoring, water quality abnormality is determined by grasping the following primary to tertiary behaviors. Note that the detection time, the threshold of the number of times of light reception interruption and the waiting time described in FIG. 8A described below are arbitrarily set by the sequencer 44.

(第一次挙動把握)
仮死状態の魚10の水槽2の越流堰20に漂着すると、先ず、最初に発光受光器3dの所定時間の受光遮断が検出されると「軽故障」と判定され、この「第一挙動」を前提条件として、次の「第二次・第三次挙動」の発生を待機する。
(Understand primary behavior)
When the fish 10 in the assassinated state drifts to the overflow weir 20 of the aquarium 2, first, when a light reception interruption of the light emitting receiver 3 d for a predetermined time is first detected, it is determined as “minor failure”, and this “first behavior” As a precondition, the next “secondary / tertiary behavior” is awaited.

図8(a)に例示された監視では、判定部41は所定の時間帯(例えば2分間)において越流堰20近傍における発光受光器3dの所定時間(例えば15秒間)の受光遮断が少なくとも一回検出した場合に魚10の仮死状態と判断して水槽2の水質に異常があると判定する。この異常は「軽故障」として制御盤4の警報表示部42に表示される。   In the monitoring illustrated in FIG. 8A, the determination unit 41 determines that the light-receiving / blocking of the light emitting / receiving device 3d in the vicinity of the overflow weir 20 in the predetermined time zone (for example, 2 minutes) is at least one. If it is detected twice, it is determined that the fish 10 is in a dead state, and it is determined that the water quality of the aquarium 2 is abnormal. This abnormality is displayed on the alarm display unit 42 of the control panel 4 as “minor failure”.

(第二次・第三次挙動把握)
そして、「第一次挙動」に引き続き所定時間内に第二番目及び第三番目の第三次挙動を検知した場合、すなわち、発光受光器3dの所定時間の受光遮断が少なくとも二回検出されると第一挙動よりも重度な水質異常として判定される。
(Understand secondary and tertiary behavior)
Then, when the second and third tertiary behaviors are detected within a predetermined time following the “primary behavior”, that is, the light reception interruption of the light emitting receiver 3d for a predetermined time is detected at least twice. It is determined that the water quality is more severe than the first behavior.

図8(a)に例示された監視では、判定部41は、所定の時間帯(例えば2分間)において発光受光器3dの所定時間(例えば15秒間)の受光遮断を少なくとも一回検出する。さらに所定時間(例えば30秒)経過後、発光受光器3dの所定時間(例えば15秒間)の受光遮断を少なくとも二回検出した場合に魚10の致死状態と判断して前記異常よりも重度な水質異常があると判定する。この異常は「重故障」として制御盤4の警報表示部42に表示され、これと連動して警報ブザー43が鳴動する。そして、監視対象の水を供給する設備が停止される。   In the monitoring illustrated in FIG. 8A, the determination unit 41 detects light reception interruption of the light emitting / receiving device 3d for a predetermined time (for example, 15 seconds) at least once in a predetermined time zone (for example, 2 minutes). Further, after the elapse of a predetermined time (for example, 30 seconds), when the light receiving interruption of the light emitting / receiving device 3d is detected at least twice for a predetermined time (for example, 15 seconds), it is determined that the fish 10 is dead and the water quality is more severe than the abnormality. It is determined that there is an abnormality. This abnormality is displayed as a “serious failure” on the alarm display unit 42 of the control panel 4, and the alarm buzzer 43 sounds in conjunction with this abnormality. And the facility which supplies the water to be monitored is stopped.

したがって、以上の第三の監視によれば誤検出を起こすことなく水質異常に起因する魚10の仮死状態や致死状態を検知でき、警報を促すことができる。   Therefore, according to the third monitoring described above, it is possible to detect an assassination state or a lethal state of the fish 10 caused by the water quality abnormality without causing erroneous detection, and to prompt an alarm.

[第二の監視と第三の監視の組合せ]
魚10の挙動はその多様であり、決まった行動のパターンはない。そこで、本監視では上述の第二の監視と第三の監視とを組み合わせることで水質異常時の魚10の挙動をより確実に検出する。
[Combination of second monitoring and third monitoring]
The behavior of the fish 10 is diverse, and there is no fixed pattern of behavior. Therefore, in this monitoring, the behavior of the fish 10 when the water quality is abnormal is more reliably detected by combining the second monitoring and the third monitoring described above.

すなわち、判定部41は所定の時間帯において発光受光器3dの所定時間の受光遮断を検出した場合に水槽2の水質に異常があると判定する。さらには、発光受光器3dの所定時間の受光遮断を検出した後に所定時間内におけるいずれかの発光受光器3cの単位時間当たりの受光遮断の回数が所定回数以上検出した場合に前記異常よりも重度な水質異常があると判定する。以下に述べる図8(b)に記載の検出時間及び受光遮断の回数の閾値及び間合い時間はシーケンサ44によって任意に設定される。   That is, the determination unit 41 determines that there is an abnormality in the water quality of the aquarium 2 when detecting the light reception interruption of the light emitting / receiving device 3d for a predetermined time in a predetermined time zone. Furthermore, when the number of light reception interruptions per unit time of any of the light emission receivers 3c within a predetermined time after detecting the light reception interruption of the light emission receiver 3d for a predetermined time is more severe than the abnormality. It is determined that there is an abnormal water quality. The detection time, the threshold of the number of times of light reception interruption and the waiting time described in FIG. 8B described below are arbitrarily set by the sequencer 44.

図8(b)に例示した監視では、先ず、判定部41は所定の時間帯(例えば3分間)において発光受光器3dの所定時間(例えば30秒間)の受光遮断を検出した場合に水槽2の水質に異常があると判定する。この異常は「軽故障」として制御盤4の警報表示部42に表示される。   In the monitoring illustrated in FIG. 8B, first, when the determination unit 41 detects light reception interruption of the light emitting receiver 3d for a predetermined time (for example, 30 seconds) in a predetermined time zone (for example, 3 minutes), Judge that there is an abnormality in water quality. This abnormality is displayed on the alarm display unit 42 of the control panel 4 as “minor failure”.

次いで、所定時間(例えば10分間)の後に、判定部41は所定時間(例えば3分間)内におけるいずれかの発光受光器3cの単位時間当たりの受光遮断の回数が所定回数以上(例えば60回以上/分)検出された場合に前記異常よりも重度な水質異常があると判定する。この異常は「重故障」として制御盤4の警報表示部42に表示され、これと連動して警報ブザー43が鳴動する。そして、監視対象の水を供給する設備が停止される。   Next, after a predetermined time (for example, 10 minutes), the determination unit 41 determines that the number of light reception interruptions per unit time of any one of the light emitting / receiving devices 3c within the predetermined time (for example, 3 minutes) is a predetermined number or more (for example, 60 times or more). / Min) If detected, it is determined that there is a water quality abnormality that is more severe than the abnormality. This abnormality is displayed as a “serious failure” on the alarm display unit 42 of the control panel 4, and the alarm buzzer 43 sounds in conjunction with this abnormality. And the facility which supplies the water to be monitored is stopped.

したがって、以上の第二の監視と第三の監視の組み合わせによれば誤検出を起こすことなく水質異常に起因する魚10の狂乱状態並びに仮死状態や致死状態をより精度よく検知でき、警報を促すことができる。   Therefore, according to the combination of the second monitoring and the third monitoring described above, it is possible to more accurately detect the frenzy state, asphyxia state, and lethal state of the fish 10 caused by the water quality abnormality without causing false detection, and prompt an alarm. be able to.

[第四の監視]
魚10の睡眠状態は薬物による致死状態と似ており判断し難い。また、これと併行して水槽2の越流堰20に引っ掛かる魚10もある。そこで、本監視では異常の判定の過程に遅延時間を設けている。以下に述べる図8(c)に記載の受光遮断時間はシーケンサ44によって任意に設定される。
[Fourth monitoring]
The sleep state of the fish 10 is similar to a lethal state caused by drugs and is difficult to judge. In parallel with this, there is also a fish 10 caught on the overflow weir 20 of the aquarium 2. Therefore, in this monitoring, a delay time is provided in the abnormality determination process. The light reception blocking time described in FIG. 8C described below is arbitrarily set by the sequencer 44.

図8(c)に例示された監視では判定部41は発光受光器3dの所定時間(例えば5分)以上の受光遮断が検出された場合に魚10の致死状態と判断して水槽2の水質に重度な異常があると判定する。この異常は「重故障」として制御盤4の警報表示部42に表示され、これと連動して警報ブザー43が鳴動する。そして、監視対象の水を供給する設備が停止される。   In the monitoring illustrated in FIG. 8C, the determination unit 41 determines that the fish 10 is dead and detects the water quality of the aquarium 2 when the light receiving / blocking of the light emitting / receiving device 3d is detected for a predetermined time (for example, 5 minutes) or longer. It is determined that there is a serious abnormality. This abnormality is displayed as a “serious failure” on the alarm display unit 42 of the control panel 4, and the alarm buzzer 43 sounds in conjunction with this abnormality. And the facility which supplies the water to be monitored is stopped.

したがって、以上の第四の監視によれば本監視によれば誤検出を起こすことなく水質異常に起因する魚10の致死状態を精度よく検知でき、警報を促すことができる。   Therefore, according to the fourth monitoring described above, according to the main monitoring, the lethal state of the fish 10 caused by the water quality abnormality can be accurately detected without causing erroneous detection, and an alarm can be urged.

[濁度の監視]
本監視では図8(d)に例示したように判定部41は個々の発光受光器3bに対する反射光の減衰の度合いに基づき水槽2内の上流側、中央側、下流側の液相の濁り度を検出する。次いで、判定部41は所定時間(例えば3分間)内における受光減衰度合いに基づき個々の発光受光器3bの濁り度を算出する。濁り度は周知の測定原理例えば透過光測定方式または散乱光測定方式若しくはこれらの組合せた方式に基づき算出される。そして、算出された上流側、中央側、下流側の濁り度の値が全て1.5以上となった場合、水槽2の水質に異常があると判定する。この異常は「軽故障」として制御盤4の警報表示部42に表示される。その後、上記の「第一の監視」「第二の監視」「第三の監視」「第二の監視と第三の監視の組合せ」「第四の監視」のいずれかが継続される。前記所定時間及び濁り度の閾値はシーケンサ44によって任意に設定される。
[Monitoring turbidity]
In this monitoring, as illustrated in FIG. 8D, the determination unit 41 determines the turbidity of the liquid phase on the upstream side, the central side, and the downstream side in the water tank 2 based on the degree of attenuation of the reflected light with respect to each light emitting and receiving device 3 b. Is detected. Next, the determination unit 41 calculates the turbidity of each light emitting / receiving device 3b based on the received light attenuation within a predetermined time (for example, 3 minutes). The turbidity is calculated based on a well-known measurement principle such as a transmitted light measurement method, a scattered light measurement method, or a combination thereof. And when all the calculated values of the turbidity on the upstream side, the central side, and the downstream side are 1.5 or more, it is determined that the water quality of the aquarium 2 is abnormal. This abnormality is displayed on the alarm display unit 42 of the control panel 4 as “minor failure”. Thereafter, any one of the above-mentioned “first monitoring”, “second monitoring”, “third monitoring”, “combination of second monitoring and third monitoring”, and “fourth monitoring” is continued. The predetermined time and the turbidity threshold are arbitrarily set by the sequencer 44.

したがって、以上の濁度監視によれば流入原水の雷雨等による急激な濁り、特に上流域の夜間等の不意の濁流の流入検知等にも適用できる。例えば、夜間河川上流域に降雨(例えば夕立)等があり、その濁流の流入をいち早く検知し、浄化処理の早期対応が可能となる。この場合、水質監視装置1の制御盤4においては重故障表示及び警報が発せられる。このとき、水質監視装置1は停止されずに、監視が継続される。   Therefore, according to the above turbidity monitoring, it can be applied to the detection of sudden turbidity due to thunderstorms or the like of the inflow raw water, especially the inflow of unexpected turbulent flow at night in the upstream region. For example, there is rainfall (for example, evening) in the upstream area of the river at night, and it is possible to detect the inflow of the muddy stream as soon as possible, and to deal with the purification process at an early stage. In this case, a serious failure display and an alarm are issued on the control panel 4 of the water quality monitoring device 1. At this time, the water quality monitoring device 1 is not stopped and monitoring is continued.

1…水質監視装置
2…水槽
3,3a〜3d…発光受光器
41…判定部(判定手段)
DESCRIPTION OF SYMBOLS 1 ... Water quality monitoring apparatus 2 ... Water tank 3, 3a-3d ... Light emission receiver 41 ... Determination part (determination means)

Claims (8)

上水道の原水が供される環境のもとで魚を遊泳させる水槽と、
この水槽の液相に対して光を照射すると共に当該水槽を隔てて配置された反射体から反射された光を受光する複数の発光受光器と、
前記魚による前記受光の遮断に基づき前記水槽の水質異常を判定する判定手段と
を備え、
前記複数の発光受光器のうちで上下に配置される一対の発光受光器が前記水槽の水面付近の水面下に光を照射するように複数備えられ、
前記判定手段は所定時間内に前記いずれかの一対の発光受光器の受光遮断を複数検出した場合に前記原水の水質の異常に基づく魚の鼻上げ行動であると判定すること
を特徴とする水質監視装置。
An aquarium for swimming fish in an environment where raw water is provided,
A plurality of light-emitting receivers that irradiate light to the liquid phase of the water tank and receive light reflected from a reflector disposed across the water tank;
Determination means for determining a water quality abnormality of the aquarium based on the interception of the light reception by the fish,
A plurality of light-emitting receivers disposed above and below the plurality of light-emitting receivers are provided so as to irradiate light below the water surface near the water surface of the water tank,
The determination means determines that it is a fish nose raising action based on an abnormality in the quality of the raw water when a plurality of light reception interruptions of the pair of light emitting and receiving devices are detected within a predetermined time. apparatus.
前記一対の発光受光器以外の複数の発光受光器が前記水槽の水位未満の位置にて上下方向に配置され、
前記判定手段は、所定時間内における前記いずれかの発光受光器の単位時間当たりの受光遮断の回数を所定回数以上検出した場合に前記魚の狂乱と判断して前記水質に異常があると判定すること
を特徴とする請求項1に記載の水質監視装置。
A plurality of light-emitting receivers other than the pair of light-emitting receivers are arranged in a vertical direction at a position below the water level of the water tank,
The determination means determines that the fish is furious and determines that the water quality is abnormal when detecting the number of light reception interruptions per unit time of any one of the light-emitting receivers within a predetermined time for a predetermined number of times or more. The water quality monitoring apparatus according to claim 1.
前記判定手段は、所定時間内における前記いずれかの発光受光器の単位時間当たりの受光遮断の回数を所定回数以上検出した後、さらに所定時間内における前記いずれかの発光受光器の単位時間当たりの受光遮断の回数を所定回数以上検出した場合に前記魚の異常狂乱と判断して前記異常よりも重度な水質異常があると判定すること
を特徴とする請求項2に記載の水質監視装置。
The determination means detects the number of light reception interruptions per unit time of any one of the light-emitting receivers within a predetermined time, and then further determines the number of times per unit time of any of the light-emitting receivers within a predetermined time. The water quality monitoring apparatus according to claim 2, wherein when the number of light reception interruptions is detected a predetermined number of times or more, it is determined that there is an abnormality in the fish, and it is determined that there is a water quality abnormality that is more severe than the abnormality.
一つの発光受光器が前記水槽の越流堰付近の水面下に光を照射するように配置され、
前記判定手段は、所定時間内における前記いずれかの発光受光器の単位時間当たりの受光遮断の回数を所定回数以上検出した後、さらに前記越流堰付近の発光受光器の受光遮断時間を所定時間以上検出した場合に前記魚の異常狂乱と判断して前記異常よりも重度な水質異常があると判定すること
を特徴とする請求項2に記載の水質監視装置。
One light-emitting receiver is arranged to irradiate light below the water surface near the overflow weir of the water tank,
The determination means detects the number of light reception interruptions per unit time of any one of the light emitting receivers within a predetermined time, and further determines the light reception interruption time of the light emission receivers near the overflow weir for a predetermined time. The water quality monitoring apparatus according to claim 2, wherein when it is detected as described above, it is determined that there is an abnormality in the fish, and it is determined that there is a water quality abnormality that is more severe than the abnormality.
一つの発光受光器が前記水槽の越流堰付近の水面下に光を照射するように配置され、
前記判定手段は所定の時間帯において当該発光受光器の所定時間の受光遮断を少なくとも一回検出した場合に前記魚の仮死状態と判断して前記水質に異常があると判定すること
を特徴とする請求項1の水質監視装置。
One light-emitting receiver is arranged to irradiate light below the water surface near the overflow weir of the water tank,
The determination means determines that the fish is in an asymptomatic state and determines that the water quality is abnormal when the light-receiving / blocking of the light emitting / receiving device is detected at least once in a predetermined time period. Item 1. The water quality monitoring device according to item 1.
前記判定手段は前記所定の時間帯において当該発光受光器の所定時間の受光遮断を少なくとも一回検出した後にさらに当該発光受光器の所定時間の受光遮断を少なくとも二回検出した場合に前記魚の致死状態と判断して前記異常よりも重度な水質異常があると判定すること
を特徴とする請求項5の水質監視装置。
In the predetermined time zone, the determination means detects at least once the light reception interruption of the light emitting receiver for a predetermined time, and further detects the light reception interruption of the light emission receiver for the predetermined time at least twice. The water quality monitoring apparatus according to claim 5, wherein it is determined that there is a water quality abnormality that is more severe than the abnormality.
一つの発光受光器が前記水槽の越流堰付近の水面下に光を照射するように配置され、前記判定手段は所定の時間帯において当該発光受光器の所定時間の受光遮断を検出した場合に前記水質に異常があると判定すること
を特徴とする請求項2に記載の水質監視装置。
When one light emitting receiver is arranged to irradiate light below the surface of the water near the overflow weir, and the determination means detects a light reception interruption of the light emitting receiver for a predetermined time in a predetermined time zone. The water quality monitoring apparatus according to claim 2, wherein it is determined that the water quality is abnormal.
前記判定手段は、前記越流堰付近の発光受光器の所定時間の受光遮断が検出された後に所定時間内における前記いずれかの発光受光器の単位時間当たりの受光遮断の回数を所定回数以上検出した場合に前記異常よりも重度な水質異常があると判定すること
を特徴とする請求項7の水質監視装置。
The determination means detects the number of light reception interruptions per unit time of any one of the light emitting receivers within a predetermined time after the light reception interruption of the light emitting receivers near the overflow weir is detected for a predetermined time. The water quality monitoring apparatus according to claim 7, wherein it is determined that there is a water quality abnormality that is more severe than the abnormality.
JP2010243846A 2010-10-29 2010-10-29 Water quality monitoring device Active JP5643055B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2010243846A JP5643055B2 (en) 2010-10-29 2010-10-29 Water quality monitoring device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2010243846A JP5643055B2 (en) 2010-10-29 2010-10-29 Water quality monitoring device

Publications (2)

Publication Number Publication Date
JP2012098066A true JP2012098066A (en) 2012-05-24
JP5643055B2 JP5643055B2 (en) 2014-12-17

Family

ID=46390161

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2010243846A Active JP5643055B2 (en) 2010-10-29 2010-10-29 Water quality monitoring device

Country Status (1)

Country Link
JP (1) JP5643055B2 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20150136037A1 (en) * 2012-06-14 2015-05-21 Koninklijke Philips N.V. Illumination system for cultivation of aquatic animals

Citations (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS61224690A (en) * 1985-03-29 1986-10-06 Toshiba Corp Detector of poison of raw water
JPS63179252A (en) * 1987-01-21 1988-07-23 Hitachi Ltd Detector of poison produced by aquatic animal
US4888703A (en) * 1986-09-09 1989-12-19 Hitachi Engineering Co., Ltd. Apparatus for monitoring the toxicant contamination of water by using aquatic animals
JPH06324031A (en) * 1993-05-17 1994-11-25 Matsuyamashi Water monitoring apparatus on the basis of fish action pattern
JPH09101300A (en) * 1995-10-03 1997-04-15 Yamatake Eng Kk Water quality monitor
JPH09229924A (en) * 1996-02-20 1997-09-05 Anima Denshi Kk Water quality monitoring device using aquatic organism
JPH11142394A (en) * 1997-11-10 1999-05-28 Hitachi Ltd Apparatus for detecting water quality abnormality
JP2002311015A (en) * 2001-04-13 2002-10-23 Shikoku Res Inst Inc Water quality monitoring device
JP2004301706A (en) * 2003-03-31 2004-10-28 Sakae Takahashi Device for monitoring water quality
JP3108321U (en) * 2004-05-28 2005-04-14 隆洋 山本 Water quality monitoring device
JP2009063333A (en) * 2007-09-05 2009-03-26 Meikyo Denki Kk Water quality monitoring device

Patent Citations (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS61224690A (en) * 1985-03-29 1986-10-06 Toshiba Corp Detector of poison of raw water
US4888703A (en) * 1986-09-09 1989-12-19 Hitachi Engineering Co., Ltd. Apparatus for monitoring the toxicant contamination of water by using aquatic animals
JPS63179252A (en) * 1987-01-21 1988-07-23 Hitachi Ltd Detector of poison produced by aquatic animal
JPH06324031A (en) * 1993-05-17 1994-11-25 Matsuyamashi Water monitoring apparatus on the basis of fish action pattern
JPH09101300A (en) * 1995-10-03 1997-04-15 Yamatake Eng Kk Water quality monitor
JPH09229924A (en) * 1996-02-20 1997-09-05 Anima Denshi Kk Water quality monitoring device using aquatic organism
US5903305A (en) * 1996-02-20 1999-05-11 Anima Electronics Co., Ltd. Apparatus for monitoring water quality using aquatic living thing
JPH11142394A (en) * 1997-11-10 1999-05-28 Hitachi Ltd Apparatus for detecting water quality abnormality
JP2002311015A (en) * 2001-04-13 2002-10-23 Shikoku Res Inst Inc Water quality monitoring device
JP2004301706A (en) * 2003-03-31 2004-10-28 Sakae Takahashi Device for monitoring water quality
JP3108321U (en) * 2004-05-28 2005-04-14 隆洋 山本 Water quality monitoring device
JP2009063333A (en) * 2007-09-05 2009-03-26 Meikyo Denki Kk Water quality monitoring device

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20150136037A1 (en) * 2012-06-14 2015-05-21 Koninklijke Philips N.V. Illumination system for cultivation of aquatic animals
US11140881B2 (en) * 2012-06-14 2021-10-12 Signify Holding B.V. Illumination system for cultivation of aquatic animals

Also Published As

Publication number Publication date
JP5643055B2 (en) 2014-12-17

Similar Documents

Publication Publication Date Title
US9681636B2 (en) Detector system, sensor and dairy animal treatment device
TW200728693A (en) Flow measurement and control with bubble detection
ES2785653T3 (en) Procedure and installation of real-time control of the water quality of a distribution network
JP4712908B1 (en) Water quality automatic monitoring device and low concentration toxicity detection method
DK172996B1 (en) Centrifugal pump with shaft seal
JP2009082124A (en) Fish observation cistern
KR101193629B1 (en) Water leakage and cut-off apparatus of water purifier
US20200049682A1 (en) Ballast water measurement apparatus, ship comprising ballast water measurement apparatus, and ballast water measurement method
US20120285897A1 (en) Apparatus and Method for Maintaining Potable Water
JP5643055B2 (en) Water quality monitoring device
JP2009041333A (en) Water supply system and water supplying method
EP3641919B1 (en) Dosing assembly
JP2010043886A (en) Gas meter
JP2016161342A (en) Water quality detection device
CN208092029U (en) Full-automatic non-maintaining water quality automatic monitoring device
JP2009063333A (en) Water quality monitoring device
KR20210012587A (en) devivce pumping oil and detecting the amount of oil inflowed at groundwater using buoys
JP2863061B2 (en) Water quality monitoring device and water quality monitoring method
JP2009024960A (en) Hot water storage type hot water supply apparatus
JP6731767B2 (en) Flow detection device used in vacuum type sewage collection system, vacuum type sewage collection system, vacuum valve monitoring device and monitoring method
EP3705895B1 (en) Urinal sensor system
JP3894869B2 (en) Water quality detection device using fish
EP2662501A2 (en) A method and a system for leak protection of a supply water installation
KR200273877Y1 (en) Automatic system for supplying the disinfection chemicals in waterworks
CN208395907U (en) The automatic water-replenishing device of water tank

Legal Events

Date Code Title Description
A621 Written request for application examination

Free format text: JAPANESE INTERMEDIATE CODE: A621

Effective date: 20131007

A977 Report on retrieval

Free format text: JAPANESE INTERMEDIATE CODE: A971007

Effective date: 20140821

TRDD Decision of grant or rejection written
A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

Effective date: 20141007

A61 First payment of annual fees (during grant procedure)

Free format text: JAPANESE INTERMEDIATE CODE: A61

Effective date: 20141030

R150 Certificate of patent or registration of utility model

Ref document number: 5643055

Country of ref document: JP

Free format text: JAPANESE INTERMEDIATE CODE: R150

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250