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JP3878859B2 - Flow stabilization unit and analyzer in front of it - Google Patents
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JP3878859B2 - Flow stabilization unit and analyzer in front of it - Google Patents

Flow stabilization unit and analyzer in front of it Download PDF

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Publication number
JP3878859B2
JP3878859B2 JP2002033345A JP2002033345A JP3878859B2 JP 3878859 B2 JP3878859 B2 JP 3878859B2 JP 2002033345 A JP2002033345 A JP 2002033345A JP 2002033345 A JP2002033345 A JP 2002033345A JP 3878859 B2 JP3878859 B2 JP 3878859B2
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sample water
detector
water
outlet
flow
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JP2003232706A (en
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守三 中村
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DKK TOA Corp
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DKK TOA Corp
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Description

【0001】
【発明が属する技術分野】
本発明は、試料水を測定する水質分析計等に試料水を導入する際の、流速の変動を影響を除去・緩和するために流量を安定化させるための前処理部の構造に関連し、この前処理部を用いた水質分析計に関連する。
【0002】
【従来の技術】
産業の各方面で、試料流体を水質分析計に導入して、連続的に測定することはよく行なわれている。たとえば上水の管理においては、飲料に適することを目的として残留塩素濃度や濁度、色度、pH、導電率、溶存酸素量等の水質が測定されている。更に環境を保持することを目的に河川水の水質測定も行なわれている。また各産業分野においては様々な水質測定が行なわれている。たとえば 火力・原子力発電所をはじめ、多くの産業界で事業用のボイラ―を利用している。ボイラーを安定に稼働させるためには、ボイラーに用いるボイラー水の水質を所定の範囲に保つことが求められる。そこでボイラー水の水質を監視するために、ボイラー水(復水および給水を含む)を配管から直接、試料水をサンプリングし、分析計で自動測定したり、手分析用を行う。
【0003】
この場合、試料水を水質分析計に送液する方法として試料水源そのものが圧力をもっていてこの圧力で送液される場合と、サンプリングポンプ等で取水して送液する方法とがある。連続的なサンプリングでは、 前者の場合においては水源の圧力が変動したり、後者の場合においてはポンプの経時変化などで試料水の流速が変化するケースが多い。一方、水質分析計の検出器は、試料水の流速が一定であることによって安定した検出が可能になるものが多い。例えば残留塩素の検出器は流量が一定であることで安定した信号としての拡散電流が得られる。
【0004】
そこで多くの分析計には検出器に到達する試料水流速を安定化させるために図1のような前処理部が設置されるのが通常であった。これは通常ヘッドタンク方式と呼ばれ、一定容量のタンクを分析計の一定の高さの位置にもうけてこのヘッドタンクに通常は下部から試料水を導入し、タンクを溢れた試料水は外側に排液して流す。検出器への試料水の流速は、このヘッドタンクの位置と検出器の位置の高低差で決まる差圧で常に一定となり、安定した流速を保つことができる。また容量の大きなヘッドタンクを設ける方法のかわりに図2のようにオーバーフローする分岐の上に2〜3mの配管を立てて空間を占める割合を小さくし、かつ流量の変動を吸収しようとする配管方式と呼ばれる方式も提案されている。
【0005】
【発明が解決しようとする課題】
検出器への試料水の流速を安定化させるための従来のヘッドタンク方式は(1)ヘッドタンクの大きさが通常内径50〜100mm程度あるので、この部分が大きくなること、(2)したがって試料水の置き替わりに時間を要すること、(3)試料水の供給が途絶えたときにはタンクに溜められた試料水が逆流する虞があるので、タンク水へ供給する配管に逆止弁を取り付ける必要があること(4)最初の起動時に測定開始までに時間がかかる、などの問題点があった。またこうしたヘッドタンクを設けた分析計を10〜20台並べて多測定点の多種類の測定対象をまとめて水質分析するような場合には、広い場所を占有することになり不便であった。またこの流量安定化ユニットを分析計の最適な位置に配置して試料水の入口から出口までの流速を適正に管理するうえでも不便であった。
【0006】
また図2のような広い空間を占有しない配管方式においては、配管を長くしておかないと、流速変動の吸収幅が少ないので、流速の急変の際、大気開放口から水を噴出すおそれがあり、この不具合避けるためには、配水管をある程度太くせざるを得なかった。
【0007】
【課題を解決するための手段】
発明者らは、 上記の問題を検討して、試料水を導入する試料水入口と、これに連通する二重管であってその外管と内管の間の空隙部が有底にしてなり、前記空隙部を流通経路とする流通部と、外管に設けられた試料水出口と該出口より更に上部の内管上端部をなす溢流出口と、内管の内壁空隙部を排出経路とする排液部と、前記溢流部より更に高い外管によって構成される請求項1の流量安定化ユニットを発明した。この流量安定化ユニットにおいては、試料水入口からの試料水入口の流量が増えた場合、従来の配管方式の溢流部と構造が異なるために、 溢流部より全周囲から内管の空隙部に流れ込み、いったん流れ込むとその流れによって排水側に更に引き込みアスピレータ効果によって効果的な排水効果を得ることができる。
【0008】
この結果、内径は6mm程度であっても、溢流部より高い位置にある外管の高さが、溢流部位よりも50cm程度あれば流速が100〜200ml/min.程度の一般の水質分析計に試料水を導入する流速の変化であれば外管の先端部から噴出するという不具合も発生しない。このようにして、内管に 外径9mm、内径6mmの管を用い、外管に内径11mm、外径14mmの管を用いて、流通部の空隙幅が1mmの流量安定化ユニットを構成することが可能で 全体として外径が15mm程度のコンパクトな流量安定化ユニットの構築が可能になる。
【0009】
また請求項2の発明は、請求項1の発明になる流量安定化ユニットを水質分析計の試料水導入口と検出器の間に配置してなるものである。このように配置することによって従来の水質分析計の配置スペースを大幅に縮小できる。
更に請求項3の発明は、請求項1の流量安定化ユニットの試料水出口の位置を水質分析計の検出器の排液口の位置よりも高い位置に配置し、かつ試料水出口から分析計にいたる配管を検出器よりも低い位置に迂回して配置したことを特徴とする水質分析計である。このような配置をとることによってかりに試料水が途絶えたり、供給されない状態になった場合でも、流量安定化ユニットの前段に逆止弁を設けなくても、検出器内の試料水はU字型のループのなかに保持されることになるので、検出器の下部先端部が乾燥して、再び試料水が導入された場合の測定に支障をきたすというような不具合も解消される。
【0010】
【発明の実施の形態】
本発明の実施例形態を以下に示す。
連続的に分析データを出力する水質分析計の試料水には、自らが吐出する圧力を有しない一般河川水など一般環境水や、上水など比較的穏やかな水圧を有しているものからボイラー水など高圧を有しているものなど多岐にわたる。ボイラー水は高温高圧であるので、これを一定圧力・温度に減圧・減温してから、水質分析計や手分析用の取水口に試料水を導入する。ボイラー水を例にとると減圧装置を通過した試料水は、試料水口から置された自動分析を行うための分析計にいたる。分析計には、pH計や、溶存酸素計、導電率計、ヒドラジン計、シリカ計などがあり、それぞれに対してニードル弁で所定の流量に調節されて、流量計で流量が確認されたのちに、試料水が導入されている。分析計を通過した試料水は通常、上端が大気に開放された排水用管に導かれて、排水口に戻り排水される。この場合、ボイラーの運転条件が変動すると水質分析計の検出器への試料水の流速が変化する。またボイラーが停止した場合には、圧力が急低下するので、その影響から試料水が逆流することもある。
【0011】
【実施例】
図1は従来の流量安定化ユニット8を前置した水質分析計9の例である。試料水導入口10を経て、ニードルバルブ14で流速が調整されたのちにヘッドタンク15に到達する。ヘッドタンク15は通常、内径40〜70mmの円筒形状をしており、更に径の大きな溢流槽16のなかにおかれている。ヘッドタンク15を溢れた試料水は溢流槽16を経て排液部7をとおり排出される。ヘッドタンク15の下部は試料水出口5を経て検出器11に到達する。検出器11の手前には更に流速を調整するためのバルブ17や流速を確認するために流量計12を取り付けている場合が多い。検出器11の出口は検出器先端部11aが存在する位置よりも一段高い位置の検出器出口11bを通過してから排出されるようになっている。これは検出器の先端が確実に試料水に浸漬されるようにするためである。ヘッドタンク15は通常、塩化ビニル管などを加工して製作されており、このタンクは予め設置する位置・高さを決定してから固定するのが通常である。
【0012】
図2はタンクを使用しない方式の配管方式の流量安定化ユニット8である。この方式においては、配管を上部に2〜3m長くしておかないと、流速変動の吸収幅が少ないので、流速の急変の際、大気開放口から水を噴出すおそれがあり、この不具合避けるためには、配水管をある程度太くせざるを得なかった。
【0013】
これらに対して図3は本発明による流量安定化ユニットである。事業用のボイラー水用の水質分析計を例にとって説明すると、ボイラーの高圧用試料水はあらかじめ減圧機構18をへて通常は恒温、恒圧になって試料水導入口10をへて水質分析計9に導入される。ボイラーは発電量に合わせて蒸気の量を変化させるので試料水の圧力も変化し、試料水の流量は圧力の変化に応じて変化する。この試料液の流速変動がそのまま検出器11に伝わると、溶存酸素計、pH計等多くの検出器で指示誤差を生ずる。そこで従来は、図1や図2に示すような流量安定化ユニット8を前置してこの流速の変動の影響を受けないようにしていた。
【0014】
本発明では、試料水を導入する試料水入口1と、これに連通する二重管であってその外管2と内管3の間の空隙部の下部が底を有していて、この空隙部を流通経路とする流通部4と、外管に設けられた試料水出口5と該出口より更に高い位置にあって内管上端をなす溢流出口6と、内管の内壁空隙部を排出経路とする排液部7と、前記溢流出口6より更に高い外管2よって構成される請求項1の流量安定化ユニット8を構成する。従来の配管方式の溢流部と構造が異なるために、溢流部より全周囲から内管の空隙部に流れ込み、いったん流れ込むとその流れによって排水側に更に引き込みアスピレータ効果によって効果的な排水効果を得ることができるのでヘッド圧を一定に保つことができる。
【0015】
請求項2の発明はこの流量安定化ユニット8を水質分析計9の試料水導入口10と検出器11の間に配置してなるものである。請求項3の発明ではこの試料水出口5から出た配管は検出器11にいたるが、検出器先端部11aよりも低い位置を迂回して配置している。また検出器11からの出口は検出器先端部11aが存在する位置よりも一段高い位置の検出器出口11bを通過してから排出されるようになっている。経路の途中には検出器への流速を確認するために流量計12は適宜バルブ17が取り付けられる場合もある。
【0016】
このように配置することによってボイラーが停止して試料水が供給されなくなったり試料水供給側の配管内の試料水が水抜けしてしまった場合でも検出器先端部11aは位置の高い検出器出口11bと、試料水出口5との間で形成されるU字管のなかにあるので、先端は試料水に浸漬されたまま保持され、乾燥して次回の測定に支障をきたすとこはない。乾燥による不具合の一例としてpH測定用ガラス電極の例を説明する。pHを測定するための、pH測定用ガラス電極は、その構成の一部である比較電極が、内部液が微細多孔質材料を経由して、試料液側に微小流量で流出する構造をとっているために、乾燥状態が続くと微細多孔質材料に内部液に組成物が析出して、目詰まりを起こし、再び試料水が供給されて、測定を開始すべきときに、ただちに正常な動作をしないという問題が発生する。
【0017】
上記のようにして構成された流量安定化ユニット2は管形が外径が15mm程度のコンパクトな構造ではあるが、流通部4をオーバーフローする試料水は溢流出口6において、内管の周辺から一様に流れ込んで排水されるので、概略200〜300ml/min.の範囲で流速が変動しても溢流する部位の水位が変わることはなく、良好なヘッドの水位が保たれる。したがって検出器に導入される試料水の流速はこのヘッド差で規制され、ヘッド差が50cmの場合、試料水導入口10での流速が100〜300ml/min.変動しても、検出器の位置では約100ml/min.に制御される。図4は流量安定化ユニットの各部位の流量特性を示している。
【0018】
また仮に突発的に200〜300ml/min.を超えるような変動があっても逸流出口部より更に高い外管によって保護されるので、試料水が分析計内に溢れ出ることもない。なお実施例では内管に 外径9mm、内径6mmの管を用い、外管に内径11mmφ、外径14mmの管を用いて、流通部の空隙幅が1mmに設定して説明したがこの管径は特に限定されるものではなく、ヘッドタンク構造よりもコンパクトになる範囲で任意に選ぶことができる。更に内管、外管の構造は円径の管構造に限定されず、溢流部において全周囲から隈なく内管に流れ込む構造であれば、特に限定はない。
【0019】
【発明の効果】
本発明によれば、ボイラー水等の水質を監視するための水質分析計に前置される流速安定化ユニットを 試料水を導入する試料水入口と、これに連通する有底の二重管で構成し、溢流した試料水が内管上部の周囲から排水されるようにしたので、ヘッド差が良好に保たれ、かつコンパクトな構造とすることができた。またこの流速安定化ユニットからの出口を分析計の検出器に導入する際に検出器の排液口の位置よりも高い位置に配置し、かつ試料水出口から水質分析計にいたる配管を検出器の下部先端部よりも低い位置を迂回して配置したので、試料水が逆流して検出器の先端が試料水に浸されくなるために検出器のセンサーの先端が乾燥するという有害な現象を解決でき、実用的な効果の高いものである。
【図面の簡単な説明】
【図1】従来の従来の流量安定化ユニットと水質分析計の検出器近傍の試料水の流れを示す説明図である。
【図2】更にもう一つの従来の流量安定化ユニットと水質分析計の検出器近傍の試料水の流れを示す説明図である。
【図3】本発明の流量安定化ユニットと水質分析計の検出器近傍の試料水の流れを示す説明図である。
【図4】流量安定化ユニットの特性を示す説明図である。
【符号の説明】
1 試料水入口
2 外管
3 内管
4 流通部
5 試料水出口
6 溢流出口
7 排液部
8 流量安定化ユニット
9 水質分析計
10 試料水導入口
11 検出器
11a 検出器先端部
11b 検出器出口
[0001]
[Technical field to which the invention belongs]
The present invention relates to the structure of a pretreatment unit for stabilizing the flow rate in order to remove and mitigate the influence of fluctuations in flow velocity when introducing sample water into a water quality analyzer or the like for measuring sample water, It relates to a water quality analyzer using this pretreatment unit.
[0002]
[Prior art]
In various fields of the industry, it is common to introduce a sample fluid into a water quality analyzer and continuously measure it. For example, in the management of clean water, water quality such as residual chlorine concentration, turbidity, chromaticity, pH, conductivity, dissolved oxygen amount and the like is measured for the purpose of being suitable for beverages. In addition, the quality of river water is also measured to maintain the environment. Various water quality measurements are carried out in each industrial field. For example, industrial boilers are used in many industries, including thermal and nuclear power plants. In order to operate the boiler stably, it is required to maintain the quality of boiler water used in the boiler within a predetermined range. Therefore, in order to monitor the quality of boiler water, sample water is sampled directly from the pipe of boiler water (including condensate and feed water) and automatically measured by an analyzer or used for manual analysis.
[0003]
In this case, there are two methods for feeding the sample water to the water quality analyzer: the sample water source itself having a pressure and being sent at this pressure; In continuous sampling, the pressure of the water source fluctuates in the former case, and in many cases, the flow rate of the sample water changes due to changes over time of the pump in the latter case. On the other hand, many detectors of water quality analyzers enable stable detection when the flow rate of sample water is constant. For example, a detector for residual chlorine can obtain a diffusion current as a stable signal when the flow rate is constant.
[0004]
Therefore, many analyzers are usually provided with a pretreatment unit as shown in FIG. 1 in order to stabilize the flow rate of the sample water reaching the detector. This is usually called the head tank system, where a fixed volume tank is placed at a certain height of the analyzer and sample water is usually introduced from the bottom into the head tank. Drain and drain. The flow rate of the sample water to the detector is always constant by the differential pressure determined by the difference in height between the position of the head tank and the position of the detector, and a stable flow rate can be maintained. Also, instead of installing a large-capacity head tank, a piping system that attempts to absorb the fluctuations in flow rate by reducing the proportion of space by placing a 2-3m pipe on the overflow branch as shown in Fig. 2 There is also a proposed method.
[0005]
[Problems to be solved by the invention]
The conventional head tank system for stabilizing the flow rate of the sample water to the detector is (1) the size of the head tank is usually about 50 to 100 mm in inner diameter, and this part becomes larger, and (2) therefore the sample It takes time to replace the water. (3) When the sample water supply stops, the sample water stored in the tank may flow backward. Therefore, it is necessary to attach a check valve to the pipe that supplies the tank water. (4) There was a problem that it took time to start measurement at the first startup. In addition, when 10 to 20 analyzers provided with such head tanks are arranged and a large number of measurement objects at multiple measurement points are collectively analyzed for water quality, a large space is occupied, which is inconvenient. In addition, it was inconvenient to properly manage the flow rate from the inlet to the outlet of the sample water by arranging this flow stabilization unit at the optimal position of the analyzer.
[0006]
In addition, in the piping system that does not occupy a large space as shown in FIG. 2, if the piping is not lengthened, the absorption width of the flow velocity fluctuation is small, so there is a risk that water will be ejected from the air opening when the flow velocity changes suddenly. In order to avoid this problem, the water distribution pipes had to be thickened to some extent.
[0007]
[Means for Solving the Problems]
The inventors have studied the above problems, and the sample water inlet for introducing the sample water and a double pipe communicating with the sample water have a bottom between the outer pipe and the inner pipe. A flow passage having the void portion as a flow passage, a sample water outlet provided in the outer tube, an overflow outlet forming an upper end portion of the inner tube further above the outlet, and an inner wall void portion of the inner tube as a discharge passage. The flow stabilization unit according to claim 1, which is constituted by a draining part that performs the above and an outer pipe that is higher than the overflow part. In this flow stabilization unit, when the flow rate from the sample water inlet to the sample water inlet increases, the structure differs from the overflow part of the conventional piping system. Once it flows in, it is further drawn into the drainage side by the flow, and an effective drainage effect can be obtained by the aspirator effect.
[0008]
As a result, even if the inner diameter is about 6 mm, the flow rate is 100 to 200 ml / min. If the height of the outer tube at a position higher than the overflow portion is about 50 cm from the overflow portion. If the sample water is introduced into a general water quality analyzer with a change in flow rate, there will be no inconvenience of jetting from the tip of the outer tube. In this way, a flow stabilizing unit having a flow gap of 1 mm is formed by using a tube having an outer diameter of 9 mm and an inner diameter of 6 mm for the inner tube and a tube having an inner diameter of 11 mm and an outer diameter of 14 mm for the outer tube. As a whole, it is possible to construct a compact flow stabilization unit with an outer diameter of about 15 mm.
[0009]
According to a second aspect of the present invention, the flow rate stabilizing unit according to the first aspect of the present invention is arranged between the sample water inlet of the water quality analyzer and the detector. By arranging in this way, the arrangement space of the conventional water quality analyzer can be greatly reduced.
Furthermore, the invention of claim 3 is arranged such that the position of the sample water outlet of the flow rate stabilization unit of claim 1 is higher than the position of the drainage port of the detector of the water quality analyzer, and the analyzer from the sample water outlet. This is a water quality analyzer characterized in that the pipe leading to is detoured to a position lower than the detector. Even if the sample water is interrupted or is not supplied due to such an arrangement, the sample water in the detector is U-shaped without providing a check valve in front of the flow stabilization unit. Since the lower tip of the detector is dried and the sample water is introduced again, the problem that the measurement is hindered is also eliminated.
[0010]
DETAILED DESCRIPTION OF THE INVENTION
Examples of the present invention will be described below.
Sample water for water quality analyzers that continuously output analysis data can be used for boilers that have relatively gentle water pressure, such as general environmental water, such as general river water, which does not discharge pressure, or water. There are a wide variety of things that have high pressure such as water. Since boiler water is high-temperature and high-pressure, the sample water is introduced into a water quality analyzer or a water intake for manual analysis after the pressure is reduced to a constant pressure and temperature. Taking boiler water as an example, the sample water that has passed through the pressure reducing device leads to an analyzer for automatic analysis placed from the sample water port. The analyzer includes a pH meter, dissolved oxygen meter, conductivity meter, hydrazine meter, silica meter, etc., each of which is adjusted to a predetermined flow rate with a needle valve, and the flow rate is confirmed with a flow meter. In addition, sample water is introduced. The sample water that has passed through the analyzer is usually led to a drain pipe whose upper end is open to the atmosphere, and returned to a drain outlet to be drained. In this case, the flow rate of the sample water to the detector of the water quality analyzer changes when the operating condition of the boiler changes. In addition, when the boiler is stopped, the pressure drops rapidly, so that the sample water may flow backward due to the influence.
[0011]
【Example】
FIG. 1 shows an example of a water quality analyzer 9 provided with a conventional flow rate stabilization unit 8. After reaching the head tank 15 after the flow rate is adjusted by the needle valve 14 through the sample water inlet 10. The head tank 15 usually has a cylindrical shape with an inner diameter of 40 to 70 mm, and is placed in an overflow tank 16 having a larger diameter. The sample water overflowing the head tank 15 is discharged through the drainage section 7 via the overflow tank 16. The lower part of the head tank 15 reaches the detector 11 through the sample water outlet 5. In many cases, a valve 17 for adjusting the flow rate and a flow meter 12 for confirming the flow rate are attached in front of the detector 11. The outlet of the detector 11 is discharged after passing through the detector outlet 11b which is one step higher than the position where the detector tip 11a is present. This is to ensure that the tip of the detector is immersed in the sample water. The head tank 15 is usually manufactured by processing a vinyl chloride pipe or the like, and this tank is usually fixed after determining a position and height to be installed in advance.
[0012]
FIG. 2 shows a flow rate stabilization unit 8 of a piping system that does not use a tank. In this method, if the pipe is not extended 2-3 m in the upper part, the absorption width of the flow velocity fluctuation is small, so there is a possibility that water may be ejected from the air opening when the flow velocity suddenly changes. Therefore, the water distribution pipes had to be thickened to some extent.
[0013]
FIG. 3 shows a flow stabilization unit according to the present invention. For example, a water quality analyzer for boiler water for business use will be described. The high-pressure sample water of the boiler is normally kept at a constant temperature and pressure through the decompression mechanism 18 in advance, and then the water quality analyzer through the sample water inlet 10. 9 will be introduced. Since the boiler changes the amount of steam according to the power generation amount, the pressure of the sample water also changes, and the flow rate of the sample water changes according to the change in pressure. If the flow rate fluctuation of the sample solution is transmitted to the detector 11 as it is, an indication error occurs in many detectors such as a dissolved oxygen meter and a pH meter. Therefore, conventionally, a flow rate stabilizing unit 8 as shown in FIGS. 1 and 2 is provided in front so as not to be affected by the fluctuation of the flow velocity.
[0014]
In the present invention, a sample water inlet 1 for introducing sample water, and a double pipe communicating with the sample water, the lower part of the gap between the outer pipe 2 and the inner pipe 3 has a bottom. The flow passage 4 having the flow passage as a flow passage, the sample water outlet 5 provided in the outer pipe, the overflow outlet 6 at a position higher than the outlet and forming the upper end of the inner pipe, and the inner wall void of the inner pipe The flow rate stabilizing unit 8 according to claim 1 is constituted by the drainage part 7 as a path and the outer pipe 2 higher than the overflow outlet 6. Since the structure is different from the overflow part of the conventional piping method, it flows from the entire periphery into the gap of the inner pipe from the overflow part, and once it flows, it draws further into the drainage side by that flow and has an effective drainage effect due to the aspirator effect Since it can be obtained, the head pressure can be kept constant.
[0015]
The invention of claim 2 is such that the flow rate stabilization unit 8 is arranged between the sample water inlet 10 of the water quality analyzer 9 and the detector 11. In the invention of claim 3, the pipe coming out of the sample water outlet 5 reaches the detector 11, but is arranged around a position lower than the detector tip 11 a. The outlet from the detector 11 is discharged after passing through the detector outlet 11b at a position one step higher than the position where the detector tip 11a is present. In the middle of the path, a valve 17 may be appropriately attached to the flow meter 12 in order to confirm the flow rate to the detector.
[0016]
With this arrangement, even when the boiler stops and the sample water is not supplied or the sample water in the pipe on the sample water supply side has drained, the detector tip 11a has a high-position detector outlet. 11b and the U-shaped tube formed between the sample water outlet 5, the tip is kept immersed in the sample water and does not interfere with the next measurement by drying. An example of a glass electrode for pH measurement will be described as an example of a problem caused by drying. The glass electrode for pH measurement for measuring pH has a structure in which the reference electrode, which is a part of the structure, flows out to the sample liquid side at a minute flow rate through the microporous material. Therefore, if the dry state continues, the composition will precipitate in the internal liquid on the microporous material, causing clogging, and when sample water is supplied again and measurement should be started, normal operation is immediately started. The problem of not happening.
[0017]
The flow stabilization unit 2 configured as described above has a compact structure with a tube shape having an outer diameter of about 15 mm. However, the sample water overflowing the circulation section 4 flows from the periphery of the inner tube at the overflow outlet 6. Since it flows uniformly and is drained, it is approximately 200 to 300 ml / min. Even if the flow velocity fluctuates in this range, the water level of the overflowing portion does not change, and a good head water level is maintained. Therefore, the flow rate of the sample water introduced into the detector is regulated by this head difference. When the head difference is 50 cm, the flow rate at the sample water inlet 10 is 100 to 300 ml / min. Even if it fluctuates, the position of the detector is about 100 ml / min. Controlled. FIG. 4 shows the flow characteristics of each part of the flow stabilization unit.
[0018]
Moreover, if it is suddenly 200-300 ml / min. Even if there is a fluctuation exceeding 1, the sample water is not overflowed into the analyzer because it is protected by the outer pipe higher than the outlet part. In this embodiment, the inner tube is a tube having an outer diameter of 9 mm and an inner diameter of 6 mm, and the outer tube is a tube having an inner diameter of 11 mmφ and an outer diameter of 14 mm. Is not particularly limited, and can be arbitrarily selected as long as it is more compact than the head tank structure. Further, the structure of the inner pipe and the outer pipe is not limited to a circular pipe structure, and there is no particular limitation as long as it flows into the inner pipe from the entire periphery in the overflow portion.
[0019]
【The invention's effect】
According to the present invention, the flow rate stabilization unit placed in front of the water quality analyzer for monitoring the water quality such as boiler water is provided by the sample water inlet for introducing the sample water and the bottomed double tube communicating with the sample water inlet. In this way, the overflowing sample water is drained from the periphery of the upper part of the inner pipe, so that the head difference is kept good and a compact structure can be achieved. In addition, when the outlet from this flow rate stabilization unit is introduced into the detector of the analyzer, it is arranged at a position higher than the position of the drain of the detector, and the pipe from the sample water outlet to the water quality analyzer is connected to the detector. Since the sample water flows backward and the tip of the detector becomes soaked in the sample water, the sensor tip of the detector dries. It can be solved and has a high practical effect.
[Brief description of the drawings]
FIG. 1 is an explanatory diagram showing a flow of sample water in the vicinity of a conventional flow rate stabilization unit and a detector of a water quality analyzer.
FIG. 2 is an explanatory view showing the flow of sample water in the vicinity of another conventional flow stabilization unit and detector of the water quality analyzer.
FIG. 3 is an explanatory diagram showing the flow of sample water in the vicinity of the detector of the flow stabilization unit and the water quality analyzer of the present invention.
FIG. 4 is an explanatory diagram showing characteristics of the flow rate stabilization unit.
[Explanation of symbols]
DESCRIPTION OF SYMBOLS 1 Sample water inlet 2 Outer pipe 3 Inner pipe 4 Flow part 5 Sample water outlet 6 Overflow outlet 7 Drainage part 8 Flow rate stabilization unit 9 Water quality analyzer 10 Sample water inlet 11 Detector 11a Detector tip 11b Detector Exit

Claims (1)

試料水導入口と分析計の検出器との間に、試料水の試料水入口と、外管と内管の間の空隙部が有底の二重管の空隙部を流通経路とする流通部と、該外管に設けられた試料水出口部と該試料水出口部より更に上部の内管に設けられた溢流出口部と、該内管の内壁空隙部を排出経路とする排液部と、該溢流出口部より更に高い外管によって構成される流量安定化ユニットを配置した水質分析計において、試料水出口の位置が水質分析計の検出器の排液口の位置よりも高い位置に配置し、かつ試料水出口から水質分析計にいたる配管を検出器先端部よりも低い位置を迂回して配置し、該検出器先端部が存在する位置よりも一段高い位置の検出器出口を通過してから排出されるようになっていることを特徴とする水質分析計。Between the sample water inlet and the detector of the analyzer, the sample water inlet, and the flow channel with the gap between the outer tube and the inner tube as the flow channel of the bottomed double tube A sample water outlet provided in the outer pipe, an overflow outlet provided in the inner pipe further above the sample water outlet, and a drainage section using the inner wall gap of the inner pipe as a discharge path And a water quality analyzer in which a flow stabilization unit composed of an outer pipe higher than the overflow outlet is disposed, the position of the sample water outlet is higher than the position of the drain of the detector of the water quality analyzer And a pipe extending from the sample water outlet to the water quality analyzer, bypassing the position lower than the detector tip, and placing the detector outlet at a level higher than the position where the detector tip exists. A water quality analyzer characterized by being discharged after passing.
JP2002033345A 2002-02-12 2002-02-12 Flow stabilization unit and analyzer in front of it Expired - Fee Related JP3878859B2 (en)

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