JPH0735741A - Bod measuring equipment - Google Patents

Bod measuring equipment

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Publication number
JPH0735741A
JPH0735741A JP5178406A JP17840693A JPH0735741A JP H0735741 A JPH0735741 A JP H0735741A JP 5178406 A JP5178406 A JP 5178406A JP 17840693 A JP17840693 A JP 17840693A JP H0735741 A JPH0735741 A JP H0735741A
Authority
JP
Japan
Prior art keywords
bod
biosensor
measuring
buffer solution
measuring device
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
Application number
JP5178406A
Other languages
Japanese (ja)
Inventor
Kensuke Isobe
磯部  健介
Yoshiharu Tanaka
良春 田中
Tateo Ueno
健郎 上野
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.)
Fuji Electric Co Ltd
Original Assignee
Fuji Electric Co Ltd
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 Fuji Electric Co Ltd filed Critical Fuji Electric Co Ltd
Priority to JP5178406A priority Critical patent/JPH0735741A/en
Publication of JPH0735741A publication Critical patent/JPH0735741A/en
Pending legal-status Critical Current

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  • Sampling And Sample Adjustment (AREA)
  • Measuring Or Testing Involving Enzymes Or Micro-Organisms (AREA)

Abstract

PURPOSE:To allow independent measurement of C-BOD (biochemical oxygen demand) due to oxidation of organic substance and N-BOD based on nitrification while eliminating the clogging of piping system. CONSTITUTION:A biosenscr 31 measuring C-BOD using microorganisms eating organic substances is combined with a biosensor 32 measuring N-BOD using nitrified bacterium eating ammonia nitrogen and further provided with a pretreatment unit 2 and a suspesoid removing unit 33 thus allowing independent measurement of C-BOD and N-BOD and more detailed analysis of water quality. Even if suspesoid or suspended matters remain in the sample water passed through the pretreatment unit 2, they scarcely cause clogging of piping system and thereby the maintenance frequency can be decreased while enhancing the measurement accuracy.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は、下水処理場、工場、事
業所などからの排水、および河川、湖沼などの環境水域
における水中の生物化学的酸素要求量(BOD)につい
て、有機物由来のBOD(C−BOD)と窒素化合物の
硝化作用に基づくBOD(N−BOD)をそれぞれ独立
して測定する装置、とくにバイオセンサを用いて簡便に
精度よく測定可能なBOD測定装置に関する。
TECHNICAL FIELD The present invention relates to the biochemical oxygen demand (BOD) in water in wastewater from sewage treatment plants, factories, business establishments, and in environmental waters such as rivers and lakes. The present invention relates to an apparatus that independently measures (C-BOD) and BOD (N-BOD) based on the nitrification action of nitrogen compounds, and particularly to a BOD measurement apparatus that can be simply and accurately measured using a biosensor.

【0002】[0002]

【従来の技術】BODは20℃、5日間に好気性微生物
によって消費される水中溶存酸素量をmg/lで表わし
たものであり、最も代表的な水質汚濁指標として極めて
重要である。BODは、通常、日本工業規格(JIS)
に定められた工場排水試験法(JIS K 0102:
工業排水試験法)により、公定法として測定されている
が、この公定法には、 (イ)測定結果が得られるまでに5日間という長時間を
要し、排水処理などのプロセスを管理する上で、測定結
果を速やかに活かすことができない。
BOD is the dissolved oxygen content in water consumed by aerobic microorganisms at 20 ° C. for 5 days, expressed in mg / l, and is extremely important as the most representative water pollution index. BOD is usually Japanese Industrial Standard (JIS)
Factory drainage test method (JIS K 0102:
It is measured as an official method by the Industrial Wastewater Testing Method), but this official method requires (a) a long time of 5 days until the measurement results are obtained, which is important for managing wastewater treatment processes. Therefore, the measurement result cannot be utilized promptly.

【0003】(ロ)例えば、試料の希釈倍率の決定、p
H調製や毒物除去などの妨害の除去操作、硝化の抑制、
植種など、測定上の操作が非常に煩雑であり、熟練を要
する。 (ハ)手分析であるから、自動計測を行なうことができ
ない。 などの問題があり、近年、固定化微生物膜を応用したバ
イオセンサ(微生物センサ)を用いたBOD測定法が、
特公昭61−7258号公報などに記載されている。
(B) For example, determination of the dilution ratio of the sample, p
H removal and interference removal operations, nitrification suppression,
Measurement operations such as planting are very complicated and require skill. (C) Since it is a manual analysis, automatic measurement cannot be performed. In recent years, the BOD measurement method using a biosensor (microorganism sensor) that applies an immobilized microbial membrane has been
It is described in Japanese Examined Patent Publication No. 61-7258.

【0004】バイオセンサを用いた上記のBOD測定法
は、排水中のBODを約20〜40分程度で測定するこ
とができ、有効なBOD測定法であり、その装置が平成
2年に、日本工業規格(JIS K 3602:微生物
電極による生物化学的酸素消費量「BODS 」計測器)
として採用されるに至った。しかし、通常、固定化微生
物膜の細孔は、0.22〜0.45μm程度の小さいも
のであるから、固定化された微生物は、この細孔を通過
する溶解性有機物を直接資化することはできても、細孔
を通過できない懸濁性有機物については資化することが
できない。また、懸濁性有機物は、BOD測定装置の送
液系(ポンプ)や配管系(チューブ)などにおける目詰
まりの原因となり、測定精度やメンテナンスの点で大き
な問題となる。さらに、BODの測定に用いられるこの
種のバイオセンサは、試料水中の溶解性有機物を資化し
たときに生ずる有機酸などにより、固定化微生物膜内部
のpH値が変化して、センサ出力が変動するので、これ
を防ぐために緩衝溶液を用い、試料液を緩衝溶液と混
合,希釈した後、測定を行なうようにしている。したが
って、連続的に試料水中のBODをモニタリングする際
には、緩衝溶液の消費量が多くなるので、測定装置の保
守管理、ランニングコストなどの点にも問題がある。
The above-mentioned BOD measuring method using a biosensor is an effective BOD measuring method capable of measuring BOD in wastewater in about 20 to 40 minutes, and its apparatus was introduced in 1990 in Japan. Industrial standard (JIS K 3602: Biochemical oxygen consumption "BOD S " measuring instrument with microbial electrode)
Came to be adopted as. However, since the pores of the immobilized microbial membrane are usually as small as 0.22 to 0.45 μm, the immobilized microorganisms should directly utilize the soluble organic substances that pass through the pores. However, suspended organic substances that cannot pass through the pores cannot be assimilated. In addition, the suspended organic matter causes clogging in the liquid delivery system (pump), the piping system (tube), etc. of the BOD measurement device, which is a serious problem in terms of measurement accuracy and maintenance. Further, this type of biosensor used for BOD measurement changes the pH value inside the immobilized microbial membrane due to the organic acid generated when the soluble organic matter in the sample water is assimilated, and the sensor output fluctuates. Therefore, in order to prevent this, a buffer solution is used, and the sample solution is mixed with the buffer solution and diluted before the measurement. Therefore, when continuously monitoring the BOD in the sample water, the consumption of the buffer solution increases, which causes problems in maintenance and running cost of the measuring device.

【0005】これに対して本発明者らは、前処理装置に
より試料水中の懸濁物質を可溶化処理し、これまでのバ
イオセンサ法では不可能であった懸濁性有機物由来のB
OD測定装置を計測可能とし、緩衝溶液も節約される実
用的なBOD測定装置を、同一出願人から特開平2−3
1153号公報により開示している。以下にその概要を
述べる。
On the other hand, the present inventors solubilized suspended substances in sample water with a pretreatment device, and B derived from a suspending organic substance, which was impossible with the conventional biosensor methods.
From the same applicant, a practical BOD measuring device capable of measuring the OD measuring device and saving the buffer solution is disclosed in Japanese Patent Application Laid-Open No. 2-3.
This is disclosed in Japanese Patent No. 1153. The outline is described below.

【0006】図4は上記の本発明者らが出願中のBOD
測定装置の構成について、試料水の流れ方向を矢印で示
した模式図である。図4において、採水装置は排水を
採取する原水ポンプ1aと、オーバーフローにより採水
された試料水の貯留槽1bと配管類からなる。前処理装
は、採水ポンプ3により一定量採取された試料水中
の懸濁物質を破砕し、可溶化処理するものであり、超音
波ホモジナイザや、オゾナイザ、または本発明者らが同
一出願人により出願中の特願平5−47035号におけ
る酵素反応槽、半導体光反応槽で構成される。測定装置
は、上記採水装置と、前処理装置と、恒温槽4中に
設けたバイオセンサと、標準溶液槽6,希釈水槽7,
バルブ8,9,10,11,ポンプ12と配管とからな
る送液装置と、緩衝溶液槽13,ポンプ14と配管とか
らなる緩衝溶液循環装置15と、バイオセンサの出力
信号の演算処理と本測定装置の運転を制御する演算・制
御回路16から構成される。緩衝溶液としては、例えば
0.05〜0.1M,pH7.0のりん酸緩衝溶液を用
いる。標準溶液は、例えばグルコース・グルタミン酸の
等量混合溶液を2種類用い、バイオセンサの検量線の
作成に使用する。希釈水は例えばBOD0mg/lの標
準溶液で、配管経路の洗浄、試料水の希釈のために測定
の都度用いる。
FIG. 4 is a BOD filed by the inventors of the present invention.
It is a schematic diagram which showed the flow direction of the sample water with the arrow about the structure of a measuring device. In FIG. 4, the water sampling device 1 includes a raw water pump 1a for sampling waste water, a sample water storage tank 1b sampled by overflow, and pipes. The pretreatment device 2 crushes suspended matter in the sample water sampled by the water sampling pump 3 and solubilizes it, and uses an ultrasonic homogenizer, an ozonizer, or the same applicant as the applicant. It is composed of an enzyme reaction tank and a semiconductor photoreaction tank in Japanese Patent Application No. 5-47035. The measuring device is the water sampling device 1 , the pretreatment device 2 , the biosensor 5 provided in the constant temperature tank 4, the standard solution tank 6, the dilution water tank 7,
A liquid sending device including valves 8, 9, 10, 11 and a pump 12 and a pipe, a buffer solution circulating device 15 including a buffer solution tank 13, a pump 14 and a pipe, and an arithmetic process of an output signal of the biosensor 5. The measurement / control circuit 16 controls the operation of the measuring apparatus. As the buffer solution, for example, a phosphate buffer solution of 0.05 to 0.1 M and pH 7.0 is used. As the standard solution, for example, two kinds of equal-volume mixed solutions of glucose and glutamic acid are used, and used for preparing the calibration curve of the biosensor 5 . The dilution water is, for example, a standard solution of BOD 0 mg / l, and is used each time for measurement in order to wash the piping path and dilute the sample water.

【0007】図5はバイオセンサの構成を示す模式断
面図である。図5において、バイオセンサは、固定化
微生物膜17を取り付けたフローセル18と、溶存酸素
検出器19とにより構成してあり、図4に示す恒温槽4
に収納して測定温度に保つことができる。なお、試料水
および緩衝溶液も恒温槽4の内部で熱交換器20,21
を通過させることにより、測定温度に保っている。バイ
オセンサは、固定化微生物膜17の中に固定化された
微生物によって、溶解性有機物が資化される際に消費さ
れる溶存酸素の減少量を、溶存酸素検出器19により電
流値信号として出力する。この溶存酸素の減少量は、試
料水中に溶存する溶解性有機物の濃度に比例するので、
出力信号電流値から演算・制御回路16で演算され、溶
解性C−BODの値を求めることができる。
FIG. 5 is a schematic sectional view showing the structure of the biosensor 5 . In FIG. 5, the biosensor 5 is composed of a flow cell 18 to which an immobilized microbial membrane 17 is attached and a dissolved oxygen detector 19, and the thermostat 4 shown in FIG.
Can be stored in and kept at the measured temperature. It should be noted that the sample water and the buffer solution are also placed inside the constant temperature bath 4 in the heat exchangers 20, 21.
Is maintained at the measurement temperature by passing through. The biosensor 5 uses the dissolved oxygen detector 19 as a current value signal to show the amount of decrease in dissolved oxygen consumed when the soluble organic matter is assimilated by the microorganisms immobilized in the immobilized microbial film 17. Output. The amount of decrease in dissolved oxygen is proportional to the concentration of the dissolved organic matter dissolved in the sample water,
The value of the soluble C-BOD can be calculated by the calculation / control circuit 16 from the output signal current value.

【0008】バイオセンサによるBOD測定は、試料
水がフローセル18内に供給されてから、5〜15分程
度のあらかじめ設定した時間が経過したときの出力信号
の電流値について行なう。再び図4を参照して述べる
と、バイオセンサからの出力信号は、演算・制御回路
16のA/D変換器22でデジタル化されて演算装置2
3に送られ、所定の演算式に従って検量線の式、試料水
のBOD値を演算し記録する。出力装置24からは、算
出されたBOD値を出力し、もしくはあらかじめ設定し
た順序、時間に従い、バルブ8,9,10,11の切り
換えや、採水ポンプ3,前処理装置の動作制御信号を
出力する。緩衝溶液は、バイオセンサ内を図5に示し
たように、緩衝溶液入口27から流入して緩衝溶液出口
28から流出し、常に例えば1〜3ml/minで緩衝
溶液循環装置15によって移送され、熱交換器21を通
過して測定温度に保たれて循環する。緩衝溶液には、前
述の如く0.05〜0.1M,pH7.0のりん酸緩衝
溶液を用い、またこれに微量栄養分を添加したものも用
いることができる。
The BOD measurement by the biosensor 5 is carried out for the current value of the output signal when a preset time of about 5 to 15 minutes has passed since the sample water was supplied into the flow cell 18. Referring again to FIG. 4, the output signal from the biosensor 5 is calculated / controlled by the calculation / control circuit.
Digitalized by 16 A / D converters 22
3, the formula of the calibration curve and the BOD value of the sample water are calculated and recorded according to a predetermined calculation formula. The calculated BOD value is output from the output device 24, or the valves 8, 9, 10, 11 are switched and the operation control signals of the water sampling pump 3 and the pretreatment device 2 are output according to a preset order and time. Output. As shown in FIG. 5, the buffer solution flows in from the buffer solution inlet 27 and flows out from the buffer solution outlet 28 in the biosensor 5 , and is always transferred by the buffer solution circulation device 15 at, for example, 1 to 3 ml / min. It passes through the heat exchanger 21 and is circulated while being kept at the measurement temperature. As the buffer solution, a phosphate buffer solution of 0.05 to 0.1 M and pH 7.0 as described above may be used, and a solution containing a trace amount of nutrient added thereto may also be used.

【0009】最初に出力装置24の切り換え指令に従っ
て、希釈水槽7内の希釈水のみがバルブ10を経て、ポ
ンプ12により熱交換器20を通過して測定温度に保た
れて、液入口29から流入しバイオセンサ内に送ら
れ、液出口30から系外に排出される。バイオセンサ
の出力信号が安定した後、あらかじめ設定した順序に従
って、順次バルブ8,9.10を切り換えて、BOD標
準溶液により検量線を作成し、メモリ25にBOD演算
式を記憶させる。次に、バイオセンサの校正時に、同
時に採水ポンプ3により採水し、前処理装置で可溶化
処理された試料水が、バルブ11を通してポンプ12に
より熱交換器20を通過して測定温度に保たれて、バイ
オセンサへ送られBOD値が測定される。バイオセン
の校正は1日に数回行なわれ、試料水のBOD測定
を一定時間の間隔で繰り返し行なうことができる。
First, in accordance with the switching command of the output device 24, only the dilution water in the dilution water tank 7 passes through the valve 10 and the heat exchanger 20 by the pump 12 to be kept at the measurement temperature and flow from the liquid inlet 29. Then, it is sent into the biosensor 5 and discharged from the liquid outlet 30 to the outside of the system. Biosensor 5
After the output signal of is stabilized, the valves 8 and 9.10 are sequentially switched according to a preset order, a calibration curve is created by the BOD standard solution, and the BOD calculation formula is stored in the memory 25. Next, at the time of calibration of the biosensor 5 , the sample water sampled at the same time by the water sampling pump 3 and solubilized by the pretreatment device 2 passes through the heat exchanger 20 by the pump 12 through the valve 11 and the measured temperature. And the BOD value is measured by being sent to the biosensor 5 . The biosensor 5 is calibrated several times a day, and the BOD measurement of the sample water can be repeated at regular time intervals.

【0010】[0010]

【発明が解決しようとする課題】最近の研究によれば、
生物処理によって有機物が十分に除去されたと見られる
処理水は、BODを手分析で測定した結果、本来、有機
物の酸化によるBOD(C−BOD)が測定されるべき
であるが、硝化作用によるBOD(N−BOD)が同時
に測定されてしまうため、意外に高いBODを示すこと
が、例えば、服部らにより、雑誌、用水と廃水:34
(5)397(1992)などに記載され指摘されてい
る。
According to recent research,
It seems that organic matter was sufficiently removed by biological treatment.
As a result of measuring BOD by manual analysis, the treated water was originally organic.
BOD (C-BOD) due to oxidation of products should be measured
However, BOD (N-BOD) due to nitrification is simultaneously
Unexpectedly high BOD as it will be measured
However, for example, according to Hattori et al., Magazines, water and wastewater:34
(5) Described and pointed out in 397 (1992), etc.
It

【0011】このような状況下にあって、バイオセンサ
を用いた前述の特開平2−31153号公報に記載のB
OD測定装置は、懸濁性有機物の酸化分解、および溶解
性有機物で高分子量のものを低分子量化する前処理装置
を備えており、有機物由来のC−BODを測定するため
には、多くの利点を有するものであるが、硝化作用に基
づくN−BODについては測定するのが困難である。ま
た、試料の前処理装置において処理し切れずに残った懸
濁性物質や浮遊物などは、配管系の目詰まりの原因とな
り、測定精度や装置のメンテナンスの上で問題となる。
Under such circumstances, B described in the above-mentioned Japanese Patent Laid-Open No. 2-31153 using a biosensor.
The OD measuring device is equipped with a pretreatment device that oxidizes and decomposes suspended organic matter and lowers the molecular weight of soluble organic matter, and in order to measure C-BOD derived from organic matter, many Although it has advantages, it is difficult to measure N-BOD based on nitrification. In addition, a suspended substance or a suspended matter that has not been completely processed in the sample pretreatment device causes clogging of the piping system, which causes a problem in measurement accuracy and maintenance of the device.

【0012】本発明は上述の点に着目してなされたもの
であり、その目的は、有機物の酸化によるC−BOD
と、硝化作用に基づくN−BODとをそれぞれ独立に測
定して、より詳細な水質分析を行なうことができ、さら
に、配管系を目詰まりさせる懸濁性物質や浮遊物を排除
することが可能な、自動逆洗機構を持つ懸濁物質除去装
置を有するバイオセンサ応用のBOD測定装置を提供す
ることにある。
The present invention has been made by paying attention to the above points, and the purpose thereof is to provide C-BOD by oxidation of organic substances.
And N-BOD based on nitrification can be measured independently to perform a more detailed water quality analysis, and further, it is possible to eliminate suspended substances and suspended substances that clog the piping system. It is another object of the present invention to provide a biosensor application BOD measuring device having a suspended substance removing device having an automatic backwashing mechanism.

【0013】[0013]

【課題を解決するための手段】上記の課題を解決するた
めに、本発明のBOD測定装置は、有機物を資化する微
生物を用いたC−BOD測定用バイオセンサと、アンモ
ニア性窒素を資化する硝化菌を用いたN−BOD測定用
バイオセンサを組み合わせからなり、これに前処理装置
と懸濁物質除去装置を設けたものである。
In order to solve the above problems, the BOD measuring apparatus of the present invention uses a biosensor for C-BOD measurement using a microorganism that assimilates an organic substance, and assimilates ammoniacal nitrogen. The biosensor for N-BOD measurement using nitrifying bacteria is used in combination with a pretreatment device and a suspended substance removing device.

【0014】[0014]

【作用】本発明のBOD測定装置は上記のように構成し
たために、C−BODとN−BODとをそれぞれ独立に
測定することができるので、より詳細な水質分析が可能
であり、さらに、前処理装置を通過した試料水中に処理
し切れずに残った懸濁性物質や浮遊物などが存在して
も、それらを排除する懸濁物質除去装置を備えているた
め、装置の配管系に目詰まりが起こり難く、メンテナン
ス頻度が少なく、測定精度も高い。
Since the BOD measuring device of the present invention is constructed as described above, it is possible to measure C-BOD and N-BOD independently of each other, which enables more detailed water quality analysis. Even if there are suspended solids or suspended solids that have not been completely processed in the sample water that has passed through the processing unit, the system is equipped with a suspended substance removal unit that eliminates them. Clogging is less likely to occur, less maintenance is required, and measurement accuracy is high.

【0015】[0015]

【実施例】以下、本発明を実施例に基づき説明する。図
1は本発明によるBOD測定装置の要部構成と試料水の
送液系統を示す模式図であり、図4と共通する部分に同
一符号を用いてある。本発明による図1の装置の基本的
な構成は、図4に示した装置と比較すればわかるよう
に、これとほぼ同じであり、点線で囲った部分をC−B
OD測定用バイオセンサ31として表わしている。
EXAMPLES The present invention will be described below based on examples. FIG. 1 is a schematic diagram showing a configuration of a main part of a BOD measuring device according to the present invention and a liquid feeding system for sample water, and the same reference numerals are used for the same parts as those in FIG. The basic structure of the apparatus of FIG. 1 according to the present invention is almost the same as that of the apparatus shown in FIG. 4, and the portion surrounded by a dotted line is C-B.
It is represented as an OD measuring biosensor 31 .

【0016】図1が図4と異なる点は二つあり、一つは
図1の装置には、N−BOD測定用バイオセンサ32
付加したこと、具体的には、固定化微生物膜内に固定す
る微生物と校正用の標準溶液とが、それぞれ亜硝酸生成
細菌と、例えば濃度0.2および0.4mg/lに変わ
る点であり、このN−BOD測定用バイオセンサ32
は、構造的にC−BOD測定用バイオセンサ31と全く
同じである。また、N−BODの測定は、あらかじめア
ンモニア性窒素濃度とN−BODとの関係を、公定法の
測定で求めた換算値により、アンモニア性窒素濃度から
N−BODを計算して求める。
There are two differences between FIG. 1 and FIG. 4, and one is
The device of FIG. 1 includes a biosensor for N-BOD measurement.32To
Added, specifically, fixed in the immobilized microbial membrane.
Nitrite is produced by the microorganisms and the standard solution for calibration.
Change with bacteria, eg to concentrations of 0.2 and 0.4 mg / l
The biosensor for N-BOD measurement32
Is structurally a biosensor for C-BOD measurement31And totally
Is the same. In addition, the N-BOD measurement should be performed in advance.
The relationship between the ammoniacal nitrogen concentration and N-BOD was calculated by the official method.
From the ammonia nitrogen concentration based on the conversion value obtained by measurement
Calculate and determine N-BOD.

【0017】図1が図4と異なる点の二つめは、懸濁物
質除去装置を33を付加したことである。以上のことか
ら、ここでは懸濁物質除去装置を33についてのみ説明
を加える。図2は懸濁物質除去装置33の要部構成を点
線で囲って示した模式図である。図2において、前処理
装置を通過した試料水は、貯留槽34により懸濁物質
を除去した後、バルブ35からポンプ12へ送る。バル
35はノーマルオープン弁35aと、ノーマルクロー
ズ弁35bの二つの互いに逆動作をする弁を持ってお
り、多孔質フィルター36は、ノーマルオープン弁35
aとノーマルクローズ弁35bを介してそれぞれエアポ
ンプ37に接続してある。多孔質フィルター36は測定
時には、ノーマルクローズ弁35bを介してポンプ12
から測定系へ試料水を送り、非測定時はエアポンプ37
から空気をノーマルオープン弁35aを通して送り、空
気により互いに逆動作をするバルブ35を利用して、自
動的に逆洗を行なうことができる。また、圧力計38の
指示圧力は、演算・制御回路16に信号として送り、圧
力がある一定値例えば0.5Kg/cm3 より増加した
場合は、フィルター交換時期として出力装置24に表示
させる。
The second difference between FIG. 1 and FIG. 4 is that a suspension substance removing device 33 is added. From the above, only the suspension substance removing device 33 will be described here. FIG. 2 is a schematic diagram showing a configuration of a main part of the suspended substance removing device 33 by enclosing it with a dotted line. In FIG. 2, the sample water that has passed through the pretreatment device 2 is sent from the valve 35 to the pump 12 after the suspended substance is removed by the storage tank 34. Bal <br/> Bed 35 has a valve to a normally open valve 35a, the two opposite operations each other normally closed valve 35b, the porous filter 36 is normally open valve 35
a and a normally closed valve 35b are connected to an air pump 37. At the time of measurement, the porous filter 36 uses the normally closed valve 35b for pump 12
Send sample water from the measuring system to the measuring system, and when not measuring, air pump 37
The air can be sent through the normally open valve 35a, and the backwash can be automatically performed by using the valves 35 that operate in reverse with each other. Further, the pressure indicated by the pressure gauge 38 is sent as a signal to the arithmetic / control circuit 16, and when the pressure exceeds a certain value, for example, 0.5 Kg / cm 3 , it is displayed on the output device 24 as the filter replacement time.

【0018】図3は本発明のBOD測定装置を用いて、
3種類の下水2次処理水を測定して得られた結果を示す
棒グラフである。図3ではそれぞれ手分析BOD、C−
BODセンサ測定値、N−BODセンサ測定値、および
(C+N)−BOD値について示してある。図3の結果
から、Total BOD即ち(C+N)−BODは公
定法(手分析)のBOD5 とほぼ近い値を得ることがで
き、またその内訳としてC−BODとN−BODも知る
ことができる。
FIG. 3 shows the use of the BOD measuring device of the present invention.
It is a bar graph which shows the result obtained by measuring three kinds of secondary treated water. In Figure 3, manual analysis BOD and C- respectively.
The BOD sensor measurement value, the N-BOD sensor measurement value, and the (C + N) -BOD value are shown. From the results of FIG. 3, Total BOD, that is, (C + N) -BOD, can obtain a value close to BOD 5 of the official method (manual analysis), and C-BOD and N-BOD can be known as a breakdown thereof. .

【0019】[0019]

【発明の効果】下水処理場、工場、事業所などからの排
水、および河川や湖沼などの環境水域における水中のB
ODを、バイオセンサを用いたBOD測定装置によって
測定する場合、本来、有機物の酸化によるBOD(C−
BOD)が測定されるべきであるが、硝化作用によるB
OD(N−BOD)が同時に測定されてしまうため、意
外に高いBOD値を示すことが指摘されている。これを
解決するためになされた本発明のBOD測定装置を用い
ることにより、実施例で述べた如く、C−BODとN−
BODとをそれぞれ独立に同時に測定することが可能で
あり、より詳細な水質分析を行なうことができ、下水処
理プロセスの放流水質に関して有効な情報が得られるの
で、これらの結果を反映させた対応が可能となる。
[Effects of the Invention] B in water in wastewater from sewage treatment plants, factories, business establishments, and in environmental waters such as rivers and lakes.
When OD is measured by a BOD measuring device using a biosensor, BOD (C-
BOD) should be measured, but B due to nitrification
Since the OD (N-BOD) is measured at the same time, it is pointed out that the BOD value is surprisingly high. By using the BOD measuring device of the present invention made to solve this, as described in the embodiment, C-BOD and N-
Since BOD and BOD can be measured independently at the same time, more detailed water quality analysis can be performed, and effective information can be obtained regarding the discharged water quality of the sewage treatment process. It will be possible.

【0020】また、従来は試料水中の懸濁物質成分が測
定装置の配管系などの目詰まりの原因となり、測定精
度、装置のメンテナンスの頻度の面から問題であったの
に対して、本発明によれば、装置系に懸濁物質除去装置
を設けることにより、前処理装置で処理し切れなかった
懸濁物質を除去した後、測定を行なうので、配管系など
の目詰まりが起こり難く、メンテナンスの頻度も少なく
なり、実用性の高いBOD測定装置を得ることができ
る。
Further, in the past, the suspended substance component in the sample water caused the clogging of the piping system of the measuring device, which was a problem in terms of measurement accuracy and frequency of maintenance of the device. According to the above, since a suspended substance removing device is provided in the device system, the suspended substance that has not been completely processed by the pretreatment device is removed, and then the measurement is performed. The frequency of the BOD measurement is reduced, and a highly practical BOD measurement device can be obtained.

【図面の簡単な説明】[Brief description of drawings]

【図1】本発明のBOD測定装置の要部構成を示す模式
FIG. 1 is a schematic diagram showing a configuration of a main part of a BOD measuring device of the present invention.

【図2】本発明のBOD測定装置に用いる懸濁物質除去
装置の要部構成を示す模式図
FIG. 2 is a schematic diagram showing a main part configuration of a suspended substance removing apparatus used in the BOD measuring apparatus of the present invention.

【図3】本発明のBOD測定装置における測定結果を示
す棒線図
FIG. 3 is a bar diagram showing the measurement results of the BOD measuring device of the present invention.

【図4】従来のBOD測定装置の構成を示す模式図FIG. 4 is a schematic diagram showing a configuration of a conventional BOD measuring device.

【図5】バイオセンサの構成を示す模式図FIG. 5 is a schematic diagram showing the configuration of a biosensor.

【符号の説明】 採水装置 1a 原水ポンプ 1b 貯留槽 前処理装置 3 採水ポンプ 4 恒温槽 バイオセンサ 6 標準溶液槽 7 希釈水槽 8 バルブ 9 バルブ 10 バルブ 11 バルブ 12 ポンプ 13 緩衝溶液槽 14 ポンプ 15 緩衝溶液循環装置16 演算・制御回路 17 固定化微生物膜 18 フローセル 19 溶存酸素検出器 20 熱交換器 21 熱交換器 22 A/D変換器 23 演算装置 24 出力装置 25 メモリ 27 緩衝溶液入口 28 緩衝溶液出口 29 液入口 30 液出口31 C−BOD測定用バイオセンサ32 N−BOD測定用バイオセンサ33 懸濁物質除去装置 34 貯留槽35 バルブ 35a ノーマルオープン弁 35b ノーマルクローズ弁 36 多孔質フィルター 37 エアポンプ 38 圧力計[Explanation of symbols] 1 water sampling device 1a raw water pump 1b storage tank 2 pretreatment device 3 water sampling pump 4 constant temperature tank 5 biosensor 6 standard solution tank 7 dilution water tank 8 valve 9 valve 10 valve 11 valve 12 pump 13 buffer solution tank 14 Pump 15 Buffer Solution Circulation Device 16 Operation / Control Circuit 17 Immobilized Microbial Membrane 18 Flow Cell 19 Dissolved Oxygen Detector 20 Heat Exchanger 21 Heat Exchanger 22 A / D Converter 23 Computing Device 24 Output Device 25 Memory 27 Buffer Solution Inlet 28 Buffer Solution Outlet 29 Liquid Inlet 30 Liquid Outlet 31 Biosensor for C-BOD Measurement 32 Biosensor for N-BOD Measurement 33 Suspended Substance Removal Device 34 Storage Tank 35 Valve 35a Normal Open Valve 35b Normal Closed Valve 36 Porous Filter 37 Air pump 38 Pressure gauge

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】試料水を採取し貯留する採水装置と、懸濁
物質を可溶化する前処理装置と、懸濁物質除去装置と、
有機物由来のBOD測定用バイオセンサ、およびアンモ
ニア性窒素由来のBOD測定用バイオセンサとを備える
ことを特徴とするBOD測定装置。
1. A water sampling device for collecting and storing sample water, a pretreatment device for solubilizing suspended matter, and a suspended substance removing device,
A BOD measuring device comprising a biosensor for measuring BOD derived from an organic substance and a biosensor for measuring BOD derived from ammoniacal nitrogen.
【請求項2】請求項1記載のBOD測定装置において、
有機物由来のBOD測定用バイオセンサは、 a.有機物を資化する微生物を固定化した固定化微生物
膜と溶存酸素検出器を組み合わせたバイオセンサ, b.試薬,洗浄水,試料水を溶存酸素検出器へ送る送液
装置, c.溶存酸素検出器に緩衝溶液を循環させる緩衝溶液循
環装置, d.恒温槽内に配置し、試料水と緩衝溶液を測定温度に
保つ熱交換器, e.バイオセンサの出力信号の演算処理と運転制御を行
なう演算・制御回路を有することを特徴とするBOD測
定装置。
2. The BOD measuring device according to claim 1,
A biosensor for measuring BOD derived from an organic substance comprises a. A biosensor combining an immobilized microbial membrane on which microorganisms that utilize organic substances are immobilized and a dissolved oxygen detector, b. A liquid sending device for sending reagents, washing water, and sample water to a dissolved oxygen detector, c. A buffer solution circulation device for circulating a buffer solution through the dissolved oxygen detector, d. A heat exchanger that is placed in a constant temperature bath to keep the sample water and the buffer solution at the measurement temperature, e. A BOD measuring device having an arithmetic / control circuit for performing arithmetic processing of an output signal of a biosensor and operation control.
【請求項3】請求項1または2記載のBOD測定装置に
おいて、アンモニア性窒素由来のBOD測定用バイオセ
ンサは、 a.選択的にアンモニア性窒素を資化する硝化菌を固定
化した固定化微生物膜と溶存酸素検出器を組み合わせた
バイオセンサ, b.試薬,洗浄水,試料水を溶存酸素検出器へ送る送液
装置, c.溶存酸素検出器に緩衝溶液を循環させる緩衝溶液循
環装置, d.恒温槽内に配置し、試料水と緩衝溶液を測定温度に
保つ熱交換器, e.バイオセンサの出力信号の演算処理と運転制御を行
なう演算・制御回路を有することを特徴とするBOD測
定装置。
3. The BOD measuring device according to claim 1 or 2, wherein the biosensor for measuring BOD derived from ammoniacal nitrogen is a. A biosensor combining an immobilized microbial membrane on which nitrifying bacteria that selectively utilize ammoniacal nitrogen are immobilized and a dissolved oxygen detector, b. A liquid sending device for sending reagents, washing water, and sample water to a dissolved oxygen detector, c. A buffer solution circulation device for circulating a buffer solution through the dissolved oxygen detector, d. A heat exchanger that is placed in a constant temperature bath to keep the sample water and the buffer solution at the measurement temperature, e. A BOD measuring device having an arithmetic / control circuit for performing arithmetic processing of an output signal of a biosensor and operation control.
【請求項4】請求項1ないし3記載のBOD測定装置に
おいて、懸濁物質除去装置は、エアポンプ、多孔質フィ
ルター、逆動作する二つの弁および圧力計を備え、あら
かじめ定めたシーケンスにより、バイオセンサの校正時
または圧力計の設定圧力超過時に稼働する逆洗機構を持
つことを特徴とするBOD測定装置。
4. The BOD measuring device according to any one of claims 1 to 3, wherein the suspended substance removing device comprises an air pump, a porous filter, two valves that operate in reverse, and a pressure gauge, and the biosensor according to a predetermined sequence. A BOD measuring device having a backwashing mechanism that operates when calibrating the pressure gauge or when the pressure exceeds the set pressure of the pressure gauge.
JP5178406A 1993-07-20 1993-07-20 Bod measuring equipment Pending JPH0735741A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP5178406A JPH0735741A (en) 1993-07-20 1993-07-20 Bod measuring equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP5178406A JPH0735741A (en) 1993-07-20 1993-07-20 Bod measuring equipment

Publications (1)

Publication Number Publication Date
JPH0735741A true JPH0735741A (en) 1995-02-07

Family

ID=16047941

Family Applications (1)

Application Number Title Priority Date Filing Date
JP5178406A Pending JPH0735741A (en) 1993-07-20 1993-07-20 Bod measuring equipment

Country Status (1)

Country Link
JP (1) JPH0735741A (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2001004626A1 (en) * 1999-07-07 2001-01-18 Korea Institute Of Science And Technology An electrochemical method for enrichment of microorganism, a biosensor for analyzing organic substance and bod
EP1143135A2 (en) 2000-04-06 2001-10-10 Kabushiki Kaisha Toyoda Jidoshokki Seisakusho Cooling water channel structure of a cylinder head and method of manufacturing a cylinder head
JP2008032691A (en) * 2006-06-29 2008-02-14 Fuji Electric Systems Co Ltd Water quality monitoring system and method
JP2010029771A (en) * 2008-07-28 2010-02-12 Kobelco Eco-Solutions Co Ltd Method for estimating water quality and biological treatment method
CN110441469A (en) * 2019-09-19 2019-11-12 威海长青海洋科技股份有限公司 A kind of water body ammonia nitrogen detection kit and detection method

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2001004626A1 (en) * 1999-07-07 2001-01-18 Korea Institute Of Science And Technology An electrochemical method for enrichment of microorganism, a biosensor for analyzing organic substance and bod
EP1143135A2 (en) 2000-04-06 2001-10-10 Kabushiki Kaisha Toyoda Jidoshokki Seisakusho Cooling water channel structure of a cylinder head and method of manufacturing a cylinder head
JP2008032691A (en) * 2006-06-29 2008-02-14 Fuji Electric Systems Co Ltd Water quality monitoring system and method
JP2010029771A (en) * 2008-07-28 2010-02-12 Kobelco Eco-Solutions Co Ltd Method for estimating water quality and biological treatment method
CN110441469A (en) * 2019-09-19 2019-11-12 威海长青海洋科技股份有限公司 A kind of water body ammonia nitrogen detection kit and detection method

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