JP2005156426A - Residual chlorine measuring device - Google Patents

Abstract

<P>PROBLEM TO BE SOLVED: To provide a small-sized residual chlorine measuring device capable of excellent cleaning of an electrode. <P>SOLUTION: This residual chlorine measuring device is equipped with a measuring tank 1 equipped with a measuring chamber 15 into which measuring fluid is introduced, and an electrode unit 2 for outputting an oxidation/reduction current based on the concentration of free residual chlorine included in the measuring fluid by being mounted on the measuring tank 1 and by being brought into contact with the measuring fluid introduced into the measuring chamber 15. The measuring chamber 15 in the measuring tank 1 is formed circularly by arranging coaxially a cylindrical unit 14 in a cylindrical space 13, and the inlet of a passage 23 linking to a discharge port 25 is provided on the upper surface center part of the measuring chamber 15. Beads 16 for cleaning the electrode in the electrode unit 2 are filled inside the circular measuring chamber 15. An irregular slope as a disturbing means of the beads 16 is formed in the cylindrical unit 14. <P>COPYRIGHT: (C)2005,JPO&NCIPI

Description

  The present invention relates to a residual chlorine measuring device that detects a residual chlorine concentration by polarography.

  In domestic water, pool water, 24-hour bath water, etc., chlorine is injected for sterilization thereof. The amount of chlorine injected is controlled by measuring the concentration of free residual chlorine contained in the sample water. As a reagent-free measuring method for measuring the free residual chlorine concentration, a polarographic method is mainly used. The polarographic method measures the ion concentration of a specific chemical species by measuring the oxidation / reduction current that flows between two electrodes when a voltage is applied between the two electrodes (counter electrode and working electrode) immersed in the test water. Is a method of measuring. A three-electrode type using a reference electrode in addition to the counter electrode and the working electrode is also known. In the three-electrode type, the reference potential is applied to the reference electrode in order to specify the potential of the working electrode whose absolute potential is unknown. This three-electrode method has the advantage of being resistant to changes in conductivity. In the polarographic method, since the oxidation / reduction current value changes when the flow rate of the sample water in contact with the electrode changes, a measurement tank called a flow cell for immersing the electrode in the water sample with a constant flow rate is used.

In addition, since the surface of the working electrode is contaminated by the reduction reaction, the ceramic beads are housed in a measuring tank and the working electrode is rotated by a motor so that the electrode surface is rubbed against the ceramic beads to clean the electrode surface. Yes. Moreover, in patent document 1, only an edge part faces an annular bead storage part in a pair of electrodes, a reflux is caused in the annular bead storage part, and the beads are made to collide with the electrode surface by centrifugal force. Is disclosed. According to this, contamination of the electrode can be effectively prevented, and the configuration can be simplified by not using a motor that rotates the electrode.
JP 2002-250711 (paragraphs 0019 to 0021, FIGS. 1 and 2)

  However, in the residual chlorine meter disclosed in Patent Document 1 described above, the beads moving together with the test water introduced into the cylindrical bead storage tank have a rotational motion along the bead storage tank, The current situation is that effective cleaning cannot be performed.

  The present invention has been made in view of these points, and an object of the present invention is to provide a residual chlorine measuring device that is small and can clean an electrode satisfactorily.

  A residual chlorine measuring device according to the present invention includes an introduction port for introducing a measurement fluid, a measurement chamber connected to the introduction port, a measurement tank having a discharge port connected to the measurement chamber and discharging the measurement fluid, and the measurement tank And an electrode unit that outputs an oxidation / reduction current based on the concentration of free residual chlorine contained in the measurement fluid in contact with the measurement fluid introduced into the measurement chamber from the introduction port. The measurement chamber is formed in a circular shape by coaxially arranging a cylindrical unit in a cylindrical space, and the introduction port is connected to introduce water into the annular measurement chamber in a tangential direction, and the measurement chamber The center of the upper surface is provided with an inlet of a flow channel connected to the discharge port, and the annular measurement chamber is filled with beads for cleaning the electrodes of the electrode unit, and the cylindrical unit is disturbed by the beads. hand Wherein the but has been formed.

  According to the present invention, since the bead disturbance means is formed in the cylindrical unit, the beads move not only in a simple rotational motion but also up and down. Thereby, the direction in which the beads hit the electrodes of the electrode unit is randomized, and the electrodes can be cleaned efficiently.

Hereinafter, preferred embodiments of the present invention will be described with reference to the accompanying drawings.
FIG. 1 is a diagram showing a configuration of a residual chlorine measurement system according to an embodiment of the present invention.
The measurement system includes a measurement tank 1, an electrode unit 2 attached to the measurement tank 1, a flow sensor 3 attached to the measurement tank 1, and an oxidation / reduction current and flow sensor 3 detected by the electrode unit 2. And an arithmetic processing unit 4 that calculates and displays the free residual chlorine contained in the test water as the measurement fluid in the measurement tank 1 based on the flow rate signal output from.

  2-5 is a figure which shows the detailed structure of the measurement tank 1. As shown in FIG. The measurement tank 1 is, for example, inserted into an inspection flow path that branches off from the main circulation path of the target water to be sterilized and joins the circulation path again, and is assembled so that the whole has a cubic shape, And an upper body portion 12. A cylindrical space 13 is formed in the lower main body 11, and a cylindrical unit 14 is coaxially accommodated in the cylindrical space 13 to form an annular residual chlorine measuring chamber 15 together with the cylindrical unit 14. The annular residual chlorine measuring chamber 15 is filled with beads 16 made of electrode cleaning ceramic, glass or the like. For example, as shown in FIG. 3, the column unit 14 is a unit in which a columnar body 14 a having an upper end formed in a conical shape and a columnar table 14 b formed so as to project in the radial direction at the lower end thereof are integrally formed. is there. A jumping table-like irregular slope 14c as a disturbance means for the beads 16 is formed on the columnar table 14b.

  A test water introduction port 17 communicating with the residual chlorine measurement chamber 15 is formed at a position below one side surface of the lower main body 11. As shown in FIG. 4, the introduction port 17 is connected in the tangential direction of the annular residual chlorine measurement chamber 15. On the other hand, an electrode unit insertion hole 18 for mounting the electrode unit 2 is formed on the other side surface of the lower main body 11, for example, the opposite side surface. The electrode unit 2 is screwed into the electrode unit insertion hole 18 so that the tip from which the three electrodes are exposed faces the residual chlorine measurement chamber 15 as described later. The O-ring 20 keeps a liquid-tight space between the distal end and the proximal end of the electrode unit 2.

  The upper body portion 12 is formed with a columnar portion 21 that fits into the cylindrical space in order to form the upper surface of the residual chlorine measurement chamber 15 of the lower body portion 11, and the lower body portion 11, the upper body portion 12, Are liquid-tightly coupled via an O-ring 22 attached to the cylindrical portion 21. In the columnar portion 21 of the upper main body 12, a water sample through hole 23 for discharging water from the center of the upper surface of the residual chlorine measuring chamber 15 is formed. The test water flow hole 23 communicates with a flow rate measurement chamber 24 which is a cylindrical space opened above the upper body portion 12, and the flow rate measurement chamber 24 is connected to one side surface of the upper body portion 12. It communicates with the drainage port 25 formed in the. As shown in FIG. 5, an impeller 27 formed by radially arranging magnets 26 is accommodated in the flow rate measurement chamber 24 so as to be rotatable about a rotation shaft 28. A magnetic sensor 29 is mounted on the upper main body 12 so as to face the impeller 27 in the radial direction. As shown in FIG. 2, the upper part of the flow rate measurement chamber 24 is liquid-tightly sealed with a cap screw 30 and an O-ring 31 attached thereto.

FIG. 6A is an external perspective view of the electrode unit 2, and FIG. 6B is a diagram illustrating a detection surface at the tip of the electrode unit 2. The electrode unit 2 is of a three-electrode type, and is arranged concentrically in a plane in the order of the working electrode 41, the reference electrode 42, and the counter electrode 43 in order from the center of the circular detection surface. These electrodes 41 to 43 are integrally sealed with a sealing material so as to be exposed only on the detection surface. These electrodes 41 to 43 and the sealing material form a cylindrical main body 44. A screw part 45, a nut part 46, and an insulating coating 47 are formed on the outer periphery of the main body part 44 in order from the distal end side (detection surface side) of the main body part 44.
Thus, since the main body 44 has the detection surface in which the working electrode 41, the reference electrode 42, and the counter electrode 43 are arranged concentrically in a plane, there is no difference in the distance between the electrodes, and the sensitivity is stabilized and improved. To do. In addition, since the electrodes 41 to 43 are concentrated on the tip surface of the electrode unit 2, the liquid contact portion may be only the tip surface of the electrode unit 2, so the area of the portion of the electrode unit 2 facing the measurement chamber 15 is reduced. It can be minimized, and the measuring tank 1 can be made compact.

  As shown in FIG. 1, the arithmetic processing unit 4 includes a voltage generator 5 that applies a predetermined pulse voltage and sweep voltage between the working electrode 41 and the reference electrode 42 of the electrode unit 2, and the working electrode 41 and the counter electrode. 43, a current detection unit 6 for detecting the oxidation-reduction current flowing through 43, an oxidation / reduction current detected by the current detection unit 6, and a flow rate signal from the flow sensor 3, and calculating a residual chlorine concentration, An arithmetic processing unit 7 that appropriately outputs a voltage generation command to the voltage generating unit 5 and a display unit 8 that displays the residual chlorine concentration calculated by the arithmetic processing unit 7 are provided.

Next, the operation of the residual chlorine measuring system configured as described above will be described.
The sample water flowing through the inspection channel is directly introduced into the annular residual concentration measurement chamber 15 from the introduction port 17 of the measurement tank 1, and swirls around the cylindrical body 14a. Since the cylindrical body 14a narrows the water detection channel in the measurement chamber 15, the water is swirled vigorously even with a small flow rate. Thereby, at the front-end | tip of the electrode unit 2, each electrode 41-43 contacts a test water with moderate flow velocity. A voltage pulse for cleaning a predetermined electrode is applied from the voltage generator 5 between the working electrode 41 and the reference electrode 42 at the start-up or at a predetermined cycle, and then a sweep voltage in a predetermined voltage range is applied. Thus, an oxidation / reduction current is obtained from the electrode unit 2. This current is detected by the current detection unit 6, and the current value is input to the arithmetic processing unit 7. Since the electrodes 41 to 43 are concentrated on the tip surface of the electrode unit 2 and the electrodes 41 to 43 are close to each other, high sensitivity can be achieved.

  On the other hand, the bead 16 filled in the residual concentration measurement chamber 15 is also swung on the swirling flow of the test water, but the cylindrical body 14a narrows the flow path of the water to increase the flow rate even at a low flow rate. As a result, the turning force of the beads 16 can be increased to improve the cleaning power. Further, since the irregular slope 14c as a disturbance means is formed on the column base 14b, the bead 16 jumps up at the irregular slope 14c, and vigorously collides with the electrodes 41 to 43 of the electrode unit 2 from a random direction. To do. Thereby, the electrode surface is washed well. In addition, since the electrodes 41 to 43 are concentrated on the distal end surface of the electrode unit 2, all the electrodes including the counter electrode 43 can be cleaned.

The sample water swirling through the chlorine concentration measurement chamber 15 is eventually discharged to the sample water flow hole 23 side. However, since the beads 16 move together with the swirling sample water, the beads 16 are moved outward by centrifugal force and are not discharged to the water sample flow hole 23 arranged in the central portion. For this reason, even if the flow rate of the test water is increased, the beads 16 do not flow out.
Further, since the beads 16 moved to the center when the operation is stopped fall to the outer peripheral side of the chlorine concentration measurement chamber 15 by the slope at the upper end of the cylindrical body 14a, the beads 16 may be discharged from the test water flow hole 23 at the time of activation. Absent.

  The sample water introduced into the sample water flow hole 23 is introduced into the flow rate measurement chamber 24 to rotate the impeller 27. Since the rotation speed at this time is proportional to the flow rate of the sample water, a flow rate pulse corresponding to the flow rate is generated by detecting the rotation speed of the impeller 2 with the magnetic sensor 29, and this flow rate pulse is input to the arithmetic processing unit 7. Is done. For example, the arithmetic processing unit 7 calculates the concentration of free residual chlorine contained in the test water based on the following arithmetic expression.

但し、Ｃ_０：ＨＯＣｌ濃度（ｍｏｌ）
Ｉ：検出電流
ｎ：電位移動数（ＨＯＣｌの場合、ｎ＝２）
Ｆ：ファラデー係数
Ａ：電極表面積（ｃｍ^２）
Ｄ：拡散係数
Ｕ：流量（ｃｍ^３／ｓ）
Ｖ：電極ユニット２の先端の直径
ｋ：係数

However, C ₀ : HOCl concentration (mol)
I: detection current n: number of potential movements (in the case of HOCl, n = 2)
F: Faraday coefficient A: Electrode surface area (cm ² )
D: Diffusion coefficient U: Flow rate (cm ³ / s)
V: Diameter of the tip of the electrode unit 2 k: Factor

As a result, even if the flow rate fluctuates somewhat, the detected current value (I) detected by the current detection unit 6 is corrected by the flow rate information (U) detected by the flow rate sensor 3, so that an accurate residual chlorine concentration is always obtained. (C ₀ ) can be calculated.

  In the residual chlorine measurement by the polarographic method, the output current of the three-electrode type electrode unit 2 is affected by the measurement flow velocity. According to this residual chlorine measurement system, the output current of the electrode unit 2 is corrected for flow rate. Therefore, it is possible to measure the residual chlorine concentration with high accuracy regardless of the flow rate of the sample water.

  The flow rate detection may be performed not only by the magnetic impeller type flow rate sensor described above but also by a mechanism such as a turbine type or a capacity type. Further, the flow rate sensor may be provided at any place as long as it is independent of the measurement chamber 15 such as the inlet and outlet of the measurement tank, and may be provided at any place.

It is a figure which shows the structure of the residual chlorine measuring system which concerns on one Embodiment of this invention. It is a longitudinal cross-sectional view which shows the detail of the measurement tank of the system. It is the external appearance perspective view which took out and showed the cylindrical unit of the measurement tank. It is A-A 'sectional drawing in FIG. FIG. 3 is a B-B ′ sectional view in FIG. 2. It is a figure which shows the electrode unit with which the measurement tank is mounted | worn, the figure (a) is an external appearance perspective view, and the figure (b) is a front view which shows a front-end | tip part.

Explanation of symbols

  DESCRIPTION OF SYMBOLS 1 ... Measuring tank, 2 ... Electrode unit, 3 ... Flow rate sensor, 4 ... Arithmetic processing unit, 5 ... Voltage generation part, 6 ... Current detection part, 7 ... Arithmetic processing part, 8 ... Display part, 11 ... Lower body part DESCRIPTION OF SYMBOLS 12 ... Upper body part, 14 ... Cylindrical unit, 15 ... Residual chlorine measurement chamber, 16 ... Bead, 17 ... Inlet, 23 ... Sample water flow hole, 24 ... Flow rate measurement chamber, 25 ... Discharge port, 26 ... Magnet 27 ... impeller, 29 ... magnetic sensor.

Claims (3)

A measurement tank having an introduction port for introducing the measurement fluid, a measurement chamber connected to the introduction port, and a discharge port connected to the measurement chamber and discharging the measurement fluid;
An electrode unit mounted on the measurement tank and in contact with the measurement fluid introduced into the measurement chamber from the introduction port and outputting an oxidation / reduction current based on the concentration of free residual chlorine contained in the measurement fluid;
The measurement chamber of the measurement tank is formed in an annular shape by coaxially arranging cylindrical units in a cylindrical space,
The inlet is connected to introduce the test water tangentially to the annular measurement chamber;
In the center of the upper surface of the measurement chamber, an entrance of a flow path connected to the discharge port is provided,
The inside of the annular measurement chamber is filled with beads for cleaning the electrodes of the electrode unit,
The column unit is provided with a means for disturbing the beads. The cylindrical unit is composed of a cylindrical body and a cylindrical base projecting radially to the base end portion thereof, and the cylindrical base has a jump base shape that jumps up the beads toward the electrode unit as means for disturbing the beads. The residual chlorine measuring device according to claim 1, wherein an irregular slope is formed.   The residual chlorine measuring device according to claim 2, wherein an upper portion of the cylindrical body of the cylindrical unit is formed in a conical shape.

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