JP4910588B2 - Water quality measuring device - Google Patents
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- JP4910588B2 JP4910588B2 JP2006250586A JP2006250586A JP4910588B2 JP 4910588 B2 JP4910588 B2 JP 4910588B2 JP 2006250586 A JP2006250586 A JP 2006250586A JP 2006250586 A JP2006250586 A JP 2006250586A JP 4910588 B2 JP4910588 B2 JP 4910588B2
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- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims description 17
- 238000005259 measurement Methods 0.000 claims description 31
- 239000007788 liquid Substances 0.000 claims description 28
- 230000003287 optical effect Effects 0.000 claims description 20
- 238000002835 absorbance Methods 0.000 claims description 19
- 239000000243 solution Substances 0.000 description 9
- 239000012088 reference solution Substances 0.000 description 4
- 238000001514 detection method Methods 0.000 description 2
- 230000000737 periodic effect Effects 0.000 description 2
- 239000000523 sample Substances 0.000 description 2
- 239000012086 standard solution Substances 0.000 description 2
- 238000010521 absorption reaction Methods 0.000 description 1
- 230000008033 biological extinction Effects 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 239000005357 flat glass Substances 0.000 description 1
- 239000011521 glass Substances 0.000 description 1
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Description
本発明は吸光度測定により色度及び濁度などの被測定液の特性を測定する水質測定装置に関する。 The present invention relates to a water quality measuring apparatus for measuring characteristics of a liquid to be measured such as chromaticity and turbidity by measuring absorbance.
図2は、従来の水質測定装置の構成例を示す図である。11は光源、12a,12bは光源11から出た光を平行な光束とするための凹面鏡などからなる光学的手段(以下「ミラー」という)である。13は基準液や測定液を内部に満たすことができる、所定の長さからなる測定セルで、ミラー12aからの平行光が入射される。14は測定セル13における測定値との比較用に設けられた、基準液や測定液を内部に満たすことができる所定の長さ(ここでは測定セル13のセル長より短い)から成る比較セルで、ミラー12bからの平行光が入射される。測定セル13と比較セル14は図示しない流路により連結され、同一サンプル液が通るようになっている。15は円板状のフィルタホイールで、その上に390nm及び660nmのフィルタ16が1個ずつ90度の角度をおいて取り付けられており、一定速度で回転している。測定セル13を出た測定光と比較セル14を出た比較光は間欠的に2個のフィルタ16を通過した後それぞれ凹面鏡17a,17bにより反射・収束されて検出器18の位置で焦点を結ぶ。そして測定光及び比較光各々2種の波長光、合わせて4種の透過光の強さが検出器18により検出される。色度光(390nm)及び濁度光(660nm)の有効セル長における吸光度Ac,Atは次式で示される。
色度光での吸光度:Ac=-log[(ICMM/ICM0)/( ICRM/ICR0)]=k1・C(lM-lR) ・・・(1)
濁度光での吸光度:At=-log[(ITMM/ITM0)/( ITRM/ITR0)]=k2・T(lM-lR) ・・・(2)
FIG. 2 is a diagram illustrating a configuration example of a conventional water quality measurement apparatus. Reference numeral 11 denotes a light source, and reference numerals 12a and 12b denote optical means (hereinafter referred to as "mirror") including a concave mirror for converting the light emitted from the light source 11 into a parallel light beam. Reference numeral 13 denotes a measurement cell having a predetermined length that can be filled with a reference solution or a measurement solution, and receives parallel light from the mirror 12a. Reference numeral 14 is a comparison cell provided for comparison with the measurement value in the measurement cell 13 and having a predetermined length (here, shorter than the cell length of the measurement cell 13) that can fill the reference liquid and the measurement liquid. Parallel light from the mirror 12b is incident. The measurement cell 13 and the comparison cell 14 are connected by a flow path (not shown) so that the same sample solution can pass therethrough. Reference numeral 15 denotes a disk-shaped filter wheel on which 390 nm and 660 nm filters 16 are attached one by one at an angle of 90 degrees, and are rotated at a constant speed. The measurement light exiting from the measurement cell 13 and the comparison light exiting from the comparison cell 14 intermittently pass through the two filters 16 and then are reflected and converged by the concave mirrors 17a and 17b, respectively, to be focused at the position of the detector 18. . Then, the detector 18 detects the intensity of two kinds of light of each of the measurement light and the comparison light, and the total of four kinds of transmitted light. Absorbances Ac and At in the effective cell length of chromaticity light (390 nm) and turbidity light (660 nm) are expressed by the following equations.
Absorbance in chromatic light: Ac = -log [(I CMM / I CM0 ) / (I CRM / I CR0 )] = k 1 · C (l M −l R ) (1)
Absorbance in turbidity light: At = -log [(I TMM / I TM0 ) / (I TRM / I TR0 )] = k 2 · T (l M −l R ) (2)
この2個の吸光度から色度C及び濁度Tの濃度は次式により演算される。
色度:C=β1(Ac−αAt) ・・・(3)
濁度:T=γ1At ・・・(4)
From these two absorbances, the concentrations of chromaticity C and turbidity T are calculated by the following equation.
Chromaticity: C = β 1 (Ac−αAt) (3)
Turbidity: T = γ 1 At (4)
ただし、
α : 濁度補償係数
β1 : 色度係数
γ1 : 濁度係数
ICR0 : ゼロ液(基準液)を入れた時の比較セル透過光量(色度光)
ICRM : 測定液を入れた時の比較セル透過光量(色度光)
ICM0 : ゼロ液を入れた時の測定セル透過光量(色度光)
ICMM : 測定液を入れた時の測定セル透過光量(色度光)
ITR0 : ゼロ液(基準液)を入れた時の比較セル透過光量(濁度光)
ITRM : 測定液を入れた時の比較セル透過光量(濁度光)
ITM0 : ゼロ液を入れた時の測定セル透過光量(濁度光)
ITMM : 測定液を入れた時の測定セル透過光量(濁度光)
lM : 測定セル長
lR : 比較セル長
C : 色度
T : 濁度
である。
However,
α: Turbidity compensation coefficient β 1 : Chromaticity coefficient γ 1 : Turbidity coefficient
I CR0 : Comparison cell light intensity (chromaticity light) when zero liquid (reference liquid) is added
I CRM : Light quantity transmitted through the comparison cell (chromatic light)
I CM0 : Measurement cell transmitted light (chromatic light) when zero liquid is added
I CMM : Light intensity transmitted through measurement cell (chromatic light)
I TR0 : Comparison cell transmitted light (turbidity light) when zero solution (reference solution) is added
I TRM : Comparison cell transmitted light amount (turbidity light) when measuring solution is put
I TM0 : Transmitted light quantity (turbidity light) in the measurement cell when zero liquid is added
I TMM : Transmitted light quantity (turbidity light) when measuring liquid is added
l M : Measurement cell length
l R : Comparison cell length
C: Chromaticity
T: Turbidity.
上記のような水質測定装置に関連する先行技術文献としては次のようなものがある。 Prior art documents related to the water quality measuring apparatus as described above include the following.
上記のような構成の水質測定装置では吸光度の演算において測定セル13と比較セル14の透過光量の比をとっているので、ランプ輝度の変動等の影響を相殺することができる。 In the water quality measuring apparatus configured as described above, the ratio of the transmitted light amount of the measurement cell 13 and the comparison cell 14 is taken in the calculation of the absorbance, so that the influence of fluctuations in lamp luminance and the like can be offset.
また、2波長を用いているので一台の装置で色度と濁度を同時に測定することができる。 Moreover, since two wavelengths are used, chromaticity and turbidity can be measured simultaneously with one apparatus.
また、2波長を用いているので、サンプル液に混じる濁度分を補償した色度を測定することができる。 Further, since two wavelengths are used, chromaticity that compensates for turbidity mixed in the sample liquid can be measured.
しかし、測定セル13と比較セル14の2つのセルを用いるので、装置が大型になるという問題があった。 However, since two cells of the measurement cell 13 and the comparison cell 14 are used, there is a problem that the apparatus becomes large.
また、フィルタホイール15を回転させるためにモータを用いており、機械的稼動部があるため定期的交換が必要になり、保守が面倒という問題があった。 In addition, since a motor is used to rotate the filter wheel 15 and there is a mechanical operating part, periodic replacement is necessary, and there is a problem that maintenance is troublesome.
本発明はこのような課題を解決しようとするもので、小型化でき、機械的稼動部のない水質測定装置を提供することを目的とする。 An object of the present invention is to provide a water quality measuring apparatus that can be downsized and does not have a mechanical working part.
このような課題を達成するために、本発明のうち請求項1記載の発明は、
セル内の被測定液の吸光度に基づいて前記被測定液の特性を測定する水質測定装置において、
光源と、
該光源から出射され前記セルを透過した光が集光される集光光学手段と、
該集光光学手段で集光された光の一部が検出される第1の検出器と、
前記集光光学手段で集光された光の他の一部が再び前記セルを透過した後検出される第2の検出器とを備え、
前記セルを被測定液で満たしたときと基準液で満たしたときのそれぞれについて、前記第1の検出器の出力と前記第2の検出器の出力との比を求め、両者の比に基づいて前記吸光度を測定する
ことを特徴とする。
In order to achieve such a problem, the invention according to claim 1 of the present invention is:
In the water quality measuring device for measuring the characteristics of the liquid to be measured based on the absorbance of the liquid to be measured in the cell,
A light source;
Condensing optical means for collecting light emitted from the light source and transmitted through the cell;
A first detector for detecting a part of the light collected by the condensing optical means;
A second detector that is detected after another part of the light condensed by the condensing optical means passes through the cell again,
A ratio between the output of the first detector and the output of the second detector is obtained for each of the time when the cell is filled with the liquid to be measured and the time when the cell is filled with the reference liquid, and based on the ratio between the two. The absorbance is measured.
請求項2記載の発明は、
請求項1記載の発明である水質測定装置において、
前記光源は、色度測定のための第1の所定波長と、濁度測定のための第2の所定波長の光を出射し、
前記第1、第2の検出器は、それぞれ前記第1、第2の波長に対応するフィルタが貼付された2つの検出器が並置されることを特徴とする。
The invention according to claim 2
In the water quality measuring device according to claim 1,
The light source emits light of a first predetermined wavelength for chromaticity measurement and a second predetermined wavelength for turbidity measurement,
The first and second detectors are characterized in that two detectors to which filters corresponding to the first and second wavelengths are attached are juxtaposed .
以上述べたように、本発明によれば、単一セルの往路光と往復路光の透過光を検出し、両検出出力の比から求めた吸光度に基づいて色度及び濁度を測定することにより、小型化が可能で、機械的稼動部が不要な水質測定装置を実現することができる。 As described above, according to the present invention, the transmitted light of the forward light and the round-trip light of a single cell is detected, and the chromaticity and turbidity are measured based on the absorbance obtained from the ratio of both detection outputs. Therefore, it is possible to realize a water quality measuring apparatus that can be miniaturized and does not require a mechanical operating unit.
以下本発明につき図面を用いて詳細に説明する。
図1は本発明に係る水質測定装置の一実施例を示す説明図である。
Hereinafter, the present invention will be described in detail with reference to the drawings.
FIG. 1 is an explanatory view showing an embodiment of a water quality measuring apparatus according to the present invention.
図1において、光源1から出射された光は光学手段を構成するレンズ2で平行光にされる。測定セル3において、セル前面に設けられた例えばガラス(窓ガラス)等で構成された入射窓3aにはレンズ2からの平行光が入射される。入射窓3aを通過した光はセル3bに入射される。セル3bは所定の光路長を有し、基準液や測定液を内部に満たすことができる。出射窓3cはセル3b後面に設けられ、セル3b内部を通過した光が入射される。球面鏡4は集光光学手段を構成し、出射窓3cを通過した光が入射される。第1の検出器5には球面鏡4で反射・集光された光の一部が入射されて検出される。第2の検出器6には球面鏡4で集光された光の他の一部が測定セル3の出射窓3c、セル3b、入射窓3aを経由して入射され、検出される。ここで、光源1、レンズ2、入射窓3a、セル3b、出射窓3c、球面鏡4、第1の検出器5、第2の検出器6は同一光軸上に配置される。
In FIG. 1, light emitted from a light source 1 is converted into parallel light by a lens 2 constituting optical means. In the
なお、図1では検出器を2つ示しているが、実際には色度と濁度についてそれぞれ2つづつ計4個の検出器を用いる。すなわち、図1において、第1の検出器5は濁度検出器5aと色度検出器5bが紙面に垂直方向に並んで配置され、第2の検出器6は濁度検出器6aと色度検出器6bが紙面に垂直方向に並んで配置される。この場合、濁度検出器5a,6aの前面には濁度光(660nm)用フィルタが貼付され、色度検出器5b,6bの前面には色度光(390nm)用フィルタが貼付される。 Although two detectors are shown in FIG. 1, actually, a total of four detectors are used, two each for chromaticity and turbidity. That is, in FIG. 1, the first detector 5 includes a turbidity detector 5a and a chromaticity detector 5b arranged in a direction perpendicular to the paper surface, and the second detector 6 includes a turbidity detector 6a and a chromaticity detector. The detector 6b is arranged side by side in the direction perpendicular to the paper surface. In this case, a turbidity light (660 nm) filter is affixed to the front surfaces of the turbidity detectors 5a and 6a, and a chromaticity light (390 nm) filter is affixed to the front surfaces of the chromaticity detectors 5b and 6b.
上記の水質測定装置の動作を以下に説明する。レンズ2から出た平行光はその往路においてセル3b内の所定光路長を伝播中にセル3b内の液(基準液又は測定液)による吸収を受ける。第1の検出器5はこの往路において吸収を受けた透過光を検出する。第2の検出器6に入射する透過光は、球面鏡4で収束された光がその復路(往路と逆方向)においてセル3b内の液による吸収を再度受けているので、通過したセル3b内の光路長は第1の検出器5の入射光の場合の2倍となる。このとき吸光度、濁度及び色度は次式で演算される。 The operation of the water quality measuring apparatus will be described below. The parallel light emitted from the lens 2 is absorbed by the liquid (reference liquid or measurement liquid) in the cell 3b while propagating through a predetermined optical path length in the cell 3b in the forward path. The first detector 5 detects the transmitted light that has been absorbed in the forward path. In the transmitted light incident on the second detector 6, the light converged by the spherical mirror 4 is again absorbed by the liquid in the cell 3b in the return path (in the opposite direction to the forward path). The optical path length is twice that of the incident light from the first detector 5. At this time, the absorbance, turbidity, and chromaticity are calculated by the following equations.
濁度の場合、
IT1/IT10=10-kT*l*T
IT2/IT20=10-kT*2*l*T
Abs(T)=−log{(IT2/IT20)/(IT1/IT10)}
=kT*T*(2*l−l)
=kT*l*T ・・・(5)
T=γ2*Abs(T) ・・・(6)
となる。ただし、
IT10 : ゼロ液(基準液)を入れた時の濁度検出器5aの透過光信号
IT1 : 測定液を入れた時の濁度検出器5aの透過光信号
IT20 : ゼロ液を入れた時の濁度検出器6aの透過光信号
IT2 : 測定液を入れた時の濁度検出器6aの透過光信号
kT : 濁度の吸光係数
l : 測定セル3の単光路の光路長
T : 濁度
Abs(T) : 濁度の吸光度
γ2 : 濁度係数(実際には(6)式で濁度標準液の吸光度Abs(T)を測定して求める)
である。
For turbidity,
I T1 / I T10 = 10 -kT * l * T
I T2 / I T20 = 10 -kT * 2 * l * T
Abs (T) = − log {( IT2 / IT20 ) / ( IT1 / IT10 )}
= K T * T * (2 * l−l)
= K T * l * T (5)
T = γ 2 * Abs (T) (6)
It becomes. However,
I T10 : Transmitted light signal of turbidity detector 5a when zero solution (reference solution) is added
I T1 : Transmitted light signal of the turbidity detector 5a when the measuring solution is added
I T20 : Transmitted light signal of turbidity detector 6a when zero liquid is added
I T2 : Transmitted light signal of turbidity detector 6a when measuring solution is put
k T : Absorption coefficient of turbidity
l: Optical path length of single optical path of
T: Turbidity
Abs (T): turbidity absorbance gamma 2: Turbidity coefficient (actually determined by measuring the turbidity standard solution absorbance Abs (T) with (6))
It is.
色度の場合、
IC1/IC10=10-kC*l*C
IC2/IC20=10-kC*2*l*C
Abs(C)=−log{(IC2/IC20)/(IC1/IC10)}
=kC*C*(2*l−l)
=kC*l*C ・・・(5)
C=β2*Abs(C) ・・・(6)
となる。ただし、
IC10 : ゼロ液(基準液)を入れた時の色度検出器5bの透過光信号
IC1 : 測定液を入れた時の色度検出器5bの透過光信号
IC20 : ゼロ液を入れた時の色度検出器6bの透過光信号
IC2 : 測定液を入れた時の色度検出器6bの透過光信号
kC : 色度の吸光係数
l : 測定セル3の単光路の光路長
C : 色度
Abs(C) : 色度の吸光度
β2 : 色度係数(実際には(6)式で色度標準液の吸光度Abs(C)を測定して求める)
である。
For chromaticity,
I C1 / I C10 = 10 -kC * l * C
I C2 / I C20 = 10 -kC * 2 * l * C
Abs (C) = − log {(I C2 / I C20 ) / (I C1 / I C10 )}
= K C * C * (2 * l−l)
= K C * l * C (5)
C = β 2 * Abs (C) (6)
It becomes. However,
I C10 : Transmitted light signal of chromaticity detector 5b when zero liquid (reference liquid) is added
I C1 : Transmitted light signal of the chromaticity detector 5b when the measurement solution is added
I C20 : Transmitted light signal of chromaticity detector 6b when zero liquid is added
I C2 : Transmitted light signal of chromaticity detector 6b when measuring solution is put
k C : Chromatic extinction coefficient
l: Optical path length of single optical path of
C: Chromaticity
Abs (C): chromaticity of absorbance beta 2: chromaticity coefficient (actually determined by measuring the absorbance Abs (C) chromaticity standard solution in (6))
It is.
上記のような構成の水質測定装置によれば、従来のように比較セルと測定セルの2種類のセルを必要とせず、単一の測定セルを使用しているので、小型化することができる。 According to the water quality measuring apparatus having the above-described configuration, it is not necessary to use two types of cells, a comparison cell and a measurement cell, as in the prior art, and a single measurement cell is used. .
また、往復路光と往路光の検出出力に基づいて吸光度を測定しているので、機械的稼動部が不要で、定期的交換が不要となる。 In addition, since the absorbance is measured based on the detection output of the round trip light and the forward light, a mechanical operating unit is unnecessary and periodic replacement is unnecessary.
また、(5)式に示すように、吸光度の演算の際に往復路と往路の透過光信号の比をとっているので、光源1のランプ輝度の変動の影響を相殺することができる。 Further, as shown in the equation (5), since the ratio of the transmitted light signal between the round trip path and the forward path is taken when calculating the absorbance, the influence of the fluctuation of the lamp luminance of the light source 1 can be offset.
また、2波長を用いているので一台の装置で色度と濁度を同時に測定できる。 Moreover, since two wavelengths are used, chromaticity and turbidity can be measured simultaneously with one apparatus.
また、2波長を用いているので、(3)式と同様にしてサンプル液に混じる濁度分を補償した色度を測定することができる。 Since two wavelengths are used, the chromaticity compensated for the turbidity mixed in the sample liquid can be measured in the same manner as the equation (3).
なお、上記の実施例では被測定液の特性が色度及び濁度である場合を示したが、色度検出器又は濁度検出器を用いて色度又は濁度の一方を検出してもよい。 In the above embodiment, the case where the characteristic of the liquid to be measured is chromaticity and turbidity is shown. However, even if one of chromaticity or turbidity is detected using a chromaticity detector or turbidity detector, Good.
また、色度及び濁度に限らず、吸光度に基づいて測定される被測定液の様々な特性の測定に適用することができる。
また、上記の実施例では集光光学手段として球面鏡を用いているが、干渉膜等測定セル3に再入射させることのできる、各種の集光光学手段を用いることができる。
Further, the present invention is not limited to chromaticity and turbidity, and can be applied to measurement of various characteristics of a liquid to be measured that is measured based on absorbance.
In the above embodiment, a spherical mirror is used as the condensing optical means, but various condensing optical means that can be re-incident on the measuring
1 光源
3 セル
4 集光光学手段
5 第1の検出器
6 第2の検出器
DESCRIPTION OF SYMBOLS 1
Claims (2)
光源と、
該光源から出射され前記セルを透過した光が集光される集光光学手段と、
該集光光学手段で集光された光の一部が検出される第1の検出器と、
前記集光光学手段で集光された光の他の一部が再び前記セルを透過した後検出される第2の検出器とを備え、
前記セルを被測定液で満たしたときと基準液で満たしたときのそれぞれについて、前記第1の検出器の出力と前記第2の検出器の出力との比を求め、両者の比に基づいて前記吸光度を測定する
ことを特徴とする水質測定装置。 In the water quality measuring device for measuring the characteristics of the liquid to be measured based on the absorbance of the liquid to be measured in the cell,
A light source;
Condensing optical means for collecting light emitted from the light source and transmitted through the cell;
A first detector for detecting a part of the light collected by the condensing optical means;
A second detector that is detected after another part of the light condensed by the condensing optical means passes through the cell again,
A ratio between the output of the first detector and the output of the second detector is obtained for each of the time when the cell is filled with the liquid to be measured and the time when the cell is filled with the reference liquid, and based on the ratio between the two. A water quality measuring device that measures the absorbance.
前記第1、第2の検出器は、それぞれ前記第1、第2の波長に対応するフィルタが貼付された2つの検出器が並置されることを特徴とする請求項1記載の水質測定装置。 The light source emits light of a first predetermined wavelength for chromaticity measurement and a second predetermined wavelength for turbidity measurement,
2. The water quality measuring apparatus according to claim 1, wherein the first and second detectors are juxtaposed with two detectors to which filters corresponding to the first and second wavelengths are attached, respectively .
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